open.alberta.ca · Devon NEC Corporation Pike 1 Project Volume 3 – EIA Appendices June 2012...

Appendix H

Fisheries and Aquatic Resources

Appendix H1

Survey Sampling Summary by Season

Devon NEC Corporation Pike 1 Project Volume 3 – EIA Appendices June 2012

Appendix H1 – Page 1

Table H1-1: Aquatic Resources Survey Sampling Summary by Season

Site Stream/River or Water Body Name Spring 2010 Summer 2010 Fall 2010 Spring 2011

A1 Watercourse A •▲ – •▲ –A7 Watercourse A-1 •▲ – •▲◘ ■ –A2 Watercourse A •▲ – •▲ –A3 Hay Lake •▲ •▲◘ •▲■ –A4 Watercourse A •▲ – •▲ –A5 Kirby Lake •▲ •▲◘ •▲■ – A6 Watercourse A-5 • – – – B1 Sandy River •▲ – •▲■ –B2 Watercourse B-9 •▲ – •▲◘ –B3 Lake B-1 •▲ •▲◘ •▲ –B4 Watercourse B-15 •▲ – •▲■ –B5 Watercourse B-9 •▲ – •▲ –B6 Sandy River •▲ •▲ •▲ –B7 Watercourse B-12 •▲ – •▲ –B8 Watercourse B-13 – – •▲ •▲ B9 Watercourse B-14 • – – – B10 Sandy River •▲ – •▲ –B11 Lake B-2 •▲ •▲ •▲◘ ■ –B12 Watercourse B-16-1 •▲ – •▲ – B13 Watercourse B-16 •▲ – •▲◘ –B14 Lake B-3 – – •▲■ •▲ B15 Lake B-4 – – •▲ •▲ B16 Sandy River •▲ – •▲ –B17 Watercourse B-16 – – •▲■ •▲ C1 Monday Creek – – •▲■ •▲ C2 Watercourse C-1 – – •▲ • C3 Watercourse C-2 – – •▲◘ •▲ C4 Watercourse C-3 C5 Watercourse C-4 – – •▲ •▲

Note: • Aquatic Habitat ▲ Fish Inventory ◘ Fish Health/Toxicology ■ Benthic Invertebrates – No Survey Conducted

Appendix H2

Fish Health Assessment Summary Data, Definitions and Field Data Sheets



Table H2-1: Fish Health Assessment Definitions Variable Variable Condition CodeEyes no aberrations; good “clear” eye N

blind; an opaque eye (one or both) B swollen, protruding eye (one or both) E hemorrhaging or bleeding in the eye (one or both) H missing one or both eyes M other; any condition not covered above OT

Gills normal; no apparent aberrations N frayed; erosion of tips of gill lamellae resulting in “ragged” gills F clubbed; swelling of the tips of the gill lamellae C marginate; gills with light, discoloured margin along tips of the lamellae M pale; very light in colour P other; any condition not covered above OT

Skin normal; no aberrations 0 mild skin aberrations 1 moderate skin aberrations 2 severe skin aberrations 3

Fins no active erosion 0 light active erosion 1 moderate active erosion with some hemorrhaging 2 severe active erosion with hemorrhaging 3

Opercle no shortening 0 mild shortening 1 Severe shortening 2

Body deformities none No any deformity (provide details) Yes

Liver normal; solid red or light red colour A “fatty” liver; “coffee with cream” colour C nodules in the liver; cysts or nodules D focal discoloration; distinct localized colour changes E general discoloration; colour change in whole liver F other; any condition not covered above OT

Gall bladder normal 0 enlarged 1 parasites 2

Spleen normal; black, very dark red, or red B granular; rough appearance of spleen G nodular; containing fistulas or nodules of varying sizes D enlarged; noticeable enlarged E other; any condition not covered above OT

Kidney normal; firm dark red colour, lying relatively flat along vertebral column N swollen; enlarged or swollen wholly or in part S mottled; grey discoloration M granular; granular appearance and texture G urolithiasis/nephrocalcinosis; white/cream mineral material in tubules U other; any condition not covered above OT

Parasites no observed parasites 0 few observed parasites 1 moderate parasite infestation 2 numerous parasites 3



Table H2-2: Summary of Fish Tissue Samples Collected in the ALSA, 2010 Summer Survey Fall Survey

Sample Analytical Method

Fish Species

Length (mm)

Whole Fish Weight

(g)

Carcass Weight

(g) Sex Sample Analytical

Method Fish

Species Length (mm)

Whole Fish Weight

(g)

Carcass Weight

(g) Sex

Site A3 – Hay Lake LF-1 Individual NRPK 490 690 580 M LF-2 Individual NRPK 475 780 640 M LF-3 Individual NRPK 402 490 420 M LF-4 Individual NRPK 500 900 790 F LF-5 Individual NRPK 479 810 710 M LF-6 Individual NRPK 471 650 570 F LF-7 Individual NRPK 458 650 570 F LF-8 Individual NRPK 387 400 340 M LF-9 Individual NRPK 403 470 360 M

LF-10 Individual NRPK 404 400 370 F

Site A5 – Kirby Lake LF-1 Individual NRPK 607 1580 1380 M LF-2 Individual NRPK 708 2670 2280 F LF-3 Individual NRPK 687 2580 2250 F LF-4 Individual NRPK 677 2470 2170 F LF-5 Individual NRPK 645 1600 1450 F LF-6 Individual NRPK 564 1350 1240 M LF-7 Individual NRPK 580 1490 1350 M LF-8 Individual NRPK 780 3370 3020 F LF-9 Individual NRPK 726 2700 2460 F

LF-10 Individual NRPK 750 3450 2980 F

Site A7 – Watercourse A-1 FF-1 Composite FNDC 70 4 - - FF-2 Composite FNDC 81 6 - - FF-3 Composite FNDC 71 4 - - FF-4 Composite FNDC 69 4 - - FF-5 Composite FNDC 70 4 - - FF-6 Composite FNDC 70 4 - - FF-7 Composite FNDC 61 4 - - FF-8 Composite FNDC 64 3 - - FF-9 Composite FNDC 65 3 - - FF-10 Composite FNDC 63 3.5 - -



Summer Survey Fall Survey


Fish Species

Length (mm)

Whole Fish Weight

(g)

Carcass Weight


Method Fish

Species Length (mm)

Whole Fish Weight

(g)

Carcass Weight

(g) Sex

Site B2 – Watercourse B-9 FF-1 Composite BKST 62 3 - - FF-2 Composite BKST 47 2 - - FF-3 Composite BKST 23 <1 - - FF-4 Composite BKST 65 3 - - FF-5 Composite BKST 24 <1 - - FF-6 Composite BKST 38 1 - - FF-7 Composite BKST 24 <1 - - FF-8 Composite BKST 24 <1 - - FF-9 Composite BKST 21 <1 - - FF-10 Composite BKST 58 2 - -

Site B3 – Lake B-1 FF-1 Composite FNDC 59 2.2 - - FF-2 Composite FNDC 55 2.3 - - FF-3 Composite FNDC 57 2.2 - - FF-4 Composite FNDC 56 1.9 - - FF-5 Composite FNDC 50 1.5 - - FF-6 Composite FNDC 53 1.6 - - FF-7 Composite FNDC 57 2.1 - - FF-8 Composite FNDC 45 1.2 - - FF-9 Composite FNDC 55 2.1 - -

FF-10 Composite FNDC 45 1.0 - -

Site B11 – Lake B-2 LF-1 Individual WHSC 443 1410 1000 M LF-2 Individual WHSC 345 600 500 M LF-3 Individual WHSC 425 1200 1000 F LF-4 Individual WHSC 439 1400 900 M LF-5 Individual WHSC 390 800 700 F LF-6 Individual WHSC 379 700 600 F LF-7 Individual WHSC 403 1000 700 F LF-8 Individual WHSC 419 1100 800 M LF-9 Individual WHSC 413 1200 900 F LF-10 Individual WHSC 399 1100 800 M



Summer Survey Fall Survey


Fish Species

Length (mm)

Whole Fish Weight

(g)

Carcass Weight


Method Fish

Species Length (mm)

Whole Fish Weight

(g)

Carcass Weight

(g) Sex

Site B13 – Watercourse B-16 FF-1 Composite BKST 60 3 - - FF-2 Composite BKST 55 2 - - FF-3 Composite BKST 51 2 - - FF-4 Composite BKST 64 4 - - FF-5 Composite BKST 50 1 - - FF-6 Composite BKST 60 4 - - FF-7 Composite BKST 58 3 - - FF-8 Composite BKST 47 2 - - FF-9 Composite BKST 57 3 - - FF-10 Composite BKST 40 1 - -

Site C3 – Watercourse C-2 FF-1 Composite WHSC 84 6.0 - - FF-2 Composite WHSC 83 5.5 - - FF-3 Composite WHSC 72 3.1 - - FF-4 Composite WHSC 74 4.2 - - FF-5 Composite WHSC 68 2.7 - -



Table H2-3: Analytical Methods and Associated Detection Limits Used for Analysis of Inorganic Chemical Parameters

Parameter Method Detection Limit (mg/Kg)

Aluminum (Al) EPA 200.3/200.7-ICPOES 2.0 Antimony (Sb) EPA 200.3/200.8-ICPMS 0.01 Arsenic (As) EPA 200.3/200.8-ICPMS 0.01 Barium (Ba) EPA 200.3/200.8-ICPMS 0.02 Beryllium (Be) EPA 200.3/200.8-ICPMS 0.1 Bismuth (Bi) EPA 200.3/200.8-ICPMS 0.06 Cadmium (Cd) EPA 200.3/200.8-ICPMS 0.006 Calcium (Ca) EPA 200.3/200.7-ICPOES 2.0 Chromium (Cr) EPA 200.3/200.7-ICPOES 0.1 Cobalt (Co) EPA 200.3/200.8-ICPMS 0.02 Copper (Cu) EPA 200.3/200.8-ICPMS 0.04 Iron (Fe) EPA 200.3/200.7-ICPOES 1.0 Lead (Pb) EPA 200.3/200.8-ICPMS 0.02 Lithium (Li) EPA 200.3/200.8-ICPMS 0.1 Magnesium (Mg) EPA 200.3/200.8-ICPMS 1.0 Manganese (Mn) EPA 200.3/200.8-ICPMS 0.01 Mercury (Hg) EPA 200.3 / EPA 245.1 0.002 Molybdenum (Mo) EPA 200.3/200.8-ICPMS 0.01 Nickel (Ni) EPA 200.3/200.8-ICPMS 0.1 Phosphorus (P) EPA 200.3/200.7-ICPOES 5.0 Potassium (K) EPA 200.3/200.7-ICPOES 20.0 Selenium (Se) EPA 200.3/200.8-ICPMS 0.2 Silver (Ag) EPA 200.3/200.8-ICPMS 0.05 Sodium (Na) EPA 200.3/200.7-ICPOES 20.0 Strontium (Sr) EPA 200.3/200.8-ICPMS 0.01 Thallium (Tl) EPA 200.3/200.8-ICPMS 0.01 Tin (Sn) EPA 200.3/200.8-ICPMS 0.05 Titanium (Ti) EPA 200.3/200.7-ICPOES 0.1 Uranium (U) EPA 200.3/200.8-ICPMS 0.002 Vanadium (V) EPA 200.3/200.8-ICPMS 0.1 Zinc (Zn) EPA 200.3/200.7-ICPOES 0.1 % Moisture Oven dry 105C-Gravimetric 0.1



Table H2-4: Criteria Used for Evaluating Risk to Fish Health Based on Concentrations of Metals that have Lethal, Sublethal, or No Effects on Freshwater Fish

Variable Endpoint Concentrations (mg/kg) Tissue Species Life Stage or Size Route (Days)

Metals Aluminum Survival no effects 1.0-1.15 muscle rainbow trout, Atlantic salmon 171 g, alevin oral, water 30-42

effects 20-36.8 whole body Atlantic salmon Alevin Water 30 Antimony Survival no effects 5 whole body rainbow trout fingerling (1.2 g) water 30

effects 9 whole body rainbow trout fingerling (1.2 g) water 30 Arsenic Survival no effects 2.6-11.4 carcass, whole body rainbow trout juvenile oral, water 21-56

effects 11.2-17.9 carcass rainbow trout juvenile oral 56 Growth no effects 0.9-6.5 carcass, whole body rainbow trout juvenile oral, water 21-56

effects 3.1 carcass rainbow trout Juvenile oral 56 Cadmium Survival no effects 0.02-2.8 muscle rainbow trout, brook trout 150-200 g, adult water, in injection2 210-455

effects 0.14-0.7 whole body rainbow trout, brook trout 5-15 g water 29-30 Growth no effects 0.09-2.8 muscle, whole body rainbow trout, brook trout 3.1 g,, 5 g, adult water 30-455

effects 0.12-0.96 muscle, whole body rainbow trout, Atlantic salmon 3.1 g, alevin water 92-210 Reproduction no effects 0.4 muscle rainbow trout adult water 455

Copper Survival no effects 0.5-3.4 muscle rainbow trout, brook trout embryo-adult-juvenile water 0.33-720 no effects 0.5 muscle rainbow trout 138 g water 0.33

Growth no effects 3.4 muscle brook trout embryo-adult-juvenile water 720 Reproduction no effects 3.4 muscle brook trout embryo-adult-juvenile water 720

Lead Survival no effects 4.0 carcass rainbow trout under-yearlings (6.5 g) water 224 Mercury1 Survival no effects 1.91-35.0 whole body, muscle rainbow trout, brook trout 10-20 mm, juvenile, fingerling,

yearling-adult, adult ip injection2, , oral, water

15-273

effects 3.7-31 whole body, muscle rainbow trout, brook trout 10-20 mm, subadult (100-150 g), ip injection2, oral 186-273 northern pike yearling-adult, adult water

Growth no effects 2.28-29.0 whole body, muscle rainbow trout fingerling, juvenile oral, water 24-105 effects 8.6-35.0 whole body, muscle rainbow trout fingerling oral 84-105 Reproduction no effects 9.2 muscle brook trout yearling-adult water 273

effects 23.5 muscle brook trout yearling-adult water 273 Nickel Survival no effects 0.82-58.0 muscle rainbow trout, carp 15 g, 150-200 g water 5 0 180

effects 118.1 Muscle carp 15 g water 4 Selenium Survival no effects 0.28-3.1 whole body, carcass rainbow trout, Chinook

salmon larvae-swim-up, egg-juvenile water, oral 28-308

largemouth bass fingerling-juvenile effects 0.92-2.5 whole body, carcass rainbow trout, Chinook

salmon larvae-swim-up, fingerling-juvenile water, oral 28-168

Growth no effects 0.08-1.08 whole body, carcass rainbow trout, Chinook larvae-swim-up, juvenile oral 60-308



Variable Endpoint Concentrations (mg/kg) Tissue Species Life Stage or Size Route (Days)

Metals salmon

fingerling-juvenile, juvenile effects 0.32-2.08 whole body, carcass rainbow trout, Chinook

salmon larvae-swim-up, fingerling-juvenile, juvenile

oral 60-168

Silver Survival no effects 0.003 carcass largemouth bass young-of-year water 180 Growth no effects 0.003 carcass largemouth bass young-of-year water 180

Vanadium Survival no effects 5.33 carcass rainbow trout juvenile oral 84 Growth no effects 0.02 carcass rainbow trout juvenile oral 84

effects 0.41 carcass rainbow trout juvenile oral 84 Zinc Survival no effects 60 whole body Atlantic salmon juvenile water 80

Growth no effects 60 whole body Atlantic salmon juvenile water 80

Note:

1 Methylated forms of mercury; 2 ip = intraperitoneal injection is the injection of a substance into the body cavity. Only thresholds derived from the most relevant studies were used to screen the fish tissue data; those derived from studies on small-bodied fish or tropical fish species, and those that simultaneously evaluated effects of conventional variables on toxicity or maternal transfer studies, were excluded. Effects concentrations associated with acute exposures were only included for contaminants where few other data existed.

External Fish Examination Data Sheets

AMEC EARTH & ENVIRONMENTAL

221 18 ST SE

CALGARY AB T2E 6J5

Report On: 10-JUN-06 05:16 AMATTN: BRETT MCLEOD

THIS REPORT SHALL NOT BE REPRODUCED EXCEPT IN FULL WITHOUT THE WRITTEN AUTHORITY OF THE LABORATORY.ANY REMAINING SAMPLES WILL BE DISPOSED OF AFTER 30 DAYS FOLLOWING ANALYSIS. PLEASE CONTACT THE LAB IF YOUREQUIRE ADDITIONAL SAMPLE STORAGE TIME.

PRELIMINARY RESULTS

Comments:

APPROVED BY: ____________________________________________

PATRICK CORBIELL

Project Manager

CEO3399 PHASE 700Job Reference: Project P.O. #:

Legal Site Desc: 245664CofC Numbers:

29-MAY-06Lab Work Order #: L393340 Date Received:

ALS Canada LimitedEnvironmental Division

Part of the ALS Laboratory GroupBay 1, 245 MacDonald Cresent, Fort McMurray, AB T9H 4B5

Phone: +1 780 791 1524 Fax: +1 780 791 1586 www.alsglobal.comA Campbell Brothers Limited Company

ALS LABORATORY GROUP ANALYTICAL REPORT

L393340 CONTD....

2PAGE

Result D.L. Units Extracted Analyzed BySample Details/Parameters

of

CEO3399 PHASE 700

Qualifier* Batch

3

L393340-11 COMPOSITEBM on 26-MAY-06 @ 18:45Sample By:

FISH TISSUEMetals in Animal Tissue

Arsenic (As)

Silver (Ag)Aluminum (Al)Barium (Ba)Beryllium (Be)Cadmium (Cd)Cobalt (Co)Chromium (Cr)Copper (Cu)Molybdenum (Mo)Nickel (Ni)Lead (Pb)Antimony (Sb)Tin (Sn)Strontium (Sr)Thallium (Tl)Vanadium (V)Zinc (Zn)

Calcium (Ca)Potassium (K)Magnesium (Mg)Sodium (Na)Iron (Fe)Manganese (Mn)Phosphorus (P)Selenium (Se)Titanium (Ti)

Mercury (Hg)

mg/kg

mg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kg

mg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kg

mg/kg

07-JUN-06

07-JUN-0607-JUN-0607-JUN-0607-JUN-0607-JUN-0607-JUN-0607-JUN-0607-JUN-0607-JUN-0607-JUN-0607-JUN-0607-JUN-0607-JUN-0607-JUN-0607-JUN-0607-JUN-0607-JUN-06

08-JUN-0608-JUN-0608-JUN-0608-JUN-0608-JUN-0608-JUN-0608-JUN-0607-JUN-0607-JUN-06

07-JUN-06

CVE

CVECVECVECVECVECVECVECVECVECVECVECVECVECVECVECVECVE

HASHASHASHASHASHASHASCVECVE

CVE

<0.05

<0.05<21.0

<0.2<0.01<0.1<0.12.36

<0.050.020.04

<0.05<0.12.95

<0.05<0.134.7

7030<5

<20<5

<0.550

0.150.14

0.07

Metals in Tissue

Metals in Tissue

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

Matrix:

R407772

R407772R407772R407772R407772R407772R407772R407772R407772R407772R407772R407772R407772R407772R407772R407772R407772R407772

R407620R407620R407620R407620R407620R407620R407620R407772R407772

R407772

* Refer to Referenced Information for Qualifiers (if any) and Methodology.

AS-FAUNA-EDHG-FAUNA-EDMET1-FAUNA-EDMET2-FAUNA-EDP-FAUNA-EDSE-FAUNA-EDTI-FAUNA-ED

Reference Information

Arsenic (As)Mercury (Hg)Metals in TissueMetals in TissuePhosphorus (P)Selenium (Se)Titanium (Ti)

L393340 CONTD....

3PAGE of

CEO3399 PHASE 700

Methods Listed (if applicable):

ALS Test Code Test Description

TissueTissueTissueTissueTissueTissueTissue

EPA 6020EPA 6020EPA 6020EPA 200.7EPA 200.7EPA 6020EPA 6020

Analytical Method Reference(Based On)

** Laboratory Methods employed follow in-house procedures, which are generally based on nationally or internationally accepted methodologies.

EPA 200.3EPA 200.3EPA 200.3EPA 200.3EPA 200.3EPA 200.3EPA 200.3

Preparation Method Reference(Based On) Matrix

GLOSSARY OF REPORT TERMSSurr - A surrogate is an organic compound that is similar to the target analyte(s) in chemical composition and behavior but not normally detected in environmental samples. Prior to sample processing, samples are fortified with one or more surrogate compounds.The reported surrogate recovery value provides a measure of method efficiency. The Laboratory control limits are determined under column heading D.L.mg/kg (units) - unit of concentration based on mass, parts per millionmg/L (units) - unit of concentration based on volume, parts per million< - Less thanD.L. - Detection LimitN/A - Result not available. Refer to qualifier code and definition for explanation

Test results reported relate only to the samples as received by the laboratory.UNLESS OTHERWISE STATED, ALL SAMPLES WERE RECEIVED IN ACCEPTABLE CONDITION.UNLESS OTHERWISE STATED, SAMPLES ARE NOT CORRECTED FOR CLIENT FIELD BLANKS.Although test results are generated under strict QA/QC protocols, any unsigned test reports, faxes, or emails are considered preliminary.

ALS Laboratory Group has an extensive QA/QC program where all analytical data reported is analyzed using approved referenced procedures followed by checks and reviews by senior managers and quality assurance personnel. However, since the results are obtained from chemical measurements and thus cannot be guaranteed, ALS Laboratory Group assumes no liability for the use or interpretation of the results.

The last two letters of the above test code(s) indicate the laboratory that performed analytical analysis for that test. Refer to the list below:

Laboratory Definition Code Laboratory Location Laboratory Definition Code Laboratory Location

ED ALS LABORATORY GROUP - EDMONTON, ALBERTA, CANADA

Chain of Custody numbers:

245664

3

ALS Laboratory Group Quality Control ReportPage 1 of

Client:

Contact:

AMEC EARTH & ENVIRONMENTAL221 18 ST SE CALGARY AB T2E 6J5

BRETT MCLEOD

Report Date: 10-JUN-06Workorder: L393340

Test Matrix Reference Result Qualifier Units RPD Limit Analyzed

AS-FAUNA-ED

HG-FAUNA-ED

MET1-FAUNA-ED

Tissue

Tissue

Tissue

R407772

R407772

R407772

Batch

Batch

Batch

CRM

DUP

MB

MS

CRM

DUP

MB

MS

CRM

DUP

WG451079-2

WG451079-3

WG451079-1

WG451079-4

WG451079-2

WG451079-3

WG451079-1

WG451079-4

WG451079-2

WG451079-3

DORM-2_FISH

L389813-10

L389813-10

DORM-2_FISH

L389813-10

L389813-10

DORM-2_FISH

L389813-10

Arsenic (As)

Arsenic (As)

Arsenic (As)

Arsenic (As)

Mercury (Hg)

Mercury (Hg)

Mercury (Hg)

Mercury (Hg)

Aluminum (Al)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Nickel (Ni)

Zinc (Zn)

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

108

<0.05

<0.05

110

63

0.08

<0.01

97

92

90

97

94

86

97

85

77

<2

<0.05

<0.1

<0.2

<0.01

<0.1

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

N/A

0.00

N/A

N/A

N/A

N/A

N/A

N/A

19

0.04

23

35

14

26

21

16

89-144

70-127

35-128

67-122

48-144

72-116

74-125

83-128

76-104

51-120

75-108

57-117

%

mg/kg

mg/kg

%

%

mg/kg

mg/kg

%

%

%

%

%

%

%

%

%

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

0.25

0.05

RPD-NA

J

RPD-NA

RPD-NA

RPD-NA

RPD-NA

RPD-NA

RPD-NA

<0.05

0.08

<2

<0.05

<0.1

<0.2

<0.01

<0.1

5

ALS Laboratory Group Quality Control ReportPage 2 ofReport Date: 10-JUN-06Workorder: L393340


MET1-FAUNA-ED Tissue

R407772BatchDUP

MB

MS

WG451079-3

WG451079-1

WG451079-4

L389813-10

L389813-10

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

<0.1

0.59

<0.02

<0.05

<0.02

<0.05

0.21

<0.05

<0.1

<0.1

4.7

<2

<0.05

<0.1

<0.2

<0.01

<0.1

<0.1

<0.05

<0.02

<0.05

<0.02

<0.05

<0.05

<0.05

<0.1

<0.1

<0.5

94

94

98

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

N/A

0.19

N/A

N/A

N/A

N/A

0.11

N/A

N/A

N/A

0.7

23

0.2

26

50

23

33

0.2

26

38

25

2

73-121

80-114

77-120

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

%

%

%

10

0.25

0.5

1

0.05

0.5

0.5

0.25

0.1

0.25

0.1

0.25

0.25

0.25

0.5

0.5

2.5

RPD-NA

J

RPD-NA

RPD-NA

RPD-NA

RPD-NA

J

RPD-NA

RPD-NA

RPD-NA

J

<0.1

0.39

<0.02

<0.05

<0.02

<0.05

0.33

<0.05

<0.1

<0.1

3.9

5



MET1-FAUNA-ED

MET2-FAUNA-ED

Tissue

Tissue

R407772

R407620

Batch

Batch

MS

CRM

DUP

MB

WG451079-4

WG451079-2

WG451079-3

WG451079-1

L389813-10

DORM-2_FISH

L389813-10

L389813-10

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

Silver (Ag)

Iron (Fe)

Manganese (Mn)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

93

89

121

97

99

93

96

105

109

98

106

102

134

55

103

99

230

<5

272

<0.5

3640

530

<20

<5

<5

<0.5

<20

<20

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

27

N/A

5.7

N/A

7.5

10

19

15

14

15

15

22

59-119

66-115

68-145

83-123

79-119

77-118

82-122

81-119

81-129

78-119

87-118

76-122

26-142

56-122

90-124

83-118

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

G

100

25

25

2.5

100

100

G

RPD-NA

RPD-NA

300

<5

257

<0.5

3370

480

5



MET2-FAUNA-ED

P-FAUNA-ED

SE-FAUNA-ED

TI-FAUNA-ED

Tissue

Tissue

Tissue

Tissue

R407620

R407620

R407772

R407772

Batch

Batch

Batch

Batch

MS

DUP

MB

MS

CRM

DUP

MB

MS

DUP

MB

MS

WG451079-4

WG451079-3

WG451079-1

WG451079-4

WG451079-2

WG451079-3

WG451079-1

WG451079-4

WG451079-3

WG451079-1

WG451079-4

L389813-10

L389813-10

L389813-10

DORM-2_FISH

L389813-10

L389813-10

L389813-10

L389813-10

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Phosphorus (P)

Phosphorus (P)

Phosphorus (P)

Selenium (Se)

Selenium (Se)

Selenium (Se)

Selenium (Se)

Titanium (Ti)

Titanium (Ti)

Titanium (Ti)

101

101

99

100

98

100

1820

60

94

113

0.27

<0.05

98

0.12

0.06

102

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

2.3

0.02

0.01

17

0.2

0.2

71-125

63-129

78-113

80-115

56-154

82-122

64-133

101-168

44-153

18-177

%

%

%

%

%

%

mg/kg

mg/kg

%

%

mg/kg

mg/kg

%

mg/kg

mg/kg

%

100

0.25

0.25

J

J

1870

0.29

0.11

5

Legend:

Qualifier:

RPD-NA Relative Percent Difference Not Available due to result(s) being less than detection limit.A Method blank exceeds acceptance limit. Blank correction not applied, unless the qualifier "RAMB" (result adjusted for method blank) appears in the Analytical Report.B Method blank result exceeds acceptance limit, however, it is less than 5% of sample concentration. Blank correction not applied. E Matrix spike recovery may fall outside the acceptance limits due to high sample background. F Silver recovery low, likely due to elevated chloride levels in sample. G Outlier - No assignable cause for nonconformity has been determined.J Duplicate results and limit(s) are expressed in terms of absolute difference.K The sample referenced above is of a non-standard matrix type; standard QC acceptance criteria may not be achievable.

Limit 99% Confidence Interval (Laboratory Control Limits)DUP DuplicateRPD Relative Percent DifferenceN/A Not AvailableLCS Laboratory Control SampleSRM Standard Reference MaterialMS Matrix SpikeMSD Matrix Spike DuplicateADE Average Desorption EfficiencyMB Method BlankIRM Internal Reference MaterialCRM Certified Reference MaterialCCV Continuing Calibration VerificationCVS Calibration Verification StandardLCSD Laboratory Control Sample Duplicate

ALS Laboratory Group Quality Control ReportPage 5 ofReport Date: 10-JUN-06Workorder: L393340 5


221 18 ST SE

CALGARY AB T2E 6J5

Report On: 10-JUN-06 05:16 AMATTN: BRETT MCLEOD

THIS REPORT SHALL NOT BE REPRODUCED EXCEPT IN FULL WITHOUT THE WRITTEN AUTHORITY OF THE LABORATORY.ANY REMAINING SAMPLES WILL BE DISPOSED OF AFTER 30 DAYS FOLLOWING ANALYSIS. PLEASE CONTACT THE LAB IF YOUREQUIRE ADDITIONAL SAMPLE STORAGE TIME.

PRELIMINARY RESULTS

Comments:

APPROVED BY: ____________________________________________

PATRICK CORBIELL

Project Manager

CEO3399 PHASE 700Job Reference: Project P.O. #:



ALS Canada LimitedEnvironmental Division

Part of the ALS Laboratory GroupBay 1, 245 MacDonald Cresent, Fort McMurray, AB T9H 4B5

Phone: +1 780 791 1524 Fax: +1 780 791 1586 www.alsglobal.comA Campbell Brothers Limited Company


L393340 CONTD....

2PAGE


of

CEO3399 PHASE 700

Qualifier* Batch

3

L393340-11 COMPOSITEBM on 26-MAY-06 @ 18:45Sample By:


Arsenic (As)



Mercury (Hg)

mg/kg



mg/kg

07-JUN-06



07-JUN-06

CVE



CVE

<0.05

<0.05<21.0

<0.2<0.01<0.1<0.12.36

<0.050.020.04

<0.05<0.12.95

<0.05<0.134.7

7030<5

<20<5

<0.550

0.150.14

0.07

Metals in Tissue

Metals in Tissue

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

Matrix:

R407772


R407620R407620R407620R407620R407620R407620R407620R407772R407772

R407772


AS-FAUNA-EDHG-FAUNA-EDMET1-FAUNA-EDMET2-FAUNA-EDP-FAUNA-EDSE-FAUNA-EDTI-FAUNA-ED


Arsenic (As)Mercury (Hg)Metals in TissueMetals in TissuePhosphorus (P)Selenium (Se)Titanium (Ti)

L393340 CONTD....

3PAGE of

CEO3399 PHASE 700



TissueTissueTissueTissueTissueTissueTissue

EPA 6020EPA 6020EPA 6020EPA 200.7EPA 200.7EPA 6020EPA 6020



EPA 200.3EPA 200.3EPA 200.3EPA 200.3EPA 200.3EPA 200.3EPA 200.3


GLOSSARY OF REPORT TERMSSurr - A surrogate is an organic compound that is similar to the target analyte(s) in chemical composition and behavior but not normally detected in environmental samples. Prior to sample processing, samples are fortified with one or more surrogate compounds.The reported surrogate recovery value provides a measure of method efficiency. The Laboratory control limits are determined under column heading D.L.mg/kg (units) - unit of concentration based on mass, parts per millionmg/L (units) - unit of concentration based on volume, parts per million< - Less thanD.L. - Detection LimitN/A - Result not available. Refer to qualifier code and definition for explanation







245664

3


Client:

Contact:


BRETT MCLEOD

Report Date: 10-JUN-06Workorder: L393340


AS-FAUNA-ED

HG-FAUNA-ED

MET1-FAUNA-ED

Tissue

Tissue

Tissue

R407772

R407772

R407772

Batch

Batch

Batch

CRM

DUP

MB

MS

CRM

DUP

MB

MS

CRM

DUP

WG451079-2

WG451079-3

WG451079-1

WG451079-4

WG451079-2

WG451079-3

WG451079-1

WG451079-4

WG451079-2

WG451079-3

DORM-2_FISH

L389813-10

L389813-10

DORM-2_FISH

L389813-10

L389813-10

DORM-2_FISH

L389813-10

Arsenic (As)

Arsenic (As)

Arsenic (As)

Arsenic (As)

Mercury (Hg)

Mercury (Hg)

Mercury (Hg)

Mercury (Hg)

Aluminum (Al)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Nickel (Ni)

Zinc (Zn)

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

108

<0.05

<0.05

110

63

0.08

<0.01

97

92

90

97

94

86

97

85

77

<2

<0.05

<0.1

<0.2

<0.01

<0.1

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

N/A

0.00

N/A

N/A

N/A

N/A

N/A

N/A

19

0.04

23

35

14

26

21

16

89-144

70-127

35-128

67-122

48-144

72-116

74-125

83-128

76-104

51-120

75-108

57-117

%

mg/kg

mg/kg

%

%

mg/kg

mg/kg

%

%

%

%

%

%

%

%

%

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

0.25

0.05

RPD-NA

J

RPD-NA

RPD-NA

RPD-NA

RPD-NA

RPD-NA

RPD-NA

<0.05

0.08

<2

<0.05

<0.1

<0.2

<0.01

<0.1

5




R407772BatchDUP

MB

MS

WG451079-3

WG451079-1

WG451079-4

L389813-10

L389813-10

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

<0.1

0.59

<0.02

<0.05

<0.02

<0.05

0.21

<0.05

<0.1

<0.1

4.7

<2

<0.05

<0.1

<0.2

<0.01

<0.1

<0.1

<0.05

<0.02

<0.05

<0.02

<0.05

<0.05

<0.05

<0.1

<0.1

<0.5

94

94

98

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

N/A

0.19

N/A

N/A

N/A

N/A

0.11

N/A

N/A

N/A

0.7

23

0.2

26

50

23

33

0.2

26

38

25

2

73-121

80-114

77-120

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

%

%

%

10

0.25

0.5

1

0.05

0.5

0.5

0.25

0.1

0.25

0.1

0.25

0.25

0.25

0.5

0.5

2.5

RPD-NA

J

RPD-NA

RPD-NA

RPD-NA

RPD-NA

J

RPD-NA

RPD-NA

RPD-NA

J

<0.1

0.39

<0.02

<0.05

<0.02

<0.05

0.33

<0.05

<0.1

<0.1

3.9

5



MET1-FAUNA-ED

MET2-FAUNA-ED

Tissue

Tissue

R407772

R407620

Batch

Batch

MS

CRM

DUP

MB

WG451079-4

WG451079-2

WG451079-3

WG451079-1

L389813-10

DORM-2_FISH

L389813-10

L389813-10

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

Silver (Ag)

Iron (Fe)

Manganese (Mn)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

93

89

121

97

99

93

96

105

109

98

106

102

134

55

103

99

230

<5

272

<0.5

3640

530

<20

<5

<5

<0.5

<20

<20

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

27

N/A

5.7

N/A

7.5

10

19

15

14

15

15

22

59-119

66-115

68-145

83-123

79-119

77-118

82-122

81-119

81-129

78-119

87-118

76-122

26-142

56-122

90-124

83-118

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

G

100

25

25

2.5

100

100

G

RPD-NA

RPD-NA

300

<5

257

<0.5

3370

480

5



MET2-FAUNA-ED

P-FAUNA-ED

SE-FAUNA-ED

TI-FAUNA-ED

Tissue

Tissue

Tissue

Tissue

R407620

R407620

R407772

R407772

Batch

Batch

Batch

Batch

MS

DUP

MB

MS

CRM

DUP

MB

MS

DUP

MB

MS

WG451079-4

WG451079-3

WG451079-1

WG451079-4

WG451079-2

WG451079-3

WG451079-1

WG451079-4

WG451079-3

WG451079-1

WG451079-4

L389813-10

L389813-10

L389813-10

DORM-2_FISH

L389813-10

L389813-10

L389813-10

L389813-10

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Phosphorus (P)

Phosphorus (P)

Phosphorus (P)

Selenium (Se)

Selenium (Se)

Selenium (Se)

Selenium (Se)

Titanium (Ti)

Titanium (Ti)

Titanium (Ti)

101

101

99

100

98

100

1820

60

94

113

0.27

<0.05

98

0.12

0.06

102

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

08-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

07-JUN-06

2.3

0.02

0.01

17

0.2

0.2

71-125

63-129

78-113

80-115

56-154

82-122

64-133

101-168

44-153

18-177

%

%

%

%

%

%

mg/kg

mg/kg

%

%

mg/kg

mg/kg

%

mg/kg

mg/kg

%

100

0.25

0.25

J

J

1870

0.29

0.11

5

Legend:

Qualifier:



ALS Laboratory Group Quality Control ReportPage 5 ofReport Date: 10-JUN-06Workorder: L393340 5

ANALYTICAL REPORT

Reported On: 25-JUL-06 04:31 PM

THIS REPORT SHALL NOT BE REPRODUCED EXCEPT IN FULL WITHOUT THE WRITTEN AUTHORITY OF THE LABORATORY.ALL SAMPLES WILL BE DISPOSED OF AFTER 30 DAYS FOLLOWING ANALYSIS. PLEASE CONTACT THE LAB IF YOUREQUIRE ADDITIONAL SAMPLE STORAGE TIME.

APPROVED BY: ____________________________________________

PATRICK CORBIELL

Project Manager

CE03399. PHASE 700

Comments:

Job Reference: Project P.O. #:

Other Information:


Bay 1, 245 MacDonald Cresent, Fort McMurray, AB T9H 4B5Phone: +1 780 791 1524 Fax: +1 780 791 1586 www.alsglobal.com

A Campbell Brothers Limited Company Now part of the ALS Laboratory Group



221 18 ST SE

CALGARY AB T2E 6J5

ATTN: BRETT MCLEODRevision: 1


L393516 CONTD....

2PAGE


of

CE03399. PHASE 700

Qualifier* Batch

10

L393516-1

L393516-2

NRPK-1 SITE 13A

NRPK-2 SITE 13A

BM on 29-MAY-06 @ 13:30

BM on 29-MAY-06 @ 13:30

Sampled By:

Sampled By:

TISSUE

TISSUE

Metals in Animal Tissue


Arsenic (As)



% MoistureMercury (Hg)

Arsenic (As)

Silver (Ag)Aluminum (Al)Barium (Ba)Beryllium (Be)Cadmium (Cd)Cobalt (Co)Chromium (Cr)Copper (Cu)Molybdenum (Mo)Nickel (Ni)Lead (Pb)Antimony (Sb)Tin (Sn)

mg/kg



%mg/kg

mg/kg

mg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kg

16-JUN-06

15-JUN-06



17-JUN-0615-JUN-06

15-JUN-06

15-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-06

CVE



CMMCVE

CVE

CVECVECVECVECVECVECVECVECVECVECVECVECVE

<0.05

<0.05<20.1

<0.2<0.01<0.10.2

0.34<0.05<0.02<0.02<0.05<0.10.30

<0.05<0.16.4

2203140291420<5

<0.519600.130.12

79.00.33

<0.05

<0.05<20.2

<0.2<0.01<0.10.2

0.30<0.05<0.02<0.02<0.05<0.1

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.10.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

Matrix:

Matrix:

RAMB

R411577


R411587R411587R411587R411587R411587R411587R411587R411577R411577

R410656R411577

R411577

R411577R411577R411577R411577R411577R411577R411577R411577R411577R411577R411577R411577R411577


L393516 CONTD....

3PAGE


of

CE03399. PHASE 700

Qualifier* Batch

10

L393516-2

L393516-3

NRPK-2 SITE 13A

NRPK-3 SITE 13A

BM on 29-MAY-06 @ 13:30

BM on 29-MAY-06 @ 13:30

Sampled By:

Sampled By:

TISSUE

TISSUE



Strontium (Sr)Thallium (Tl)Vanadium (V)Zinc (Zn)



Arsenic (As)



mg/kgmg/kgmg/kgmg/kg


%mg/kg

mg/kg



16-JUN-06

15-JUN-0615-JUN-0615-JUN-0615-JUN-06


17-JUN-0615-JUN-06

15-JUN-06



CVECVECVECVE


CMMCVE

CVE



0.28<0.05<0.15.2

2303970361480<5

<0.524700.100.11

79.70.17

<0.05

<0.05<20.1

<0.2<0.01<0.10.1

0.36<0.05<0.02<0.02<0.05<0.10.28

<0.05<0.16.2

2003450308460<5

<0.520200.140.12

Metals in Tissue

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.050.050.10.5

20205

205

0.520

0.050.05

0.10.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

Matrix:

Matrix:

RAMB

RAMB

R411577R411577R411577R411577

R411587R411587R411587R411587R411587R411587R411587R411577R411577

R410656R411577

R411577


R411587R411587R411587R411587R411587R411587R411587R411577R411577


L393516 CONTD....

4PAGE


of

CE03399. PHASE 700

Qualifier* Batch

10

L393516-3

L393516-4

L393516-5

NRPK-3 SITE 13A

NRPK-4 SITE 13A

NRPK-5 SITE 13A

BM on 29-MAY-06 @ 13:30

BM on 29-MAY-06 @ 13:30

BM on 29-MAY-06 @ 13:30

Sampled By:

Sampled By:

Sampled By:

TISSUE

TISSUE

TISSUE





Arsenic (As)




Arsenic (As)

Silver (Ag)Aluminum (Al)Barium (Ba)Beryllium (Be)Cadmium (Cd)

%mg/kg

mg/kg



%mg/kg

mg/kg

mg/kgmg/kgmg/kgmg/kgmg/kg

16-JUN-06

16-JUN-06

17-JUN-0615-JUN-06

15-JUN-06



17-JUN-0615-JUN-06

15-JUN-06

15-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-06

CMMCVE

CVE



CMMCVE

CVE

CVECVECVECVECVE

79.30.13

<0.05

<0.05<20.3

<0.2<0.01<0.10.1

0.39<0.05<0.02<0.02<0.05<0.10.51

<0.05<0.17.2

4303520313320<5

<0.522900.130.12

79.60.12

<0.05

<0.05<2

<0.1<0.2

<0.01

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.10.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.10.01

0.05

0.052

0.10.2

0.01

Matrix:

Matrix:

Matrix:

RAMB

R410656R411577

R411577


R411587R411587R411587R411587R411587R411587R411587R411577R411577

R410656R411577

R411577

R411577R411577R411577R411577R411577


L393516 CONTD....

5PAGE


of

CE03399. PHASE 700

Qualifier* Batch

10

L393516-5

L393516-6

NRPK-5 SITE 13A

NRPK-6 SITE 13A

BM on 29-MAY-06 @ 13:30

BM on 29-MAY-06 @ 13:30

Sampled By:

Sampled By:

TISSUE

TISSUE



Cobalt (Co)Chromium (Cr)Copper (Cu)Molybdenum (Mo)Nickel (Ni)Lead (Pb)Antimony (Sb)Tin (Sn)Strontium (Sr)Thallium (Tl)Vanadium (V)Zinc (Zn)



Arsenic (As)


Calcium (Ca)

mg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kg


%mg/kg

mg/kg


mg/kg

16-JUN-06

15-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-06


17-JUN-0615-JUN-06

15-JUN-06


15-JUN-06

CVECVECVECVECVECVECVECVECVECVECVECVE


CMMCVE

CVE


HAS

<0.10.1

0.42<0.050.02

<0.02<0.05<0.10.18

<0.05<0.15.7

1503850324290

9<0.522000.130.12

80.60.12

<0.05

<0.05<20.2

<0.2<0.01<0.10.1

0.30<0.05<0.02<0.02<0.05<0.10.34

<0.05<0.15.2

310

Metals in Tissue

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.10.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20

Matrix:

Matrix:

RAMB

RAMB

R411577R411577R411577R411577R411577R411577R411577R411577R411577R411577R411577R411577

R411587R411587R411587R411587R411587R411587R411587R411577R411577

R410656R411577

R411577


R411587


L393516 CONTD....

6PAGE


of

CE03399. PHASE 700

Qualifier* Batch

10

L393516-6

L393516-7

NRPK-6 SITE 13A

NRPK-7 SITE 13A

BM on 29-MAY-06 @ 13:30

BM on 29-MAY-06 @ 13:30

Sampled By:

Sampled By:

TISSUE

TISSUE



Potassium (K)Magnesium (Mg)Sodium (Na)Iron (Fe)Manganese (Mn)Phosphorus (P)Selenium (Se)Titanium (Ti)


Arsenic (As)




mg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kg

%mg/kg

mg/kg



%mg/kg

16-JUN-06

16-JUN-06

15-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-06

17-JUN-0615-JUN-06

15-JUN-06



17-JUN-0615-JUN-06

HASHASHASHASHASHASCVECVE

CMMCVE

CVE



CMMCVE

3730361380<50.6

23700.140.11

80.50.11

<0.05

<0.05<20.5

<0.2<0.01<0.10.2

0.31<0.050.03

<0.02<0.05<0.11.08

<0.05<0.18.4

10003620323530<51.6

25000.160.14

80.30.10

Metals in Tissue

Metals in Tissue

Metals in Tissue

205

205

0.520

0.050.05

0.10.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.10.01

Matrix:

Matrix:

RAMB

R411587R411587R411587R411587R411587R411587R411577R411577

R410656R411577

R411577


R411587R411587R411587R411587R411587R411587R411587R411577R411577

R410656R411577


L393516 CONTD....

7PAGE


of

CE03399. PHASE 700

Qualifier* Batch

10

L393516-8

L393516-9

NRPK-8 SITE 13A

NRPK-9 SITE 13A

BM on 29-MAY-06 @ 13:30

BM on 29-MAY-06 @ 13:30

Sampled By:

Sampled By:

TISSUE

TISSUE



Arsenic (As)




Arsenic (As)

Silver (Ag)Aluminum (Al)Barium (Ba)Beryllium (Be)Cadmium (Cd)Cobalt (Co)Chromium (Cr)Copper (Cu)Molybdenum (Mo)Nickel (Ni)Lead (Pb)Antimony (Sb)Tin (Sn)

mg/kg



%mg/kg

mg/kg

mg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kg

16-JUN-06

15-JUN-06



17-JUN-0615-JUN-06

15-JUN-06

15-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-0615-JUN-06

CVE



CMMCVE

CVE

CVECVECVECVECVECVECVECVECVECVECVECVECVE

<0.05

<0.05<20.1

<0.2<0.01<0.10.1

0.29<0.05<0.02<0.02<0.05<0.10.20

<0.05<0.16.2

1203350291370<5

<0.519100.130.12

81.40.07

<0.05

<0.05<20.4

<0.2<0.01<0.10.1

0.26<0.05<0.02<0.02<0.05<0.1

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.10.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

Matrix:

Matrix:

RAMB

R411577


R411587R411587R411587R411587R411587R411587R411587R411577R411577

R410656R411577

R411577

R411577R411577R411577R411577R411577R411577R411577R411577R411577R411577R411577R411577R411577


L393516 CONTD....

8PAGE


of

CE03399. PHASE 700

Qualifier* Batch

10

L393516-9

L393516-10

NRPK-9 SITE 13A

NRPK-10 SITE 13A

BM on 29-MAY-06 @ 13:30

BM on 29-MAY-06 @ 13:30

Sampled By:

Sampled By:

TISSUE

TISSUE



Strontium (Sr)Thallium (Tl)Vanadium (V)Zinc (Zn)



Arsenic (As)



mg/kgmg/kgmg/kgmg/kg


%mg/kg

mg/kg



16-JUN-06

15-JUN-0615-JUN-0615-JUN-0615-JUN-06


17-JUN-0615-JUN-06

15-JUN-06



CVECVECVECVE


CMMCVE

CVE



0.70<0.05<0.16.4

6703420307290<51.0

23500.130.12

79.80.08

<0.05

<0.054

0.3<0.2

<0.01<0.10.2

0.32<0.05<0.02<0.02<0.05<0.10.55

<0.05<0.17.1

5703500303390<50.5

24300.120.13

Metals in Tissue

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.050.050.10.5

20205

205

0.520

0.050.05

0.10.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

Matrix:

Matrix:

URNP

RAMB

URNP

RRV

RRV

RRV

RAMB

R411577R411577R411577R411577

R411587R411587R411587R411587R411587R411587R411587R411577R411577

R410656R411577

R411577


R411587R411587R411587R411587R411587R411587R411587R411577R411577


L393516 CONTD....

9PAGE


of

CE03399. PHASE 700

Qualifier* Batch

10

L393516-10 NRPK-10 SITE 13ABM on 29-MAY-06 @ 13:30Sampled By:

TISSUEMetals in Animal Tissue


%mg/kg

16-JUN-06 17-JUN-0615-JUN-06

CMMCVE

82.30.16

0.10.01

Matrix:

R410656R411577


AS-FAUNA-EDHG-FAUNA-EDMET1-FAUNA-EDMET2-FAUNA-EDMOISTURE-IN-ED

P-FAUNA-EDSE-FAUNA-EDTI-FAUNA-ED


Arsenic (As)Mercury (Hg)Metals in TissueMetals in Tissue% Moisture

Phosphorus (P)Selenium (Se)Titanium (Ti)

L393516 CONTD....

10PAGE of

CE03399. PHASE 700



TissueTissueTissueTissueTissue

TissueTissueTissue

RAMB

RRV

URNP

Result Adjusted For Method Blank

Reported Result Verified By Repeat Analysis

Unreliable: Result Not Reproducible

Sample Parameter Qualifier key listed:

EPA 6020EPA 6020EPA 6020EPA 200.7Gravimetric: Oven-dried @ 105C

EPA 200.7EPA 6020EPA 6020



Description Qualifier

EPA 200.3EPA 200.3EPA 200.3EPA 200.3

EPA 200.3EPA 200.3EPA 200.3


GLOSSARY OF REPORT TERMSSurr - A surrogate is an organic compound that is similar to the target analyte(s) in chemical composition and behavior but not normally detected in environmental samples. Prior to sample processing, samples are fortified with one or more surrogate compounds.The reported surrogate recovery value provides a measure of method efficiency. The Laboratory control limits are determined under column heading D.L.mg/kg (units) - unit of concentration based on mass, parts per million.mg/L (units) - unit of concentration based on volume, parts per million.< - Less than.D.L. - The reporting limit.N/A - Result not available. Refer to qualifier code and definition for explanation.







245666

10


Client:

Contact:


BRETT MCLEOD

Report Date: 25-JUL-06Workorder: L393516


AS-FAUNA-ED

HG-FAUNA-ED

MET1-FAUNA-ED

Tissue

Tissue

Tissue

R411577

R411577

R411577

Batch

Batch

Batch

CRM

CRM

DUP

MB

MB

MS

MS

CRM

CRM

DUP

MB

MB

MS

MS

CRM

WG455394-2

WG455396-2

WG455394-3

WG455394-1

WG455396-1

WG455394-4

WG455396-4

WG455394-2

WG455396-2

WG455394-3

WG455394-1

WG455396-1

WG455394-4

WG455396-4

WG455394-2

DORM-2_FISH

DORM-2_FISH

L393516-9

L393516-9

L393516-10

DORM-2_FISH

DORM-2_FISH

L393516-9

L393516-9

L393516-10

DORM-2_FISH

Arsenic (As)

Arsenic (As)

Arsenic (As)

Arsenic (As)

Arsenic (As)

Arsenic (As)

Arsenic (As)

Mercury (Hg)

Mercury (Hg)

Mercury (Hg)

Mercury (Hg)

Mercury (Hg)

Mercury (Hg)

Mercury (Hg)

Aluminum (Al)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

143

117

<0.05

<0.05

<0.05

113

98

93

80

0.09

<0.01

0.02

86

84

95

90

124

118

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

N/A

0.00

19

0.04

89-144

89-144

70-127

70-127

35-128

35-128

67-122

67-122

48-144

72-116

74-125

83-128

%

%

mg/kg

mg/kg

mg/kg

%

%

%

%

mg/kg

mg/kg

mg/kg

%

%

%

%

%

%

0.25

0.25

0.05

0.05

RPD-NA

J

<0.05

0.08

8

ALS Laboratory Group Quality Control ReportPage 2 ofReport Date: 25-JUL-06Workorder: L393516



R411577BatchCRM

CRM

DUP

MB

WG455394-2

WG455396-2

WG455394-3

WG455394-1

DORM-2_FISH

DORM-2_FISH

L393516-9

Copper (Cu)

Lead (Pb)

Nickel (Ni)

Zinc (Zn)

Aluminum (Al)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Nickel (Ni)

Zinc (Zn)

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

Antimony (Sb)

98

73

103

96

103

93

108

104

93

114

90

105

<2

<0.05

0.1

<0.2

<0.01

0.1

<0.1

0.30

<0.02

<0.05

<0.02

<0.05

0.23

<0.05

<0.1

<0.1

5.5

<0.05

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

N/A

N/A

0.2

N/A

N/A

0.0

N/A

0.04

N/A

N/A

N/A

N/A

0.46

N/A

N/A

N/A

15

23

35

0.4

26

21

0.4

23

0.2

26

50

23

33

0.2

26

38

25

25

76-104

51-120

75-108

57-117

48-144

72-116

74-125

83-128

76-104

51-120

75-108

57-117

%

%

%

%

%

%

%

%

%

%

%

%

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg 0.25

RPD-NA

RPD-NA

J

RPD-NA

RPD-NA

J

RPD-NA

J

RPD-NA

RPD-NA

RPD-NA

RPD-NA

J,G

RPD-NA

RPD-NA

RPD-NA

COMMENTS: Strontium value rechecked, data flagged as URNP.

<2

<0.05

0.4

<0.2

<0.01

0.1

<0.1

0.26

<0.02

<0.05

<0.02

<0.05

0.70

<0.05

<0.1

<0.1

6.4

8




R411577BatchMB

MB

MS

WG455394-1

WG455396-1

WG455394-4 L393516-9

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

0.2

<0.2

<0.01

<0.1

<0.1

0.10

<0.02

<0.05

0.03

<0.05

0.17

<0.05

<0.1

<0.1

2.4

<2

<0.05

0.1

<0.2

<0.01

<0.1

<0.1

0.09

<0.02

<0.05

<0.02

<0.05

0.13

<0.05

<0.1

<0.1

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

0.5

1

0.05

0.5

0.5

0.25

0.1

0.25

0.1

0.25

0.25

0.25

0.5

0.5

2.5

10

0.25

0.5

1

0.05

0.5

0.5

0.25

0.1

0.25

0.1

0.25

0.25

0.25

0.5

0.5

8




R411577BatchMS

MS

WG455394-4

WG455396-4

L393516-9

L393516-10

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

107

96

98

106

91

131

110

105

90

104

106

93

108

95

105

105

99

108

96

98

99

90

140

109

102

91

106

104

89

104

95

103

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

73-121

80-114

77-120

59-119

66-115

68-145

83-123

79-119

77-118

82-122

81-119

56-122

81-129

78-119

87-118

76-122

26-142

73-121

80-114

77-120

59-119

66-115

68-145

83-123

79-119

77-118

82-122

81-119

56-122

81-129

78-119

87-118

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

8



MET1-FAUNA-ED

MET2-FAUNA-ED

Tissue

Tissue

R411577

R411587

Batch

Batch

MS

CRM

CRM

DUP

DUP

MB

MB

WG455396-4

WG455394-2

WG455396-2

WG455394-3

WG455396-3

WG455394-1

WG455396-1

L393516-10

DORM-2_FISH

DORM-2_FISH

L393516-9

L393516-10

Vanadium (V)

Zinc (Zn)

Iron (Fe)

Manganese (Mn)

Iron (Fe)

Manganese (Mn)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

107

100

112

116

104

101

<5

304

<0.5

3530

310

<5

335

2.5

3340

390

30

<5

<5

<0.5

120

40

20

<5

12

<0.5

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

N/A

0.89

N/A

3.3

8.2

N/A

10

2.0

4.9

0.34

15

14

15

15

22

15

14

2

15

22

76-122

26-142

90-124

83-118

90-124

83-118

%

%

%

%

%

%

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

B

100

25

25

2.5

100

100

100

25

25

2.5

RPD-NA

RPD-NA

J

<5

307

1.0

3420

290

<5

303

0.5

3500

390

8



MET2-FAUNA-ED

MOISTURE-IN-ED

P-FAUNA-ED

SE-FAUNA-ED

Tissue

Tissue

Tissue

Tissue

R411587

R410656

R411587

Batch

Batch

Batch

MB

MS

MS

DUP

DUP

MB

MB

MS

MS

WG455396-1

WG455394-4

WG455396-4

WG456778-1

WG455394-3

WG455394-1

WG455396-1

WG455394-4

WG455396-4

L393516-9

L393516-10

L393516-10

L393516-9

L393516-9

L393516-10

Potassium (K)

Sodium (Na)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

% Moisture

Phosphorus (P)

Phosphorus (P)

Phosphorus (P)

Phosphorus (P)

Phosphorus (P)

30

50

105

104

105

103

97

103

94

101

103

101

98

104

81.8

2140

100

80

109

101

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

17-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

0.52

9.7

9.5

17

71-125

63-129

78-113

80-115

56-154

82-122

71-125

63-129

78-113

80-115

56-154

82-122

64-133

64-133

mg/kg

mg/kg

%

%

%

%

%

%

%

%

%

%

%

%

%

mg/kg

mg/kg

mg/kg

%

%

100

100

100

100

82.3

2350

8



SE-FAUNA-ED

TI-FAUNA-ED

Tissue

Tissue

R411577

R411577

Batch

Batch

CRM

CRM

DUP

MB

MB

MS

MS

DUP

MB

MB

MS

MS

WG455394-2

WG455396-2

WG455394-3

WG455394-1

WG455396-1

WG455394-4

WG455396-4

WG455394-3

WG455394-1

WG455396-1

WG455394-4

WG455396-4

DORM-2_FISH

DORM-2_FISH

L393516-9

L393516-9

L393516-10

L393516-9

L393516-9

L393516-10

Selenium (Se)

Selenium (Se)

Selenium (Se)

Selenium (Se)

Selenium (Se)

Selenium (Se)

Selenium (Se)

Titanium (Ti)

Titanium (Ti)

Titanium (Ti)

Titanium (Ti)

Titanium (Ti)

157

116

0.14

<0.05

<0.05

123

118

0.11

0.19

0.06

101

101

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

15-JUN-06

0.01

0.01

0.2

0.2

101-168

101-168

44-153

44-153

18-177

18-177

%

%

mg/kg

mg/kg

mg/kg

%

%

mg/kg

mg/kg

mg/kg

%

%

0.25

0.25

0.25

0.25

J

J

0.13

0.12

8

Legend:

Qualifier:



ALS Laboratory Group Quality Control ReportPage 8 ofReport Date: 25-JUL-06Workorder: L393516 8

Reported On: 20-NOV-06 08:07 PM


ROY JONESGeneral Manager, Edmonton

CE03399/01/700

Comments:


Other Information:


PRELIMINARY RESULTS

9936-67 Avenue, Edmonton, AB T6E 0P5Phone: +1 780 413 5227 Fax: +1 780 437 2311 www.alsglobal.com

A Campbell Brothers Limited Company

11-SEP-06Lab Work Order #: L431315 Date Received:


221 18 ST SE

CALGARY AB T2E 6J5

ATTN: RYAN FAULTER/BRETT MCLEOD

For any questions about this report please contact your Account Manager:

ERIN BEAUDIN

____________________________________________


L431315 CONTD....

2PAGE


of

Qualifier* Batch

9

L431315-1

L431315-2

F-1 SITE 3A

F-2 SITE 3A

RF on 10-SEP-06 @ 14:00

RF on 10-SEP-06 @ 14:00

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE



Arsenic (As)



Mercury (Hg)

Arsenic (As)

Silver (Ag)Aluminum (Al)Barium (Ba)Beryllium (Be)Cadmium (Cd)Cobalt (Co)Chromium (Cr)Copper (Cu)Molybdenum (Mo)Nickel (Ni)Lead (Pb)Antimony (Sb)Tin (Sn)Strontium (Sr)

mg/kg



mg/kg

mg/kg

mg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kg

04-NOV-06

04-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-06

03-NOV-0603-NOV-0603-NOV-0603-NOV-0603-NOV-0603-NOV-0603-NOV-0604-NOV-0603-NOV-06

04-NOV-06

04-NOV-06

04-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-06

JGP

JGPJGPJGPJGPJGPJGPJGPJGPJGPJGPJGPJGPJGPJGPJGPJGPJGP

HASHASHASHASHASHASHASJGPHAS

JGP

JGP

JGPJGPJGPJGPJGPJGPJGPJGPJGPJGPJGPJGPJGPJGP

<0.05

<0.05963.3

<0.2<0.01<0.1<0.10.67

<0.050.17

<0.02<0.05<0.110.2

<0.05<0.112.8

96102890341

108063

27.959800.070.46

0.02

0.05

<0.052744.8

<0.2<0.01

0.10.4

0.70<0.050.300.06

<0.05<0.111.7

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.05

Matrix:

Matrix:

R462975


R461818R461818R461818R461818R461818R461818R461818R462975R461818

R462975

R462975

R462975R462975R462975R462975R462975R462975R462975R462975R462975R462975R462975R462975R462975R462975


L431315 CONTD....

3PAGE


of

Qualifier* Batch

9

L431315-2

L431315-3

F-2 SITE 3A

F-3 SITE 3A

RF on 10-SEP-06 @ 14:00

RF on 10-SEP-06 @ 14:00

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE



Thallium (Tl)Vanadium (V)Zinc (Zn)


Mercury (Hg)

Arsenic (As)



Mercury (Hg)

mg/kgmg/kgmg/kg


mg/kg

mg/kg



mg/kg

04-NOV-0604-NOV-0604-NOV-06


04-NOV-06

04-NOV-06



04-NOV-06

JGPJGPJGP


JGP

JGP



JGP

<0.050.3

13.6

116002660382

113013127.57040<0.054.14

0.03

0.05

<0.05783.1

<0.2<0.01

0.10.2

0.90<0.050.290.03

<0.05<0.110.2

<0.050.1

16.1

115002730364

117011641.57110<0.051.19

0.03

Metals in Tissue

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

Matrix:

Matrix:

R462975R462975R462975

R461818R461818R461818R461818R461818R461818R461818R462975R461818

R462975

R462975


R461818R461818R461818R461818R461818R461818R461818R462975R461818

R462975


L431315 CONTD....

4PAGE


of

Qualifier* Batch

9

L431315-3

L431315-4

L431315-5

F-3 SITE 3A

F-4 SITE 3A

F-5 SITE 3A

RF on 10-SEP-06 @ 14:00

RF on 10-SEP-06 @ 14:00

RF on 10-SEP-06 @ 14:00

Sampled By:

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE

FISH TISSUE



Arsenic (As)



Mercury (Hg)

Arsenic (As)

Silver (Ag)Aluminum (Al)Barium (Ba)Beryllium (Be)Cadmium (Cd)Cobalt (Co)Chromium (Cr)Copper (Cu)Molybdenum (Mo)Nickel (Ni)

mg/kg



mg/kg

mg/kg

mg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kg

04-NOV-06



04-NOV-06

04-NOV-06

04-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-06

JGP



JGP

JGP

JGPJGPJGPJGPJGPJGPJGPJGPJGPJGP

0.36

<0.0538619.3<0.20.030.81.0

6.270.261.980.25

<0.05<0.164.5

<0.050.5102

773001830024107470467212

474000.592.05

0.27

0.06

<0.05552.8

<0.2<0.01

0.10.1

0.92<0.050.28

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.02

Matrix:

Matrix:

Matrix:

R462975


R461818R461818R461818R461818R461818R461818R461818R462975R461818

R462975

R462975

R462975R462975R462975R462975R462975R462975R462975R462975R462975R462975


L431315 CONTD....

5PAGE


of

Qualifier* Batch

9

L431315-5

L431315-6

F-5 SITE 3A

F-6 SITE 3A

RF on 10-SEP-06 @ 14:00

RF on 10-SEP-06 @ 14:00

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE



Lead (Pb)Antimony (Sb)Tin (Sn)Strontium (Sr)Thallium (Tl)Vanadium (V)Zinc (Zn)


Mercury (Hg)

Arsenic (As)


Calcium (Ca)Potassium (K)Magnesium (Mg)Sodium (Na)Iron (Fe)Manganese (Mn)Phosphorus (P)

mg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kg


mg/kg

mg/kg



04-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-06


04-NOV-06

04-NOV-06



JGPJGPJGPJGPJGPJGPJGP


JGP

JGP


HASHASHASHASHASHASHAS

0.03<0.05<0.18.66

<0.05<0.113.5

106002740349

116060

27.266700.070.08

0.04

0.06

<0.05723.9

<0.2<0.01

0.10.2

0.77<0.050.260.05

<0.05<0.18.52

<0.050.1

13.4

9940256034989069

33.66200

Metals in Tissue

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

Matrix:

Matrix:

R462975R462975R462975R462975R462975R462975R462975

R461818R461818R461818R461818R461818R461818R461818R462975R461818

R462975

R462975


R461818R461818R461818R461818R461818R461818R461818


L431315 CONTD....

6PAGE


of

Qualifier* Batch

9

L431315-6

L431315-7

L431315-8

F-6 SITE 3A

F-7 SITE 3A

F-8 SITE 3A

RF on 10-SEP-06 @ 14:00

RF on 10-SEP-06 @ 14:00

RF on 10-SEP-06 @ 14:00

Sampled By:

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE

FISH TISSUE




Selenium (Se)Titanium (Ti)

Mercury (Hg)

Arsenic (As)



Mercury (Hg)

Arsenic (As)


mg/kgmg/kg

mg/kg

mg/kg



mg/kg

mg/kg


04-NOV-0603-NOV-06

04-NOV-06

04-NOV-06



04-NOV-06

04-NOV-06

04-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-06

JGPHAS

JGP

JGP



JGP

JGP

JGPJGPJGPJGPJGP

0.070.48

0.03

0.06

<0.051082.8

<0.2<0.01<0.10.3

0.730.060.300.02

<0.05<0.19.32

<0.05<0.113.1

101002840363

102013132.76400<0.050.81

0.02

0.05

<0.05182.9

<0.2<0.01

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.01

Matrix:

Matrix:

Matrix:

R462975R461818

R462975

R462975


R461818R461818R461818R461818R461818R461818R461818R462975R461818

R462975

R462975

R462975R462975R462975R462975R462975


L431315 CONTD....

7PAGE


of

Qualifier* Batch

9

L431315-8

L431315-9

F-8 SITE 3A

F-9 SITE 3A

RF on 10-SEP-06 @ 14:00

RF on 10-SEP-06 @ 14:00

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE





Mercury (Hg)

Arsenic (As)


Calcium (Ca)Potassium (K)



mg/kg

mg/kg


mg/kgmg/kg

04-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-0604-NOV-06


04-NOV-06

04-NOV-06


03-NOV-0603-NOV-06

JGPJGPJGPJGPJGPJGPJGPJGPJGPJGPJGPJGP


JGP

JGP


HASHAS

0.10.1

0.79<0.050.25

<0.02<0.05<0.110.9

<0.05<0.114.2

11400228034198055

32.867500.090.39

0.03

<0.05

<0.05112.1

<0.2<0.01<0.10.1

0.68<0.050.21

<0.02<0.05<0.19.49

<0.05<0.112.1

96702510

Metals in Tissue

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

2020

Matrix:

Matrix:

R462975R462975R462975R462975R462975R462975R462975R462975R462975R462975R462975R462975

R461818R461818R461818R461818R461818R461818R461818R462975R461818

R462975

R462975


R461818R461818


L431315 CONTD....

8PAGE


of

Qualifier* Batch

9

L431315-9

L431315-10

F-9 SITE 3A

F-10 SITE 3A

RF on 10-SEP-06 @ 14:00

RF on 10-SEP-06 @ 14:00

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE



Magnesium (Mg)Sodium (Na)Iron (Fe)Manganese (Mn)Phosphorus (P)Selenium (Se)Titanium (Ti)

Mercury (Hg)

Arsenic (As)



Mercury (Hg)


mg/kg

mg/kg



mg/kg


04-NOV-06

11-NOV-06



11-NOV-06

HASHASHASHASHASJGPHAS

JGP

JGP



JGP

33192042

21.461400.080.07

0.02

<0.05

<0.05122.4

<0.2<0.01

0.1<0.10.76

<0.050.24

<0.02<0.05<0.19.66

<0.05<0.115.9

107002540341

103066

25.064500.150.16

0.03

Metals in Tissue

Metals in Tissue

Metals in Tissue

5205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

Matrix:

Matrix:

R461818R461818R461818R461818R461818R462975R461818

R462975

R466347


R461818R461818R461818R461818R461818R461818R461818R466347R461818

R466347


AS-FAUNA-EDHG-FAUNA-ED

MET1-FAUNA-EDMET2-FAUNA-EDP-FAUNA-ED

SE-FAUNA-EDTI-FAUNA-ED


Arsenic (As)Mercury (Hg)

Metals in TissueMetals in TissuePhosphorus (P)


L431315 CONTD....

9PAGE of



TissueTissue

TissueTissueTissue

TissueTissue

EPA 6020EPA 6020

EPA 6020EPA 200.7EPA 200.7

EPA 6020EPA 200.7



EPA 200.3EPA 200.3

EPA 200.3EPA 200.3EPA 200.3

EPA 200.3EPA 200.3









246150

9


Client:

Contact:


RYAN FAULTER/BRETT MCLEOD

Report Date: 20-NOV-06Workorder: L431315


AS-FAUNA-ED

HG-FAUNA-ED

MET1-FAUNA-ED

Tissue

Tissue

Tissue

R462975

R466347

R462975

R466347

R462975

Batch

Batch

Batch

Batch

Batch

CRM

MB

MS

CRM

MB

MS

CRM

MB

WG519274-2

WG519274-1

WG519274-3

WG519274-2

WG519274-1

WG519274-3

WG519274-2

WG519274-1

DORM-2_FISH

L431315-10

DORM-2_FISH

L431315-10

DORM-2_FISH

Arsenic (As)

Arsenic (As)

Arsenic (As)

Mercury (Hg)

Mercury (Hg)

Mercury (Hg)

Aluminum (Al)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Nickel (Ni)

Zinc (Zn)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

110

<0.05

123

72

0.02

78

112

103

95

110

94

88

95

74

<0.05

<0.1

<0.2

<0.01

<0.1

<0.1

04-NOV-06

04-NOV-06

11-NOV-06

04-NOV-06

04-NOV-06

11-NOV-06

04-NOV-06

04-NOV-06

04-NOV-06

04-NOV-06

04-NOV-06

04-NOV-06

04-NOV-06

04-NOV-06

04-NOV-06

04-NOV-06

04-NOV-06

04-NOV-06

04-NOV-06

04-NOV-06

89-144

70-127

44-138

67-122

48-144

72-116

74-125

88-137

79-110

51-120

75-108

57-117

%

mg/kg

%

%

mg/kg

%

%

%

%

%

%

%

%

%

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

0.25

0.05

0.25

0.5

1

0.05

0.5

0.5

5

ALS Laboratory Group Quality Control ReportPage 2 ofReport Date: 20-NOV-06Workorder: L431315


MET1-FAUNA-ED

MET2-FAUNA-ED

Tissue

Tissue

R462975

R466347

Batch

Batch

MB

MS

WG519274-1

WG519274-3 L431315-10

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

Aluminum (Al)

Antimony (Sb)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Lead (Pb)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

Barium (Ba)

Copper (Cu)

Molybdenum (Mo)

Nickel (Ni)

<0.05

<0.02

<0.05

0.03

<0.05

0.17

<0.05

<0.1

<0.1

1.0

25

101

83

82

86

94

107

93

95

116

102

85

64

76

74

125

120

04-NOV-06

04-NOV-06

04-NOV-06

04-NOV-06

04-NOV-06

04-NOV-06

04-NOV-06

04-NOV-06

04-NOV-06

04-NOV-06

04-NOV-06

11-NOV-06

11-NOV-06

11-NOV-06

11-NOV-06

11-NOV-06

11-NOV-06

11-NOV-06

11-NOV-06

11-NOV-06

11-NOV-06

11-NOV-06

11-NOV-06

11-NOV-06

11-NOV-06

11-NOV-06

11-NOV-06

80-114

59-119

66-115

68-145

83-123

77-118

56-122

81-129

78-119

87-118

76-122

26-142

77-120

79-119

82-122

81-119

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

A

G

G

G

G

0.25

0.1

0.25

0.1

0.25

0.25

0.25

0.5

0.5

2.5

10

5



MET2-FAUNA-ED

P-FAUNA-ED

SE-FAUNA-ED

TI-FAUNA-ED

Tissue

Tissue

Tissue

Tissue

R461818

R461818

R462975

R466347

Batch

Batch

Batch

Batch

CRM

MB

MS

MB

MS

CRM

MB

MS

WG519274-2

WG519274-1

WG519274-3

WG519274-1

WG519274-3

WG519274-2

WG519274-1

WG519274-3

DORM-2_FISH

L431315-10

L431315-10

DORM-2_FISH

L431315-10

Iron (Fe)

Manganese (Mn)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Phosphorus (P)

Phosphorus (P)

Selenium (Se)

Selenium (Se)

Selenium (Se)

101

91

<20

<5

<5

<0.5

40

<20

87

96

95

95

102

99

20

95

125

<0.05

101

03-NOV-06

03-NOV-06

03-NOV-06

03-NOV-06

03-NOV-06

03-NOV-06

03-NOV-06

03-NOV-06

03-NOV-06

03-NOV-06

03-NOV-06

03-NOV-06

03-NOV-06

03-NOV-06

03-NOV-06

03-NOV-06

04-NOV-06

04-NOV-06

11-NOV-06

90-124

83-118

71-125

63-129

78-113

80-115

56-154

82-122

64-133

101-168

44-153

%

%

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

%

%

%

%

%

%

mg/kg

%

%

mg/kg

%

100

25

25

2.5

100

100

100

0.25

5



TI-FAUNA-ED Tissue

R461818BatchMB

MS

WG519274-1

WG519274-3 L431315-10

Titanium (Ti)

Titanium (Ti)

0.13

103

03-NOV-06

03-NOV-0682-124

mg/kg

%

0.25

5

Legend:

Qualifier:

RPD-NA Relative Percent Difference Not Available due to result(s) being less than detection limit.A Method blank exceeds acceptance limit. Blank correction not applied, unless the qualifier "RAMB" (result adjusted for method blank) appears in the Analytical Report.B Method blank result exceeds acceptance limit, however, it is less than 5% of sample concentration. Blank correction not applied. E Matrix spike recovery may fall outside the acceptance limits due to high sample background. F Silver recovery low, likely due to elevated chloride levels in sample. G Outlier - No assignable cause for nonconformity has been determined.J Duplicate results and limit(s) are expressed in terms of absolute difference.K The sample referenced above is of a non-standard matrix type; standard QC acceptance criteria may not be achievable. L Low matrix spike recovery due to instability of spiked analyte in the sample matrix.


ALS Laboratory Group Quality Control ReportPage 5 ofReport Date: 20-NOV-06Workorder: L431315 5

Reported On: 30-NOV-06 08:10 PM



CE03399 PHASE 700

Comments:


Other Information:


PRELIMINARY RESULTS





221 18 ST SE

CALGARY AB T2E 6J5

ATTN: RYAN FAULTER / BRETT MCLEOD


ERIN BEAUDIN

____________________________________________


L432784 CONTD....

2PAGE


of

CE03399 PHASE 700

Qualifier* Batch

3

L432784-11 COMPOSITERF on 12-SEP-06 @ 10:00Sampled By:


Arsenic (As)



Mercury (Hg)

mg/kg



mg/kg

26-NOV-06



26-NOV-06

JGP



JGP

<0.05

<0.05<2

<0.1<0.2

<0.01<0.1<0.10.16

<0.05<0.02<0.02<0.05<0.10.32

<0.05<0.15.4

87802700373

1010425.5

61700.49

<0.05

0.45

Metals in Tissue

Metals in Tissue

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

Matrix:

R471371


R469585R469585R469585R469585R469585R469585R469585R471371R469585

R471371









L432784 CONTD....

3PAGE of

CE03399 PHASE 700



TissueTissue

TissueTissueTissue

TissueTissue

EPA 6020EPA 6020

EPA 6020EPA 200.7EPA 200.7

EPA 6020EPA 200.7



EPA 200.3EPA 200.3

EPA 200.3EPA 200.3EPA 200.3

EPA 200.3EPA 200.3









246151

3


Client:

Contact:


RYAN FAULTER / BRETT MCLEOD

Report Date: 30-NOV-06Workorder: L432784


AS-FAUNA-ED

HG-FAUNA-ED

MET1-FAUNA-ED

Tissue

Tissue

Tissue

R471371

R471371

R471371

Batch

Batch

Batch

CRM

DUP

MB

CRM

MB

CRM

DUP

WG529032-2

WG529032-3

WG529032-1

WG529032-2

WG529032-1

WG529032-2

WG529032-3

DORM-2_FISH

DORM-2_FISH

DORM-2_FISH

Arsenic (As)

Arsenic (As)

Arsenic (As)

Mercury (Hg)

Mercury (Hg)

Aluminum (Al)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Nickel (Ni)

Zinc (Zn)

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

104

<0.05

<0.05

70

0.02

103

96

97

107

88

89

92

86

<2

<0.05

<0.1

<0.2

<0.01

<0.1

<0.1

0.20

<0.02

<0.05

<0.02

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

N/A

N/A

N/A

N/A

N/A

N/A

N/A

N/A

0.01

N/A

N/A

N/A

19

23

35

14

26

21

16

23

0.2

26

50

23

89-144

44-138

48-144

72-116

74-125

88-137

79-110

51-120

75-108

57-117

%

mg/kg

mg/kg

%

mg/kg

%

%

%

%

%

%

%

%

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

0.25

0.05

RPD-NA

RPD-NA

RPD-NA

RPD-NA

RPD-NA

RPD-NA

RPD-NA

RPD-NA

J

RPD-NA

RPD-NA

RPD-NA

N/A

N/A

N/A

N/A

N/A

N/A

N/A

N/A

N/A

N/A

N/A

N/A

5



MET1-FAUNA-ED

MET2-FAUNA-ED

Tissue

Tissue

R471371

R469585

Batch

Batch

DUP

MB

CRM

DUP

WG529032-3

WG529032-1

WG529032-2

WG529032-3

DORM-2_FISH

Silver (Ag)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

Iron (Fe)

Manganese (Mn)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

<0.05

<0.05

<0.1

<0.1

5.1

<2

<0.05

0.1

<0.2

<0.01

<0.1

<0.1

0.06

<0.02

<0.05

<0.02

<0.05

0.12

<0.05

<0.1

<0.1

1.7

103

92

<5

308

<0.5

3580

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

25-NOV-06

25-NOV-06

25-NOV-06

25-NOV-06

25-NOV-06

25-NOV-06

N/A

N/A

N/A

N/A

12

N/A

10

N/A

13

33

26

38

25

25

15

14

15

15

90-124

83-118

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

%

%

mg/kg

mg/kg

mg/kg

mg/kg

10

0.25

0.5

1

0.05

0.5

0.5

0.25

0.1

0.25

0.1

0.25

0.25

0.25

0.5

0.5

2.5

RPD-NA

RPD-NA

RPD-NA

RPD-NA

RPD-NA

RPD-NA

N/A

N/A

N/A

N/A

N/A

N/A

N/A

N/A

N/A

5



MET2-FAUNA-ED

P-FAUNA-ED

SE-FAUNA-ED

TI-FAUNA-ED

Tissue

Tissue

Tissue

Tissue

R469585

R469585

R471371

R469585

Batch

Batch

Batch

Batch

DUP

MB

MS

MB

MS

CRM

DUP

MB

DUP

MB

WG529032-3

WG529032-1

WG529032-4

WG529032-1

WG529032-4

WG529032-2

WG529032-3

WG529032-1

WG529032-3

WG529032-1

L450406-95

L450406-95

DORM-2_FISH

Sodium (Na)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Phosphorus (P)

Phosphorus (P)

Selenium (Se)

Selenium (Se)

Selenium (Se)

Titanium (Ti)

Titanium (Ti)

250

20

<5

<5

<0.5

<20

<20

101

101

101

100

102

98

<20

105

120

0.28

<0.05

0.30

0.27

25-NOV-06

25-NOV-06

25-NOV-06

25-NOV-06

25-NOV-06

25-NOV-06

25-NOV-06

25-NOV-06

25-NOV-06

25-NOV-06

25-NOV-06

25-NOV-06

25-NOV-06

25-NOV-06

25-NOV-06

26-NOV-06

26-NOV-06

26-NOV-06

25-NOV-06

25-NOV-06

7.7

0.03

0.04

22

0.2

0.2

71-125

63-129

78-113

80-115

56-154

82-122

64-133

101-168

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

%

%

%

%

%

%

mg/kg

%

%

mg/kg

mg/kg

mg/kg

mg/kgA

100

25

25

2.5

100

100

100

0.25

0.25

J

J

N/A

N/A

N/A

5



TI-FAUNA-ED Tissue

R469585BatchMSWG529032-4 L450406-95

Titanium (Ti) 104 25-NOV-0682-124%

5

Legend:

Qualifier:



ALS Laboratory Group Quality Control ReportPage 5 ofReport Date: 30-NOV-06Workorder: L432784 5

Reported On: 31-OCT-06 08:21 PM



CE03399 PHASE 700

Comments:


Other Information:


PRELIMINARY RESULTS





221 18 ST SE

CALGARY AB T2E 6J5

ATTN: RYAN FAULTER / BRETT MCLEOD


ERIN BEAUDIN

____________________________________________


L432785 CONTD....

2PAGE


of

CE03399 PHASE 700

Qualifier* Batch

9

L432785-1

L432785-2

SITE 79 FF-1

SITE 79 FF-2

RW on 12-SEP-06

RW on 12-SEP-06

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE



Arsenic (As)



Mercury (Hg)

Arsenic (As)


mg/kg



mg/kg

mg/kg


26-OCT-06

26-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-06

25-OCT-0625-OCT-0625-OCT-0625-OCT-0625-OCT-0625-OCT-0625-OCT-0626-OCT-0625-OCT-06

26-OCT-06

26-OCT-06

26-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-06

JGP


SYFSYFSYFSYFSYFSYFSYFJGPSYF

JGP

JGP


0.08

<0.055

2.2<0.2

<0.01<0.1<0.11.18

<0.050.13

<0.02<0.05<0.111.2

<0.05<0.122.1

70902930315950583.4

50400.09

<0.05

0.02

0.09

<0.059

2.1<0.2

<0.01<0.1<0.11.330.050.14

<0.02<0.05<0.110.6

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.05

Matrix:

Matrix:

R459910


R458203R458203R458203R458203R458203R458203R458203R459910R458203

R459910

R459910

R459910R459910R459910R459910R459910R459910R459910R459910R459910R459910R459910R459910R459910R459910


L432785 CONTD....

3PAGE


of

CE03399 PHASE 700

Qualifier* Batch

9

L432785-2

L432785-3

SITE 79 FF-2

SITE 79 FF-3

RW on 12-SEP-06

RW on 12-SEP-06

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE





Mercury (Hg)

Arsenic (As)



Mercury (Hg)

mg/kgmg/kgmg/kg


mg/kg

mg/kg



mg/kg

26-OCT-0626-OCT-0626-OCT-06


26-OCT-06

26-OCT-06



26-OCT-06

JGPJGPJGP


JGP

JGP



JGP

<0.05<0.124.4

74903200325930494.6

53600.13

<0.05

0.03

0.09

<0.054

2.4<0.2

<0.01<0.1<0.12.77

<0.050.16

<0.02<0.05<0.112.0

<0.05<0.126.5

76203240317950484.4

54600.16

<0.05

0.02

Metals in Tissue

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

Matrix:

Matrix:

R459910R459910R459910

R458203R458203R458203R458203R458203R458203R458203R459910R458203

R459910

R459910


R458203R458203R458203R458203R458203R458203R458203R459910R458203

R459910


L432785 CONTD....

4PAGE


of

CE03399 PHASE 700

Qualifier* Batch

9

L432785-3

L432785-4

L432785-5

SITE 79 FF-3

SITE 79 FF-4

SITE 79 FF-5

RW on 12-SEP-06

RW on 12-SEP-06

RW on 12-SEP-06

Sampled By:

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE

FISH TISSUE



Arsenic (As)



Mercury (Hg)

Arsenic (As)


mg/kg



mg/kg

mg/kg


26-OCT-06



26-OCT-06

26-OCT-06

26-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-06

JGP



JGP

JGP


0.08

<0.053

1.7<0.2

<0.01<0.1<0.11.91

<0.050.15

<0.02<0.05<0.111.7

<0.05<0.127.5

69203040310860544.9

50800.10

<0.05

0.02

0.09

<0.053

1.9<0.2

<0.01<0.1<0.11.73

<0.050.15

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.02

Matrix:

Matrix:

Matrix:

R459910


R458203R458203R458203R458203R458203R458203R458203R459910R458203

R459910

R459910

R459910R459910R459910R459910R459910R459910R459910R459910R459910R459910


L432785 CONTD....

5PAGE


of

CE03399 PHASE 700

Qualifier* Batch

9

L432785-5

L432785-6

SITE 79 FF-5

SITE 79 FF-6

RW on 12-SEP-06

RW on 12-SEP-06

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE





Mercury (Hg)

Arsenic (As)





mg/kg

mg/kg



26-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-06


26-OCT-06

26-OCT-06





JGP

JGP


SYFSYFSYFSYFSYFSYFSYF

<0.02<0.05<0.112.4

<0.05<0.126.7

76103100324900473.7

54300.16

<0.05

0.02

0.13

<0.054

1.9<0.2

<0.01<0.1<0.11.88

<0.050.13

<0.02<0.05<0.111.4

<0.05<0.119.8

64203110313820943.2

4840

Metals in Tissue

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

Matrix:

Matrix:

R459910R459910R459910R459910R459910R459910R459910

R458203R458203R458203R458203R458203R458203R458203R459910R458203

R459910

R459910


R458203R458203R458203R458203R458203R458203R458203


L432785 CONTD....

6PAGE


of

CE03399 PHASE 700

Qualifier* Batch

9

L432785-6

L432785-7

L432785-8

SITE 79 FF-6

SITE 79 FF-7

SITE 79 FF-8

RW on 12-SEP-06

RW on 12-SEP-06

RW on 12-SEP-06

Sampled By:

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE

FISH TISSUE





Mercury (Hg)

Arsenic (As)



Mercury (Hg)

Arsenic (As)


mg/kgmg/kg

mg/kg

mg/kg



mg/kg

mg/kg


26-OCT-0625-OCT-06

26-OCT-06

26-OCT-06



26-OCT-06

26-OCT-06

26-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-06

JGPSYF

JGP

JGP



JGP

JGP

JGPJGPJGPJGPJGP

0.16<0.05

0.02

0.11

<0.053

1.9<0.2

<0.01<0.1<0.11.840.050.18

<0.02<0.05<0.113.3

<0.05<0.124.3

87403090329960473.3

58500.12

<0.05

0.03

0.08

<0.054

1.6<0.2

<0.01

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.01

Matrix:

Matrix:

Matrix:

R459910R458203

R459910

R459910


R458203R458203R458203R458203R458203R458203R458203R459910R458203

R459910

R459910

R459910R459910R459910R459910R459910


L432785 CONTD....

7PAGE


of

CE03399 PHASE 700

Qualifier* Batch

9

L432785-8

L432785-9

SITE 79 FF-8

SITE 79 FF-9

RW on 12-SEP-06

RW on 12-SEP-06

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE





Mercury (Hg)

Arsenic (As)





mg/kg

mg/kg


mg/kgmg/kg

26-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-0626-OCT-06


26-OCT-06

26-OCT-06


25-OCT-0625-OCT-06



JGP

JGP


SYFSYF

<0.1<0.12.18

<0.050.16

<0.02<0.05<0.111.9

<0.05<0.125.5

73502870299870264.4

52000.11

<0.05

0.02

0.13

<0.052

1.5<0.2

<0.01<0.1<0.12.61

<0.050.18

<0.02<0.05<0.112.9

<0.05<0.130.9

78303100

Metals in Tissue

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

2020

Matrix:

Matrix:

R459910R459910R459910R459910R459910R459910R459910R459910R459910R459910R459910R459910

R458203R458203R458203R458203R458203R458203R458203R459910R458203

R459910

R459910


R458203R458203


L432785 CONTD....

8PAGE


of

CE03399 PHASE 700

Qualifier* Batch

9

L432785-9

L432785-10

SITE 79 FF-9

SITE 79 FF-10

RW on 12-SEP-06

RW on 12-SEP-06

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE




Mercury (Hg)

Arsenic (As)



Mercury (Hg)


mg/kg

mg/kg



mg/kg


26-OCT-06

26-OCT-06



26-OCT-06

SYFSYFSYFSYFSYFJGPSYF

JGP

JGP



JGP

318820463.8

54500.18

<0.05

0.03

0.08

<0.053

1.8<0.2

<0.01<0.1<0.12.03

<0.050.160.03

<0.05<0.111.3

<0.05<0.126.9

70602960307900343.8

51800.16

<0.05

0.02

Metals in Tissue

Metals in Tissue

Metals in Tissue

5205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

Matrix:

Matrix:

R458203R458203R458203R458203R458203R459910R458203

R459910

R459910


R458203R458203R458203R458203R458203R458203R458203R459910R458203

R459910









L432785 CONTD....

9PAGE of

CE03399 PHASE 700



TissueTissue

TissueTissueTissue

TissueTissue

EPA 6020EPA 6020

EPA 6020EPA 200.7EPA 200.7

EPA 6020EPA 200.7



EPA 200.3EPA 200.3

EPA 200.3EPA 200.3EPA 200.3

EPA 200.3EPA 200.3









246153

9


Client:

Contact:


RYAN FAULTER / BRETT MCLEOD

Report Date: 31-OCT-06Workorder: L432785


AS-FAUNA-ED

HG-FAUNA-ED

MET1-FAUNA-ED

Tissue

Tissue

Tissue

R459910

R459910

R459910

Batch

Batch

Batch

CRM

MB

MS

CRM

MB

MS

CRM

MB

WG515261-2

WG515261-1

WG515261-3

WG515261-2

WG515261-1

WG515261-3

WG515261-2

WG515261-1

DORM-2_FISH

L432785-10

DORM-2_FISH

L432785-10

DORM-2_FISH

Arsenic (As)

Arsenic (As)

Arsenic (As)

Mercury (Hg)

Mercury (Hg)

Mercury (Hg)

Aluminum (Al)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Nickel (Ni)

Zinc (Zn)

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Lead (Pb)

Molybdenum (Mo)

101

<0.05

115

68

<0.01

87

73

108

90

107

93

76

90

86

<2

<0.05

0.5

<0.2

<0.01

<0.1

<0.1

0.08

<0.05

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

89-144

70-127

44-138

67-122

48-144

72-116

74-125

88-137

79-110

51-120

75-108

57-117

%

mg/kg

%

%

mg/kg

%

%

%

%

%

%

%

%

%

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

0.25

0.05

10

0.25

0.5

1

0.05

0.5

0.5

0.1

0.25

4

ALS Laboratory Group Quality Control ReportPage 2 ofReport Date: 31-OCT-06Workorder: L432785


MET1-FAUNA-ED

MET2-FAUNA-ED

Tissue

Tissue

R459910

R458203

Batch

Batch

MB

MS

CRM

MB

WG515261-1

WG515261-3

WG515261-2

WG515261-1

L432785-10

DORM-2_FISH

Nickel (Ni)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

Copper (Cu)

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

Iron (Fe)

Manganese (Mn)

Calcium (Ca)

<0.02

<0.05

<0.05

<0.05

<0.1

<0.1

2.1

0.30

88

97

94

95

91

97

108

92

94

97

104

69

63

101

101

97

3

94

72

<20

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

25-OCT-06

25-OCT-06

25-OCT-06

73-121

80-114

77-120

59-119

66-115

68-145

83-123

79-119

77-118

82-122

81-119

56-122

81-129

78-119

87-118

76-122

26-142

90-124

83-118

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

mg/kg

A

E

E

G

0.1

0.25

0.25

0.25

0.5

0.5

2.5

0.25

100

4

ALS Laboratory Group Quality Control ReportPage 3 ofReport Date: 31-OCT-06Workorder: L432785


MET2-FAUNA-ED

P-FAUNA-ED

SE-FAUNA-ED

TI-FAUNA-ED

Tissue

Tissue

Tissue

Tissue

R458203

R458203

R459910

R458203

Batch

Batch

Batch

Batch

MB

MS

MB

MS

CRM

MB

MS

MB

MS

WG515261-1

WG515261-3

WG515261-1

WG515261-3

WG515261-2

WG515261-1

WG515261-3

WG515261-1

WG515261-3

L432785-10

L432785-10

DORM-2_FISH

L432785-10

L432785-10

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Phosphorus (P)

Phosphorus (P)

Selenium (Se)

Selenium (Se)

Selenium (Se)

Titanium (Ti)

Titanium (Ti)

<5

5

<0.5

<20

<20

101

98

97

97

109

101

<20

98

98

<0.05

118

0.07

100

25-OCT-06

25-OCT-06

25-OCT-06

25-OCT-06

25-OCT-06

25-OCT-06

25-OCT-06

25-OCT-06

25-OCT-06

25-OCT-06

25-OCT-06

25-OCT-06

25-OCT-06

26-OCT-06

26-OCT-06

26-OCT-06

25-OCT-06

25-OCT-06

71-125

63-129

78-113

80-115

56-154

82-122

64-133

101-168

44-153

82-124

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

%

%

%

%

%

%

mg/kg

%

%

mg/kg

%

mg/kg

%

G

25

25

2.5

100

100

100

0.25

0.25

4

Legend:

Qualifier:



ALS Laboratory Group Quality Control ReportPage 4 ofReport Date: 31-OCT-06Workorder: L432785 4

ANALYTICAL REPORT

Reported On: 04-DEC-06 09:03 AM



CE03399 PHASE 700

Comments:


Other Information:

Legal Site Desc: 246154, 246155CofC Numbers:





221 18 ST SE

CALGARY AB T2E 6J5

ATTN: RYAN FAULTER/BRETT MCLEOD


ERIN BEAUDIN

Revision: 1

____________________________________________


L433144 CONTD....

2PAGE


of

CE03399 PHASE 700

Qualifier* Batch

16

L433144-1

L433144-2

LF-1 TELEPHONE LAKE

LF-2 TELEPHONE LAKE

RF on 13-SEP-06

RF on 13-SEP-06

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE



Arsenic (As)



Mercury (Hg)

Arsenic (As)


mg/kg



mg/kg

mg/kg


21-NOV-06



21-NOV-06

21-NOV-06


JGP


HASHASHASHASHASHASHASJGPJGP

JGP

JGP


<0.05

<0.05<2

<0.1<0.2

<0.01<0.10.2

0.41<0.050.02

<0.02<0.05<0.10.21

<0.05<0.15.5

2903900328480<5

<0.520900.100.90

0.02

<0.05

<0.05<20.1

<0.2<0.01<0.10.1

0.44<0.05<0.02<0.02<0.05<0.10.18

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.05

Matrix:

Matrix:

R467505


R469138R469138R469138R469138R469138R469138R469138R467505R467505

R467505

R467505

R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505


L433144 CONTD....

3PAGE


of

CE03399 PHASE 700

Qualifier* Batch

16

L433144-2

L433144-3

LF-2 TELEPHONE LAKE

LF-3 TELEPHONE LAKE

RF on 13-SEP-06

RF on 13-SEP-06

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE





Mercury (Hg)

Arsenic (As)



Mercury (Hg)

mg/kgmg/kgmg/kg


mg/kg

mg/kg



mg/kg

21-NOV-0621-NOV-0621-NOV-06


21-NOV-06

21-NOV-06



21-NOV-06

JGPJGPJGP


JGP

JGP



JGP

<0.05<0.15.7

1604110329440<5

<0.520800.090.86

0.02

<0.05

<0.05<20.2

<0.2<0.01<0.10.1

0.33<0.050.04

<0.02<0.05<0.11.58

<0.05<0.15.1

19303740358350<5

<0.528000.080.93

0.02

Metals in Tissue

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

Matrix:

Matrix:

R467505R467505R467505

R469138R469138R469138R469138R469138R469138R469138R467505R467505

R467505

R467505


R469138R469138R469138R469138R469138R469138R469138R467505R467505

R467505


L433144 CONTD....

4PAGE


of

CE03399 PHASE 700

Qualifier* Batch

16

L433144-3

L433144-4

L433144-5

LF-3 TELEPHONE LAKE

LF-4 TELEPHONE LAKE

LF-5 TELEPHONE LAKE

RF on 13-SEP-06

RF on 13-SEP-06

RF on 13-SEP-06

Sampled By:

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE

FISH TISSUE



Arsenic (As)



Mercury (Hg)

Arsenic (As)


mg/kg



mg/kg

mg/kg


21-NOV-06



21-NOV-06

21-NOV-06


JGP



JGP

JGP


<0.05

<0.05<2

<0.1<0.2

<0.01<0.10.1

0.34<0.05<0.02<0.02<0.05<0.10.11

<0.05<0.15.4

1403830324430<5

<0.520800.070.85

0.03

<0.05

<0.05<2

<0.1<0.2

<0.01<0.10.1

0.40<0.05<0.02

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.02

Matrix:

Matrix:

Matrix:

R467505


R469138R469138R469138R469138R469138R469138R469138R467505R467505

R467505

R467505

R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505


L433144 CONTD....

5PAGE


of

CE03399 PHASE 700

Qualifier* Batch

16

L433144-5

L433144-6

LF-5 TELEPHONE LAKE

LF-6 TELEPHONE LAKE

RF on 13-SEP-06

RF on 13-SEP-06

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE





Mercury (Hg)

Arsenic (As)





mg/kg

mg/kg





21-NOV-06

21-NOV-06





JGP

JGP



<0.02<0.05<0.10.12

<0.05<0.15.3

1403730330350<5

<0.519900.080.80

0.02

<0.05

<0.05<2

<0.1<0.2

<0.01<0.10.1

0.44<0.05<0.020.02

<0.05<0.10.16

<0.05<0.17.1

2004070339510<5

<0.52060

Metals in Tissue

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

Matrix:

Matrix:

R467505R467505R467505R467505R467505R467505R467505

R469138R469138R469138R469138R469138R469138R469138R467505R467505

R467505

R467505


R469138R469138R469138R469138R469138R469138R469138


L433144 CONTD....

6PAGE


of

CE03399 PHASE 700

Qualifier* Batch

16

L433144-6

L433144-7

L433144-8

LF-6 TELEPHONE LAKE

LF-7 TELEPHONE LAKE

LF-8 TELEPHONE LAKE

RF on 13-SEP-06

RF on 13-SEP-06

RF on 13-SEP-06

Sampled By:

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE

FISH TISSUE





Mercury (Hg)

Arsenic (As)



Mercury (Hg)

Arsenic (As)


mg/kgmg/kg

mg/kg

mg/kg



mg/kg

mg/kg


21-NOV-0621-NOV-06

21-NOV-06

21-NOV-06



21-NOV-06

21-NOV-06

21-NOV-0621-NOV-0621-NOV-0621-NOV-0621-NOV-06

JGPJGP

JGP

JGP



JGP

JGP

JGPJGPJGPJGPJGP

0.090.70

0.02

<0.05

<0.05<2

<0.1<0.2

<0.01<0.10.1

0.29<0.05<0.02<0.02<0.05<0.10.18

<0.05<0.14.4

1503870337260<5

<0.520100.080.77

0.02

<0.05

<0.05<2

<0.1<0.2

<0.01

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.01

Matrix:

Matrix:

Matrix:

R467505R467505

R467505

R467505


R469138R469138R469138R469138R469138R469138R469138R467505R467505

R467505

R467505

R467505R467505R467505R467505R467505


L433144 CONTD....

7PAGE


of

CE03399 PHASE 700

Qualifier* Batch

16

L433144-8

L433144-9

LF-8 TELEPHONE LAKE

LF-9 TELEPHONE LAKE

RF on 13-SEP-06

RF on 13-SEP-06

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE





Mercury (Hg)

Arsenic (As)





mg/kg

mg/kg


mg/kgmg/kg

21-NOV-0621-NOV-0621-NOV-0621-NOV-0621-NOV-0621-NOV-0621-NOV-0621-NOV-0621-NOV-0621-NOV-0621-NOV-0621-NOV-06


21-NOV-06

21-NOV-06


24-NOV-0624-NOV-06



JGP

JGP


HASHAS

<0.10.7

0.290.160.76

<0.02<0.05<0.10.19

<0.05<0.14.9

1403780363310<5

<0.519900.080.83

0.02

<0.05

<0.05<20.1

<0.2<0.01<0.1<0.10.36

<0.05<0.02<0.02<0.05<0.10.14

<0.05<0.15.9

1904010

Metals in Tissue

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

2020

Matrix:

Matrix:

R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505

R469138R469138R469138R469138R469138R469138R469138R467505R467505

R467505

R467505


R469138R469138


L433144 CONTD....

8PAGE


of

CE03399 PHASE 700

Qualifier* Batch

16

L433144-9

L433144-10

L433144-11

LF-9 TELEPHONE LAKE

LF-10 TELEPHONE LAKE

PRDC FF+1 SITE 24A

RF on 13-SEP-06

RF on 13-SEP-06

RW on 13-SEP-06

Sampled By:

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE

FISH TISSUE





Mercury (Hg)

Arsenic (As)



Mercury (Hg)

Arsenic (As)


mg/kg

mg/kg



mg/kg

mg/kg


21-NOV-06

23-NOV-06



23-NOV-06

21-NOV-06

HASHASHASHASHASJGPJGP

JGP

JGP



JGP

JGP

348410<5

<0.521900.090.84

0.02

<0.05

<0.05<20.2

<0.2<0.01<0.1<0.10.37

<0.05<0.020.02

<0.05<0.10.34

<0.05<0.16.7

2903920345330<5

<0.521600.070.21

0.07

<0.05

Metals in Tissue

Metals in Tissue

Metals in Tissue

5205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

Matrix:

Matrix:

Matrix:

R469138R469138R469138R469138R469138R467505R467505

R467505

R468447


R469138R469138R469138R469138R469138R469138R469138R468447R468447

R468447

R467505


L433144 CONTD....

9PAGE


of

CE03399 PHASE 700

Qualifier* Batch

16

L433144-11

L433144-12

PRDC FF+1 SITE 24A

PRDC FF-2 SITE 24A

RW on 13-SEP-06

RW on 13-SEP-06

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE





Mercury (Hg)

Arsenic (As)

Silver (Ag)Aluminum (Al)Barium (Ba)Beryllium (Be)Cadmium (Cd)Cobalt (Co)Chromium (Cr)Copper (Cu)Molybdenum (Mo)Nickel (Ni)Lead (Pb)Antimony (Sb)Tin (Sn)Strontium (Sr)Thallium (Tl)



mg/kg

mg/kg

mg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kgmg/kg



21-NOV-06

21-NOV-06

21-NOV-0621-NOV-0621-NOV-0621-NOV-0621-NOV-0621-NOV-0621-NOV-0621-NOV-0621-NOV-0621-NOV-0621-NOV-0621-NOV-0621-NOV-0621-NOV-0621-NOV-06



JGP

JGP

JGPJGPJGPJGPJGPJGPJGPJGPJGPJGPJGPJGPJGPJGPJGP

<0.05<21.7

<0.2<0.01<0.1<0.10.88

<0.050.17

<0.02<0.05<0.17.81

<0.05<0.127.6

88103180389950206.5

61600.383.33

0.04

<0.05

<0.05<21.5

<0.2<0.01<0.1<0.10.76

<0.050.15

<0.02<0.05<0.17.49

<0.05

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.05

Matrix:

Matrix:


R469138R469138R469138R469138R469138R469138R469138R467505R467505

R467505

R467505

R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505


L433144 CONTD....

10PAGE


of

CE03399 PHASE 700

Qualifier* Batch

16

L433144-12

L433144-13

PRDC FF-2 SITE 24A

PRDC FF-3 SITE 24A

RW on 13-SEP-06

RW on 13-SEP-06

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE



Vanadium (V)Zinc (Zn)


Mercury (Hg)

Arsenic (As)



Mercury (Hg)

mg/kgmg/kg


mg/kg

mg/kg



mg/kg

21-NOV-0621-NOV-06


21-NOV-06

21-NOV-06



21-NOV-06

JGPJGP


JGP

JGP



JGP

<0.130.6

85103160393870186.8

58800.261.26

0.04

<0.05

<0.05<21.9

<0.2<0.01<0.1<0.10.96

<0.050.17

<0.02<0.05<0.17.15

<0.05<0.129.2

95203350414960236.2

66600.260.50

0.04

Metals in Tissue

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

Matrix:

Matrix:

R467505R467505

R469138R469138R469138R469138R469138R469138R469138R467505R467505

R467505

R467505


R469138R469138R469138R469138R469138R469138R469138R467505R467505

R467505


L433144 CONTD....

11PAGE


of

CE03399 PHASE 700

Qualifier* Batch

16

L433144-14

L433144-15

PRDC FF-4 SITE 24A

PRDC FF-5 SITE 24A

RW on 13-SEP-06

RW on 13-SEP-06

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE



Arsenic (As)



Mercury (Hg)

Arsenic (As)


mg/kg



mg/kg

mg/kg


21-NOV-06



21-NOV-06

21-NOV-06


JGP



JGP

JGP


<0.05

<0.05<21.2

<0.2<0.01<0.1<0.10.92

<0.050.16

<0.02<0.05<0.16.53

<0.05<0.125.0

77803140367910193.8

56400.28

<0.05

0.03

<0.05

<0.05<21.6

<0.2<0.01<0.1<0.10.94

<0.050.16

<0.02<0.05<0.17.53

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.05

Matrix:

Matrix:

R467505


R469138R469138R469138R469138R469138R469138R469138R467505R467505

R467505

R467505

R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505


L433144 CONTD....

12PAGE


of

CE03399 PHASE 700

Qualifier* Batch

16

L433144-15

L433144-16

PRDC FF-5 SITE 24A

PRDC FF-6 SITE 24A

RW on 13-SEP-06

RW on 13-SEP-06

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE





Mercury (Hg)

Arsenic (As)



Mercury (Hg)

mg/kgmg/kgmg/kg


mg/kg

mg/kg



mg/kg

21-NOV-0621-NOV-0621-NOV-06


21-NOV-06

21-NOV-06



21-NOV-06

JGPJGPJGP


JGP

JGP



JGP

<0.05<0.126.9

87503150388950164.1

59700.25

<0.05

0.03

<0.05

<0.05<21.6

<0.2<0.01<0.1<0.10.77

<0.050.17

<0.02<0.05<0.17.15

<0.05<0.130.4

89503320390970224.5

62700.27

<0.05

0.03

Metals in Tissue

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

Matrix:

Matrix:

R467505R467505R467505

R469138R469138R469138R469138R469138R469138R469138R467505R467505

R467505

R467505


R469138R469138R469138R469138R469138R469138R469138R467505R467505

R467505


L433144 CONTD....

13PAGE


of

CE03399 PHASE 700

Qualifier* Batch

16

L433144-16

L433144-17

L433144-18

PRDC FF-6 SITE 24A

PRDC FF-7 SITE 24A

PRDC FF-8 SITE 24A

RW on 13-SEP-06

RW on 13-SEP-06

RW on 13-SEP-06

Sampled By:

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE

FISH TISSUE



Arsenic (As)



Mercury (Hg)

Arsenic (As)


mg/kg



mg/kg

mg/kg


21-NOV-06



21-NOV-06

21-NOV-06


JGP



JGP

JGP


<0.05

<0.05<21.4

<0.2<0.01<0.1<0.10.82

<0.050.21

<0.02<0.05<0.17.48

<0.05<0.123.7

89903270411880205.4

63700.25

<0.05

0.02

<0.05

<0.05<21.3

<0.2<0.01<0.1<0.11.06

<0.050.23

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.02

Matrix:

Matrix:

Matrix:

R467505


R469138R469138R469138R469138R469138R469138R469138R467505R467505

R467505

R467505

R467505R467505R467505R467505R467505R467505R467505R467505R467505R467505


L433144 CONTD....

14PAGE


of

CE03399 PHASE 700

Qualifier* Batch

16

L433144-18

L433144-19

PRDC FF-8 SITE 24A

PRDC FF-9 SITE 24A

RW on 13-SEP-06

RW on 13-SEP-06

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE





Mercury (Hg)

Arsenic (As)





mg/kg

mg/kg





21-NOV-06

21-NOV-06





JGP

JGP



<0.02<0.05<0.18.05

<0.05<0.121.1

98703220412

1090184.6

66300.290.53

0.03

<0.05

<0.052

1.6<0.2

<0.01<0.1<0.10.81

<0.050.21

<0.02<0.05<0.17.38

<0.05<0.124.7

94103190397

1020225.7

6290

Metals in Tissue

Metals in Tissue

Metals in Tissue

Metals in Tissue

0.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

Matrix:

Matrix:

R467505R467505R467505R467505R467505R467505R467505

R469138R469138R469138R469138R469138R469138R469138R467505R467505

R467505

R467505


R469138R469138R469138R469138R469138R469138R469138


L433144 CONTD....

15PAGE


of

CE03399 PHASE 700

Qualifier* Batch

16

L433144-19

L433144-20

PRDC FF-9 SITE 24A

PRDC FF-10 SITE 24A

RW on 13-SEP-06

RW on 13-SEP-06

Sampled By:

Sampled By:

FISH TISSUE

FISH TISSUE




Mercury (Hg)

Arsenic (As)



Mercury (Hg)

mg/kgmg/kg

mg/kg

mg/kg



mg/kg

21-NOV-0621-NOV-06

21-NOV-06

21-NOV-06



21-NOV-06

JGPJGP

JGP

JGP



JGP

0.32<0.05

0.03

<0.05

<0.057

1.5<0.2

<0.01<0.1<0.10.95

<0.050.19

<0.02<0.05<0.16.10

<0.05<0.133.7

84403340393930235.2

58800.220.64

0.03

Metals in Tissue

Metals in Tissue

0.050.05

0.01

0.05

0.052

0.10.2

0.010.10.1

0.050.050.020.020.050.1

0.050.050.10.5

20205

205

0.520

0.050.05

0.01

Matrix:

Matrix:

R467505R467505

R467505

R467505


R469138R469138R469138R469138R469138R469138R469138R467505R467505

R467505









L433144 CONTD....

16PAGE of

CE03399 PHASE 700



TissueTissue

TissueTissueTissue

TissueTissue

EPA 6020EPA 6020

EPA 6020EPA 200.7EPA 200.7

EPA 6020EPA 6020



EPA 200.3EPA 200.3

EPA 200.3EPA 200.3EPA 200.3

EPA 200.3EPA 200.3









246154 246155

16


Client:

Contact:


RYAN FAULTER/BRETT MCLEOD

Report Date: 04-DEC-06Workorder: L433144


AS-FAUNA-ED

HG-FAUNA-ED

Tissue

Tissue

R467505

R468447

R467505

Batch

Batch

Batch

CRM

CRM

DUP

MB

MB

MS

CRM

CRM

DUP

MB

MS

CRM

CRM

DUP

MB

MB

MS

MS

WG526691-2

WG526699-2

WG526691-3

WG526691-1

WG526699-1

WG526691-4

WG526708-2

WG526708-4

WG526708-5

WG526708-1

WG526708-6

WG526691-2

WG526699-2

WG526691-3

WG526691-1

WG526699-1

WG526691-4

WG526699-3

DORM-2_FISH

DORM-2_FISH

L433144-9

L433144-9

DORM-2_FISH

7602_BUSHES

L433144-10

L433144-10

DORM-2_FISH

DORM-2_FISH

L433144-9

L433144-9

L433144-20

Arsenic (As)

Arsenic (As)

Arsenic (As)

Arsenic (As)

Arsenic (As)

Arsenic (As)

Arsenic (As)

Arsenic (As)

Arsenic (As)

Arsenic (As)

Arsenic (As)

Mercury (Hg)

Mercury (Hg)

Mercury (Hg)

Mercury (Hg)

Mercury (Hg)

Mercury (Hg)

120

125

<0.05

<0.05

<0.05

98

106

87

<0.05

<0.05

98

78

74

0.02

<0.01

<0.01

88

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

N/A

N/A

0.00

19

19

0.04

89-144

89-144

70-127

89-144

60-109

70-127

44-138

44-138

67-122

%

%

mg/kg

mg/kg

mg/kg

%

%

%

mg/kg

mg/kg

%

%

%

mg/kg

mg/kg

mg/kg

%

0.25

0.25

0.25

0.05

0.05

RPD-NA

RPD-NA

J

<0.05

<0.05

0.02

13

ALS Laboratory Group Quality Control ReportPage 2 ofReport Date: 04-DEC-06Workorder: L433144


HG-FAUNA-ED

MET1-FAUNA-ED

Tissue

Tissue

R467505

R468447

R467505

Batch

Batch

Batch

MS

CRM

DUP

MB

MS

CRM

CRM

DUP

WG526699-3

WG526708-2

WG526708-5

WG526708-1

WG526708-6

WG526691-2

WG526699-2

WG526691-3

L433144-20

DORM-2_FISH

L433144-10

L433144-10

DORM-2_FISH

DORM-2_FISH

L433144-9

Mercury (Hg)

Mercury (Hg)

Mercury (Hg)

Mercury (Hg)

Mercury (Hg)

Aluminum (Al)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Nickel (Ni)

Zinc (Zn)

Aluminum (Al)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Nickel (Ni)

Zinc (Zn)

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

103

68

0.06

0.03

99

114

86

105

92

97

89

89

95

96

91

109

86

92

92

84

<2

<0.05

0.1

<0.2

21-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

0.01

N/A

N/A

0.0

N/A

0.04

23

35

0.4

26

67-122

44-138

67-122

48-144

74-125

88-137

79-110

51-120

75-108

57-117

48-144

72-116

74-125

88-137

79-110

51-120

75-108

57-117

%

%

mg/kg

mg/kg

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

mg/kg

mg/kg

mg/kg

0.05

J

RPD-NA

RPD-NA

J

RPD-NA

0.07

<2

<0.05

0.1

<0.2

13




R467505BatchDUP

MB

MB

WG526691-3

WG526691-1

WG526699-1

L433144-9Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

<0.2

<0.01

<0.1

<0.1

0.33

<0.02

<0.05

<0.02

<0.05

0.17

<0.05

<0.1

<0.1

5.4

<2

<0.05

<0.1

<0.2

<0.01

<0.1

<0.1

0.19

<0.02

<0.05

<0.02

<0.05

<0.05

<0.05

<0.1

<0.1

0.7

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

N/A

N/A

N/A

N/A

0.02

N/A

N/A

N/A

N/A

0.02

N/A

N/A

N/A

8.2

26

21

16

23

0.2

26

50

23

33

0.2

26

38

25

25

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

10

0.25

0.5

1

0.05

0.5

0.5

0.25

0.1

0.25

0.1

0.25

0.25

0.25

0.5

0.5

2.5

RPD-NA

RPD-NA

RPD-NA

RPD-NA

J

RPD-NA

RPD-NA

RPD-NA

RPD-NA

J

RPD-NA

RPD-NA

RPD-NA

<0.2

<0.01

<0.1

<0.1

0.36

<0.02

<0.05

<0.02

<0.05

0.14

<0.05

<0.1

<0.1

5.9

13




R467505BatchMB

MS

WG526699-1

WG526691-4 L433144-9

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

<2

<0.05

<0.1

<0.2

<0.01

<0.1

<0.1

0.07

<0.02

<0.05

<0.02

<0.05

0.13

<0.05

<0.1

<0.1

1.8

94

98

94

90

92

102

101

98

106

104

99

74

111

98

101

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

73-121

80-114

77-120

59-119

66-115

68-145

83-123

79-119

77-118

82-122

81-119

56-122

81-129

78-119

87-118

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

10

0.25

0.5

1

0.05

0.5

0.5

0.25

0.1

0.25

0.1

0.25

0.25

0.25

0.5

0.5

2.5

13




R467505

R468447

Batch

Batch

MS

MS

CRM

CRM

WG526691-4

WG526699-3

WG526708-2

WG526708-3

L433144-9

L433144-20

DORM-2_FISH

1577B_LIVER

Vanadium (V)

Zinc (Zn)

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

Aluminum (Al)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Nickel (Ni)

Zinc (Zn)

Cadmium (Cd)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

102

87

132

103

102

103

89

100

113

116

113

101

112

149

107

102

98

363

80

96

108

91

90

92

91

95

92

89

113

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

76-122

26-142

73-121

80-114

77-120

59-119

66-115

68-145

83-123

79-119

77-118

82-122

81-119

81-129

78-119

87-118

76-122

26-142

48-144

74-125

88-137

79-110

51-120

75-108

57-117

59-114

63-138

71-99

81-134

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

E

E

E

E

13




R468447BatchCRM

CRM

DUP

WG526708-3

WG526708-4

WG526708-5

1577B_LIVER

7602_BUSHES

L433144-10

Strontium (Sr)

Zinc (Zn)

Aluminum (Al)

Barium (Ba)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Strontium (Sr)

Vanadium (V)

Zinc (Zn)

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

134

82

69

102

138

67

120

81

98

118

99

97

82

94

<2

<0.05

0.1

<0.2

<0.01

<0.1

<0.1

0.36

0.02

<0.05

<0.02

<0.05

0.16

<0.05

<0.1

<0.1

6.7

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

N/A

N/A

0.1

N/A

N/A

N/A

N/A

0.02

0.00

N/A

N/A

N/A

0.19

N/A

N/A

N/A

0.77

23

35

0.4

26

21

16

23

0.2

0.08

50

23

33

0.2

26

38

25

25

79-188

48-111

55-93

81-118

89-164

59-127

99-153

68-110

69-130

79-151

54-124

74-125

75-118

51-143

%

%

%

%

%

%

%

%

%

%

%

%

%

%

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

RPD-NA

RPD-NA

J

RPD-NA

RPD-NA

RPD-NA

RPD-NA

J

J

RPD-NA

RPD-NA

RPD-NA

J

RPD-NA

RPD-NA

RPD-NA

<2

<0.05

0.2

<0.2

<0.01

<0.1

<0.1

0.37

0.02

<0.05

<0.02

<0.05

0.34

<0.05

<0.1

<0.1

6.7

13




R468447BatchMB

MS

WG526708-1

WG526708-6 L433144-10

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

Vanadium (V)

Zinc (Zn)

Aluminum (Al)

Antimony (Sb)

Barium (Ba)

Beryllium (Be)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Lead (Pb)

Molybdenum (Mo)

Nickel (Ni)

Silver (Ag)

Strontium (Sr)

Thallium (Tl)

Tin (Sn)

<2

<0.05

<0.1

<0.2

<0.01

<0.1

<0.1

0.08

<0.02

<0.05

<0.02

<0.05

0.17

<0.05

<0.1

<0.1

1.5

84

98

92

108

94

101

106

97

106

101

99

110

109

109

102

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

73-121

80-114

77-120

59-119

66-115

68-145

83-123

79-119

77-118

82-122

81-119

56-122

81-129

78-119

87-118

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

10

0.25

0.5

1

0.05

0.5

0.5

0.25

0.1

0.25

0.1

0.25

0.25

0.25

0.5

0.5

2.5

13



MET1-FAUNA-ED

MET2-FAUNA-ED

Tissue

Tissue

R468447

R469138

Batch

Batch

MS

CRM

CRM

CRM

CRM

CRM

DUP

DUP

WG526708-6

WG526691-2

WG526699-2

WG526708-2

WG526708-3

WG526708-4

WG526691-3

WG526708-5

L433144-10

DORM-2_FISH

DORM-2_FISH

DORM-2_FISH

1577B_LIVER

7602_BUSHES

L433144-9

L433144-10

Vanadium (V)

Zinc (Zn)

Iron (Fe)

Manganese (Mn)

Iron (Fe)

Manganese (Mn)

Iron (Fe)

Manganese (Mn)

Calcium (Ca)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

101

93

109

106

115

109

118

111

123

112

112

108

100

104

102

106

109

105

104

170

<5

352

<0.5

4060

400

23-NOV-06

23-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

20

N/A

0.96

N/A

1.3

1.6

80

15

14

15

15

22

76-122

26-142

90-124

83-118

90-124

83-118

90-124

83-118

55-161

74-115

74-114

72-120

67-116

85-113

80-107

82-112

86-117

69-118

79-112

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

J

RPD-NA

RPD-NA

190

<5

348

<0.5

4010

410

13




R469138BatchDUP

MB

MB

MB

MS

WG526708-5

WG526691-1

WG526699-1

WG526708-1

WG526691-4

L433144-10

L433144-9

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

260

<5

353

<0.5

4130

340

20

<5

<5

<0.5

<20

<20

20

<5

<5

<0.5

<20

<20

40

<5

13

<0.5

40

<20

106

106

107

104

112

109

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

14

N/A

2.1

N/A

5.2

2.6

19

15

14

15

15

22

71-125

63-129

78-113

80-115

56-154

82-122

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

%

%

%

%

%

100

25

25

2.5

100

100

100

25

25

2.5

100

100

100

25

25

2.5

100

100

RPD-NA

RPD-NA

290

<5

345

<0.5

3920

330

13



MET2-FAUNA-ED

P-FAUNA-ED

Tissue

Tissue

R469138

R469138

Batch

Batch

MS

MS

MS

CRM

CRM

DUP

DUP

MB

MB

MB

MS

MS

WG526691-4

WG526699-3

WG526708-6

WG526708-3

WG526708-4

WG526691-3

WG526708-5

WG526691-1

WG526699-1

WG526708-1

WG526691-4

WG526699-3

L433144-9

L433144-20

L433144-10

1577B_LIVER

7602_BUSHES

L433144-9

L433144-10

L433144-9

L433144-20

Sodium (Na)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Calcium (Ca)

Iron (Fe)

Magnesium (Mg)

Manganese (Mn)

Potassium (K)

Sodium (Na)

Phosphorus (P)

Phosphorus (P)

Phosphorus (P)

Phosphorus (P)

Phosphorus (P)

Phosphorus (P)

Phosphorus (P)

Phosphorus (P)

Phosphorus (P)

109

98

106

106

103

105

104

104

105

106

104

112

106

104

100

2100

2140

30

50

20

108

105

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

23-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

24-NOV-06

4.1

1.4

17

17

82-122

71-125

63-129

78-113

80-115

56-154

82-122

71-125

63-129

78-113

80-115

56-154

82-122

70-134

78-118

64-133

64-133

%

%

%

%

%

%

%

%

%

%

%

%

%

%

%

mg/kg

mg/kg

mg/kg

mg/kg

mg/kg

%

%

100

100

100

2190

2160

13



P-FAUNA-ED

SE-FAUNA-ED

TI-FAUNA-ED

Tissue

Tissue

Tissue

R469138

R467505

R468447

R467505

Batch

Batch

Batch

Batch

MS

CRM

DUP

MB

MB

MS

CRM

CRM

DUP

MB

MS

DUP

MB

MB

MS

WG526708-6

WG526691-2

WG526691-3

WG526691-1

WG526699-1

WG526691-4

WG526708-2

WG526708-3

WG526708-5

WG526708-1

WG526708-6

WG526691-3

WG526691-1

WG526699-1

WG526691-4

L433144-10

DORM-2_FISH

L433144-9

L433144-9

DORM-2_FISH

1577B_LIVER

L433144-10

L433144-10

L433144-9

L433144-9

Phosphorus (P)

Selenium (Se)

Selenium (Se)

Selenium (Se)

Selenium (Se)

Selenium (Se)

Selenium (Se)

Selenium (Se)

Selenium (Se)

Selenium (Se)

Selenium (Se)

Titanium (Ti)

Titanium (Ti)

Titanium (Ti)

Titanium (Ti)

105

156

0.09

<0.05

<0.05

100

121

128

0.06

<0.05

104

0.73

0.07

0.17

99

24-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

21-NOV-06

0.01

0.01

15

0.2

0.2

55

64-133

101-168

44-153

101-168

97-156

44-153

18-177

%

%

mg/kg

mg/kg

mg/kg

%

%

%

mg/kg

mg/kg

%

mg/kg

mg/kg

mg/kg

%

0.25

0.25

0.25

0.25

0.25

J

J

0.09

0.07

0.84

13



TI-FAUNA-ED Tissue

R468447BatchCRM

DUP

MB

MS

WG526708-4

WG526708-5

WG526708-1

WG526708-6

7602_BUSHES

L433144-10

L433144-10

Titanium (Ti)

Titanium (Ti)

Titanium (Ti)

Titanium (Ti)

46

0.15

0.24

96

23-NOV-06

23-NOV-06

23-NOV-06

23-NOV-06

0.06 0.2

21-120

18-177

%

mg/kg

mg/kg

%

0.25

J0.21

13

Legend:

Qualifier:



ALS Laboratory Group Quality Control ReportPage 13 ofReport Date: 04-DEC-06Workorder: L433144 13

ALS Laboratory Group – Environmental Division (Canada)

Method ID: Tissue Digestion Using Microwave Version # ISOP 77.06

Effective Date: 29-Novmeber-2005

Page: 1 of 2 ___________________________________________________________________________________

Edmonton Standard Operating

Procedure

STANDARD OPERATING PROCEDURE SUMMARY

Sample Digestion Of Biological Samples For Total Metals By ICP or ICP/MS

(Microwave with H2O, HNO3, & HF)

1 Introduction This method employs pre-treatment with deionized water, nitric acid, and hydrofluoric acid, then microwave digestion to extract metals from biological tissues. Biological tissues include both plant and animal tissue. After extraction samples can be analyzed by ICP or ICP-MS methods.

2 Scope This method is applicable to the digestion of plant material (grass, lichen, tea, etc.) as well as animal tissue (fish muscle, moose meat, whole body carcass, etc.) The test code contains either “fauna” for animal tissues, or “flora” for plant tissues. Refer to the analytical methods to obtain a list of relevant metals.

3 Principle 3.1 Prior to digestion procedure, samples have been made homogeneous through a

variety of methods. These methods include dissection and grinding in a blender, food processor, or coffee grinder (depending on size and consistency of the sample). Samples may be freeze-dried and composites may have to be completed. Moisture content is determined on a separate portion.

3.2 A representative 0.4 to 0.5 g sample is weighed into a teflon digestion vessel. The tissues are digested using the microwave apparatus with deionized water, nitric acid, and hydrofluoric acid while capped. 3.3 Analysis of the digested material for metals content can be achieved by ICP/MS

(ISOP96), or ICP-AES (ISOP100).

4 Sample Requirements Please refer to next page.


Method ID: Tissue Digestion Using Microwave Version # ISOP 77.06

Effective Date: 29-Novmeber-2005

Page: 2 of 2 ___________________________________________________________________________________


Procedure

Parameter(s) and Matrix: Frozen Tissue Samples

Container Plastic bags or glass jars (Wrapping animal tissue in aluminium foil is extremely detrimental to the analysis). Inform CSS and your supervisor if this occurs.

Preservative None Min. Sample Amount Sample Pre-treatment None Lab Storage Conditions Keep frozen

Maximum Holding Time (Standard Methods)

Can be held several months if the sample is sealed appropriately and kept well frozen). Plant tissue is stored at room temperature for up to 6 months or more.

5 Data Acquisition, Calculation and Data Reduction Data acquisition is performed following the analytical methods for ICP (ISOP100), or

ICP- MS (ISOP96). Relevant calculation and data reduction instructions will be found in those SOPs.

6 Internal Quality Control Requirements 6.1 For each batch of samples processed, a blank should be carried through the

entire sample preparation and digestion procedure. This will aid in determining amount of background contamination, if any.

6.2 One duplicate per matrix and at least one per batch is run to determine precision. 6.3 A certified reference material is run with each batch, using the matrix that most

closely matches the samples. 6.4 Matrix spikes are performed by the instrument analyst, after digestion. Ensure

that a matrix spike is created in the Seedpak workgroup with the above QC.

7 Method Reference(s) 7.1 Loosely based on; McDaniel, W. "Method 200.3 Sample Preparation Procedure

for Spectrochemical Determination of Total Recoverable Elements in Biological Tissues, Revision 1.0, April 1991". Methods for the Determination of Metals in Environmental Samples, USEPA Report Number EPA/600/4-91/010.


Method ID: Metals By ICPMS Version # ISOP 96.08

Effective Date: 24-May-2006

Page: 1 of 6

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Procedure


Metals In Liquid & Solid Samples By Inductively Coupled Plasma – Mass Spectrometry (IC/MS) ELAN 6000

1 Introduction Since the first commercial instrument was introduced in 1983, Inductively Coupled Plasma Mass Spectrometry (ICP/MS) has grown to become the technique of choice for rapid ultra-trace (sub ppb levels for most elements) multi-element analysis. It is routinely used in environmental, clinical, semiconductor, metallurgical, nuclear and geochemical laboratories. The ICP/MS is a combination of two well established technologies: the ICP, which is the ion source operated at 6000-10,000 K; and a quadrupole mass spectrometer which has very high detection power. The ICP/MS not only provides extremely high sensitivity, but also wide linear dynamic range, and simultaneous multi-element capability. In addition, valuable isotopic information can also be obtained by this technique, which is not available by Inductively Coupled Plasma Atomic Emission Spectrometry (ICP-AES). It should be emphasized here that the Inductively Coupled Plasma Mass Spectrometer (ICP/MS) is a very complicated and sophisticated piece of scientific instrumentation. Only personnel with extensive training in metal analysis (ie. ICP-AES and AA), and only personnel after extensive theoretical and hands-on training on this instrument are eligible to perform daily analysis and data interpretation on the ICP/MS.

2 Scope

The method described in this SOP is suitable for all surface, ground, potable, effluent and waste waters. It is also suitable for any other liquid or solid samples including biological and geological samples after appropriate sample pre-treatment and/or sample digestion procedures. Solid samples and biological samples are digested using EPA 3051 or EPA 3050 (ISOP 50) or a modified EPA 200.3 (ISOPs 77 and 44); depending on the matrices and client requirements in order to transform these samples into liquid form before they can be analyzed by ICP/MS. Colourless, transparent samples having a turbidity of < 1NTU, no colour, no odor, and a single phase that require total metals analysis may be analyzed by ICP/MS directly without digestion. Total metals in waters that have a turbidity >1 NTU are digested using EPA 3015 (ISOP 7) before ICP/MS analysis. Toxicity Characteristic Leaching Procedure (TCLP) leachate samples are extracted using ISOP 74 and hygiene filters are digested using ISOP 32.




Page: 2 of 6

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Procedure

Elements suitable for this analysis are listed in the table below:

Table 1: Scope of Elements, MDLs and Standard Concentrations Element Isotope Best MDL'S* Std. Conc. QC Conc. Spike Conc. (µg/L) (µg/L) (µg/L) (µg/L) Lithium 7 0.09 5, 20, 50 20, 100 20 Beryllium 9 0.07 5, 20, 50 20, 100 20 Boron 10,11 0.16 25, 100, 250 100, 500 100 Silicon 28 0.6 25, 100, 250 100, 500 100 Aluminum 27 0.22 25, 100, 250 100, 500 100 Phosphorus 31 1.0 25, 100, 250 100, 500 100 Titanium 47,49 0.05, 0.1 5, 20, 50 20, 100 20 Vanadium 51 0.01 5, 20, 50 20, 100 20 Chromium 52, 53 0.05 5, 20, 50 20, 100 20 Manganese 55 0.01 5, 20, 50 20, 100 20 Cobalt 59 0.01 5, 20, 50 20, 100 20 Nickel 60, 62 0.02, 0.2 5, 20, 50 20, 100 20 Copper 63, 65 0.08 5, 20, 50 20, 100 20 Zinc 66,67 0.14 5, 20, 50 20, 100 20 Arsenic 75 0.01 5, 20, 50 20, 100 20 Selenium 77, 82 0.1, 0.3 5, 20, 50 20, 100 20 Rubidium 85 0.04 5, 20, 50 20, 100 20 Strontium 86,88 0.02,0.01 5, 20, 50 20, 100 20 Zirconium 90,91 0.19 5, 20, 50 20, 100 20 Molybdenum 95,97 0.01, 0.03 5, 20, 50 20, 100 20




Page: 3 of 6

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Procedure

Table 1: Scope of Elements, MDLs and Standard Concentrations (continued) Element Isotope Best MDL'S* Std. Conc. QC Conc. Spike Conc. (µg/L) (µg/L) (µg/L) (µg/L) Silver 107,109 0.09 5, 20, 50 20. 100 20 Cadmium 111, 114 0.01 5, 20, 50 20, 100 20 Tin 118,120 0.02 5, 20, 50 20, 100 20 Antimony 121 0.006 5, 20, 50 20, 100 20 Tellurium 125 0.2 5, 20, 50 20 ,100 20 Cesium 132 0.01 5, 20, 50 20, 100 20 Barium 137 0.007 5, 20, 50 20, 100 20 Tungsten 184 0.02 5, 20, 50 20, 100 20 Mercury 201, 202 0.02, 0.009 0.5 , 2, 4 2, 4 2 Thallium 205 0.006 5, 20, 50 20, 100 20 Lead 208 0.01 5, 20, 50 20, 100 20 Bismuth 209 0.03 5, 20, 50 20,100 20 Uranium 238 0.008 5, 20, 50 20, 100 20 Sodium 23 0.7 250, 1000, 2500 1000, 5000 1000 Magnesium 24,25 0.2, 0.5 250, 1000, 2500 1000, 5000 1000 Potassium 39 3 250, 1000, 2500 1000, 5000 1000 Calcium 43,44 1.6, 2.5 250, 1000, 2500 1000, 5000 1000 Iron 54, 57 1.4, 4 250, 1000, 2500 1000, 5000 1000

*Actual method detection limits vary with sample matrices; DL's for diluted sample = listed DL's × dilution factor; DL's for solid sample = listed DL's × extraction ratio. 3 Principle

An ICP source consists of a flowing stream of argon gas ionized by a spark and maintained by an applied radio frequency field. Samples are introduced through a peristaltic pump to a nebulizer and the resulting aerosol is transported to the ICP source by a stream of argon gas, where the sample elements are dessolvated, vaporized, and ionized. Elements are ionized to varying degrees according to their first ionization potentials.




Page: 4 of 6

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Procedure

Ions are then extracted from the centre of the plasma at the sampling interface consisting of a 1.1 mm orifice in a water-cooled sampler cone. The ions are transmitted through this reduced pressure stage (~4 torr) behind the sampling interface, through a second cone, the skimmer cone with an orifice of 0.9 mm, into the ion lens region. This area operates at a pressure less than 8x10-4 torr maintained by a turbo molecular vacuum pump. The ion lens guides the ion beam to pass into the quadrupole mass filter where the ions are separated according to their mass to charge ratio (m/e). All the selected ions are then allowed to pass into a dual-stage discrete dynode detector placed at the exit to the quadrupole mass filter sequentially. The scanning or sequential filtering of the ions with different mass to charge ratio (m/e) is accomplished by varying the radio frequency voltage applied to the quadrupole mass filter. The pulses of ions are amplified and accumulated in multi-channel analyzers (MCA's) and then subsequently processed by a computer where both the qualitative and quantitative information about the samples are extracted and displayed.

4 Sample Requirements

Matrix Container Storage Temperature

Treatment and Preservative ** Hold Time

Dissolved water

250 mL Polyethylene bottle

Room Temperature *

Field filter 0.45μm, then 5 mL 20% Nitric acid added in the field

6 months. Hg 14 days

Extractable water


Room Temperature *

5 mL 20% Nitric acid added in the field, allow to sit for 1 hour or more, filter 0.45μm in the field

6 months once filtered. Hg 14 days

Total water 250 mL Polyethylene bottle

Room Temperature *

5 mL 20% Nitric acid added in the field. Do not filter.


Dissolved Ultra trace water

Proofed 250 mL Polyethylene bottle

Room Temperature *

Field filter 0.45μm, then 1 mL 1:1 Seastar nitric acid added in the field


Total Ultra trace water

Proofed 250 mL Polyethylene bottle

Room Temperature *

1 mL 1:1 Seastar nitric acid added in the field. Do not filter


Soils and other solid matrices

Refer to the appropriate digestion SOP as listed in section for details on sample collection and preservation.




Page: 5 of 6

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Procedure

* Samples that are properly preserved can be stored at room temperature for a maximum of 6 months. If samples are not preserved, they must be stored at 4±3°C and transported to the lab as soon as possible. Hold time is 7 days for unpreserved samples. ** Clients and/or the lab are informed when samples are received improperly preserved and/or filtered by notes in the LIMS system, by filter codes being added to the LIMS system, by notes on the client report cover page, and by notes placed in the raw calculated data file.

5 Data Acquisition, Calculation and Data Reduction Concentrations in solution are determined by the Elan 6000 based on internal standard correction, linear calibration. After the analysis is completed, transfer the ICPMS output report file onto the ETL Edmonton network’s I (Inorganic) drive. Ensure that QCs are labeled properly, and that correct dilutions have been entered. Calculate the data using ICPMS MACRO “ms200_.xls”. Save the DATASET spreadsheet, SAMPLE LIST spreadsheet, and the SRMSPK recovery spreadsheet on the network’s I drive. Once the data bundle has been approved by data review, generate a CSV file and transfer the results to Seedpak. After approval, results are reported to the client using 3 significant figures as appropriate.

6 Internal Quality Control Requirements Please refer to next page for table.

7 Method Reference(s) 7.1 EPA 200.8. 7.2 EPA 6020. 7.3 Perkin Elmer ELAN 6000 Software Guide. 7.4 Perkin Elmer ELAN 6000 Hardware Guide. 7.5 Perkin Elmer ELAN 6000 Safety Manual.




Page: 6 of 6

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Procedure

Table 2: Quality Control Requirements QUALITY CONTROL CHECK FREQUENCY ACCEPTANCE

CRITERIA CORRECTIVE ACTION

Initial Calibration (three points) (Standards #1,2,3)

Daily r2 > 0.995

Remake the calibration standards and recalibrate

Quality Control Samples (QC’s)

Daily, after calibration + 10% error or as per QC chart1

1) Remake the QC’s 2) Re-calibrate 3) QC correct data

Continuing Calibration Verification (CCV)

Every 10 Samples + 10% of true value 1) CCV correct data 2) Calibration verification 3) Re-calibration 4) Re-analyze preceding samples

Reagent Blank (RB) Every 10 samples < 5x MDL2 Rinse the system for a few more minutes and rerun the reagent blank

Method Blank (MB) One per batch < 5x MDL2 1) MBL correct the samples in the batch 2) Re-digest and re-analyze all samples in the batch

Matrix Spike (MS) 5%, or minimum of one per batch

75-125% recovery or as per QC chart1

1) Respike and rerun 2) Dilute, respike, and rerun 3) Flag data

Sample Duplicate (DUP) 5%, or minimum of one per batch

RPD3 < 20% or as per QC chart1

1) Repeat analysis 2) Re-digest or reprepare 3) Flag data

Linearity check 1) Semi-annually 2) If necessary, daily for preselected clients

If a sample is over linear range, re-run at a dilution

1 Refer to GSOP 71 for guidance on QC Data Evaluation Using Control Charting Techniques 2 MDL – Method Detection Limit 3 RPD – Relative Percent Difference r = correlation coefficient


Method ID: Metals By ICP/AES Summary Version # ISOP 100.07


Page: 1 of 4

___________________________________________________________________________________


Procedure


Determination Of Trace Elements By ICP/AES

1 Introduction Various metals are found in our environment. Rapid and accurate measurement of

these metals at various levels has become more and more important. Inductively Coupled Plasma Atomic (or Optical) Emission Spectroscopy (ICPAES or ICPOES) has been widely used to determine major, minor, and trace elements in various matrices because of its high sensitivity, wide linear dynamic range, simultaneous multi-element capability, and its relative freedom from interferences.

2 Scope The method described in this SOP is suitable for determining trace elements in both

acidic digests and undigested samples. Typical samples can be soil, waste, water, biological materials, products, leachates, food and NHP products. Detection limits are determined by matrix and available in Seedpak. Instrument detection limits and linear ranges are listed in Table 5. Solid samples and biological samples prepared using ISOP 43 and ISOP 116. They are digested using EPA 3051 (ISOP 77) or a modified EPA 200.3 (ISOPs 77 and 44); depending on the matrices and client requirements in order to transform these samples into liquid form before they can be analyzed by ICP/MS. Colourless, transparent samples having a turbidity of < 1NTU, no colour, no odor, and a single phase that require total metals analysis may be analyzed by ICPAES directly without digestion. Total metals in waters that have a turbidity >1 NTU are digested using EPA 3015 (ISOP 7) before ICPAES analysis. Toxicity Characteristic Leaching Procedure (TCLP) leachate samples are extracted using ISOP 74 and hygiene filters are digested using ISOP 32. Food and NHP products are prepared using ISOP 123 and ISOP 125.

3 Principle

An ICP source consists of a flowing stream of argon gas ionized by an applied radio frequency field. Samples are nebulised and the resulting aerosol is transported to the ICP, subjecting the constituent atoms to temperatures of about 6000 to 8000 K. The element specific emission generated by the ICP is measured using a polychromator or monochromator with a photomultiplier tube or a solid state detector to determine elemental concentrations of analytes simultaneously or sequentially. Yttrium will be added as an internal standard to correct for nebulisation efficiency differences between




Page: 2 of 4

___________________________________________________________________________________


Procedure

the standards and the samples and/or instrumental drifts. The method described here is only for Perkin-Elmer Optima 4300DV instrument, which is used in this lab.

4 Sample Requirements

Matrix Container Storage Temperature

Treatment and Preservative ** Hold Time

Dissolved water ^


Room Temperature *

Field filter 0.45μm, then 5 mL 20% Nitric acid added in the field

6 months.

Extractable water Ŧ


Room Temperature *

5 mL 20% Nitric acid added in the field, allow to sit for 1 hour or more, filter 0.45μm in the field

6 months once filtered.

Total water ╥ 250 mL Polyethylene bottle

Room Temperature *

5 mL 20% Nitric acid added in the field. Do not filter.

6 months

Soils and other matrices ╥

Refer to the appropriate digestion SOP as listed in section for details on sample collection and preservation.

* Samples that are properly preserved can be stored at room temperature for a maximum of 6 months. If samples are not preserved, they must be stored at 4±3°C and transported to the lab as soon as possible. Hold time is 7 days for unpreserved samples. ** Clients and/or the lab are informed when samples are received improperly preserved and/or filtered by notes in the LIMS system, by filter codes being added to the LIMS system, by notes on the client report cover page, and by notes placed in the raw calculated data file. ^ When possible a portion of improperly received dissolved metals sample is prepared: filter a suitable aliquot of sample upon receipt using a 5 mL syringe and 0.45 um nylon membrane filter or a suitable filtration apparatus with a 0.45 um nylon filter. Immediately following filtration, add enough trace metals grade HNO3 to make a final matrix of about 0.2% HNO3. Check using a pH strip that the pH is <2. If not, add sufficient acid to lower the pH. Ŧ If the sample arrives unpreserved, shake well and transfer 40mL to a clean polyethylene container and add 0.2 mL of conc. HNO3 to make a 0.5% HNO3 matrix. Using a pH strip to ensure the pH is <2. If not, add sufficient acid to lower the pH. Mix the sample well and wait for 1 hour. Filter sample prior to analysis. ╥ Total metals in solids, liquids, biological tissues, products, filters, leachates, NHP products, food samples: As required, the samples must be homogenised and digested with strong acid. The detail methods are listed in ISOP 7, 32, 50, 74, 77, 123 and 125.




Page: 3 of 4

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Procedure

5 Data Acquisition, Calculation and Data Reduction 5.1 The instrument will calculate results in the desired units for the samples, provided

that the necessary information has been entered in the sample table, including dilutions.

5.2 To calculate the final concentrations of the samples use in-house macro program ICP2004a (or latest version), to process data. This software performs the necessary checks on the raw data. For example, it will check for sample carryover, linear range of concentration, percent recovery of reference material and spike recovery, and relative percent difference (% rpd) on duplicates. Hard copies of the data are maintained on file. The electronic copies will be saved on the I: drive.

5.3 Before reporting the data to Seedpak, analysts are responsible to thoroughly check the data and make appropriate comments when necessary. Guidelines for these checks are listed on the back of the continuity sheets. A manager or supervisor must approve the metal data before data entry and sign on the continuity cover pages.

5.4 The elements, wavelengths, instrumental detection limits and linear ranges are listed in Table 5.

6 Internal Quality Control Requirements Please see table on the next page.

7 Method References

7.1 EPA SW-846 6010 B Inductively Coupled Plasma - Atomic Emission Spectrometry.

7.2 Perkin Elmer – WinLab32 Instrument Control Software, WinLab32 Data Management Software.

7.3 Perkin Elmer - Optima 4000 Hardware Guide.

7.4 A.P.H.A. 20th Edition - 3120 Metals by Plasma Emission Spectroscopy

7.5 EPA 3050 B, 3051, 3052.

7.6 NIOSH Manual of Analytical Methods.




Page: 4 of 4

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Procedure

Table 1: Quality Control Requirements

QUALITY CONTROL CHECK FREQUENCY

ACCEPTANCE CRITERIA CORRECTIVE ACTION

Initial Calibration (each element) (Standards #1,2,3)

Daily r2 > 0.995 1) Re-calibrate

Analytical Quality Control Samples (QCS LOW, QCS HI)

Daily, after every new calibration

+ 10% error or as per QC chart

1) Re-calibrate

Continuing Calibration Verification (CCV STD)

Every 10 Samples + 10% of true value 1) CCV correction when processing data 2) Re-calibration 3) Re-analyse preceding samples

Internal Standard (IS) All samples and standards

80 - 120% of theoretical value of IS in cal. blank 50 - 80% < 50%

1) Data acceptable 2) Data acceptable; must raise MDL by 2 times 3) Dilute and reanalyse; raise MDLs accordingly 4) Flag data with explanations

Reagent Blank (RB) 10% < MDL1 1) Recalibration 2) Calibration verification 3) Reanalyse preceding samples

Method Blank (MB) One per batch < 5 times MDL1 1) Flag data. 2) MBLK correction during data processing 3) Re-digest if necessary

Analytical Matrix Spike (SPK1) Digestive spike (SPK2)

5%, or minimum of one per batch one per digest batch

As per QC chart for all spikes

1) Reanalyse 2) Dilute as necessary; Reanalyse 3) Flag data 4) Re-digestion may be necessary

Sample Duplicate (DUP) 5%, or minimum of one per digest batch.

As per QC chart for all spike

1) Flag data 2) Re-digestion may be required

Digested Reference Material (soil, biologicals, filters, food, NHP products, etc.)

One per batch As per historical recovery or certified values

1) Re-analyse 2) Flagged data 3) Re-digestion

Linearity check Every year + 10% of previous determination

Discuss with Senior Scientist or Supervisor

1 RPD - Relative Percent Difference 2 MDL - Method Detection Limit 3 RSD - Relative Standard Deviation

4 QC Chart is used when enough data points (i.e. 20-25) are accumulated. Refer to GSOP71 for Guidance on QC Data Evaluation Using Control Charting Techniques 5 Response Factor.

Appendix H3

Benthic Invertebrate Information


Appendix H3 – Table of Contents

APPENDIX H3: BENTHIC INVERTEBRATE INFORMATION TABLE OF CONTENTS

PAGE

1.0 BENTHIC INVERTEBRATE SAMPLING METHODS ...................................................... 1 1.1 Field Sampling ....................................................................................................... 1

1.1.1 Field Measurements and Observations ................................................ 1 1.2 Laboratory Sample Sorting .................................................................................... 2

1.2.1 Splitting Technique ............................................................................... 2 1.2.2 Sorting Technique ................................................................................. 3 1.2.3 Aquatic Invertebrate Identification ......................................................... 3

2.0 TERMS AND INDICES USED FOR BENTHIC INVERTEBRATE DATA INTERPRETATION ........................................................................................................... 4 2.1 The Community Concept and Measurements ....................................................... 4 2.2 Number of Taxa ..................................................................................................... 4 2.3 Shannon-Weaver Diversity Index .......................................................................... 5 2.4 Equitability Index ................................................................................................... 5 2.5 References ............................................................................................................ 6



1.0 BENTHIC INVERTEBRATE SAMPLING METHODS

1.1 Field Sampling

A 15x15x15 cm Ekman dredge fastened to a pole was used for sampling sediments in the depositional habitat. The sampler enclosed 225 cm2 of the river bottom, and collected 4 000 cm3 of substrate. The sampler was slowly lowered to the bottom, avoiding rapid water movements which would disturb the surface of the substrate and alert the more mobile animals to escape. The closure of the dredge’s jaws was checked after slowly pulling the dredge near the water’s surface. The sample was discarded and repeated if the jaws caught material (sticks, gravel) that prevented their full closure. Each collected sample was placed in a bucket, and the suspended sediments allowed to settle. The volume of the sample was measured in a graduated plastic bucket after the water on top was decanted through a 500 µm mesh net, and the contents of the net added to the sample. The measurements of the sample volumes were later used in the laboratory to calculate the percent of different sediment fractions. The entire sample was then sieved through a 300 µm mesh net. This mesh size was found to be optimal, as it retained all the invertebrates and did not become excessively clogged. Attempts to use a smaller mesh required excessively long and energetic sieving, which resulted in significant damage to collected animals. A Hess sampler with a collection net mesh of 500 µm, enclosing an area of 850 cm2, was used for collecting samples from more compacted substrate, prevalent with stones which prevent the Ekman from closing properly. The sampler was securely pressed into the bottom of the stream, and as much substrate as possible was transferred to a bucket from inside of the sampler’s frame. The substrate remaining within the frame was mixed, and cleaned of all attached organisms, which eventually landed inside the collection net. The collected substrate was then taken to the shore, and all stones were carefully cleaned, to ensure the removal of all organisms. The collected material was sieved through a 500 µm mesh net, and then divided into size fractions through a set of sieves. The volume of each fraction was measured using calibrated buckets and cylinders. Five replicate samples were collected from each of the study sites. The collected invertebrates and associated debris were then placed in labelled plastic jars and preserved with 5% buffered formalin. The next day in the laboratory, all the samples were re-examined for the concentration of the preserving solution. Successive replicate samples in flowing watercourses were taken moving upstream to avoid previously disturbed sampling areas. Following the collection of each sample, the sampler and the nets were thoroughly rinsed.

1.1.1 Field Measurements and Observations

The following measurements and observations were taken in the field:

• UTM coordinates using the GPS unit;

• character of valley and riparian vegetation;



• prevailing bottom habitat;

• mean and maximum depth at each site;

• width of wetted channel;

• water and air temperature;

• weather conditions;

• current velocity – range at the site and for each sample;

• depth of each sampling spot; and

• a photograph of each site.

1.2 Laboratory Sample Sorting

Taxonomic analysis of the benthic invertebrate samples was carried out by Biologica Environmental Services Ltd. (Biologica). Upon arrival at the laboratory, the samples were inventoried and checked against chain-of-custody forms. Original field labels were kept with the samples throughout the sample processing procedures and were retained with the debris. Upon arrival at the laboratory, samples were transferred from formalin to alcohol. The sample material was gently washed on a screen to remove the formalin and any residual fine sediment. A screen size of at least half that of the field collection screen size (i.e., 250 µm for a 500 µm field collection screen) was used to retain soft-bodied organisms or fragments that may have contracted during preservation. Larger samples were washed in portions to maximize washing efficiency and prevent loss of material. All material retained on the sieve was returned to the originally labelled plastic jar and preserved in 70% (v/v) ethanol. All original internal and external labels remained with the re-screened sample material.

1.2.1 Splitting Technique

A splitting method was used to facilitate timely sorting and identification of some of the samples. Biologica uses the Caton Tray method. The sample was split as it was being sorted. The trays vary in size and were chosen depending on how much sediment was being sorted (6 quadrat, 12 quadrat and 24 quadrat or greater). Each size of tray also varied in mesh opening (250 µm or 500 µm) depending on the opening in the field screens. Initially, the sample was spread over the top screen by placing the Caton tray over a pan of water so that the debris was floated. When the sample was evenly spread out, the tray was drained and the sorter collected debris from a randomly selected quadrat (labelled with a letter and a number) and sorted that debris. The selection of additional quadrats was repeated until the target number of 300 to 500 organisms had been reached.



1.2.2 Sorting Technique

A standard biological stain (Rose Bengal) was added to the samples to facilitate the sorting process. Rose Bengal targets protein and turns organisms pink or red, making them easier to separate from the sediment matrix of the sample. Samples were sorted by trained technicians. Small fractions of a sample were placed in a dish with a grid and sorted with a dissecting microscope at 10x to 60x magnification. The dish was scanned systematically and all animals were removed using fine forceps. Each dish was sorted until no further organisms are recovered (each dish is sorted at least twice, regardless of the number of organisms recovered). Organisms representing major taxonomic groups (Oligochaeta, Crustacea, Insecta, Nematoda, Mollusca and Other Taxa) were sorted into individually labelled vials containing 70% ethanol.

1.2.3 Aquatic Invertebrate Identification

Identification was undertaken by North American Benthological Society (NABS)-qualified taxonomists using stereo dissecting microscopes and high-power compound microscopes. All organisms found in the samples were enumerated and identified to the lowest practical taxonomic level. If organism fragments were present, only anterior portions were counted. A list of some of the literature used during the taxonomic phase of the project can be found in the references section. Identified organisms were stored in 70% ethanol in glass storage vials, with labels indicating sample number, taxonomist and date. Each sample sorter had 25% of their sorted samples examined by a qualified sorter as a quality control measure. Quality assurance for re-sorts involved examination of each jar of sorted debris that was derived from each sample. A portion of the sample from each jar was spread in a 9" x 13" white pan and examined under a dissecting microscope at 10x magnification. If more than three identifiable organisms are removed per 500 mL then the sample was re-sorted. Any new identified specimens were checked for consistency by the principal taxonomist.



2.0 TERMS AND INDICES USED FOR BENTHIC INVERTEBRATE DATA INTERPRETATION

2.1 The Community Concept and Measurements

Each community is formed of various taxa, each taxon being represented by a specific number of individuals. A higher number of taxa suggest a habitat more versatile in terms of diverse microhabitats, providing a better opportunity for the cohabitation of taxa with different eco-physiological needs and preferences. A higher number of individuals (density) in a taxon, and a higher total number of community members (total density) per substrate surface, indicates a habitat which provides better conditions, mainly in nutritional and spatial terms. This type of habitat imposes less competitive stress on its occupants, particularly on the most abundant taxa. Basic community measures, like the number of species that form a benthic community, and the number of individuals representing each species, were supplemented with the calculation of various community indices. The idea of indices stems from the concept of a community as a system formed by different community units such as individuals, taxa, functional groups, etc., which mutually interact (compete, transfer energy, etc.) and adjust their biological requirements to each other. The state of dynamic balance observed in communities is a function of these mutually adjusted requirements by the competing community units. Communities richer in taxa and with a more equitable distribution of individuals between taxa (i.e., more taxa equally important in processes and interactions) are considered to be more complex. In ecology, this type of complexity is called diversity, and is used as a measure of a community’s endurance and capacity to absorb ecological stresses. Any ecological impediment to a community member, or even its complete elimination due to fluctuating conditions in the environment, is less detrimental to a more diverse community, in which the role of one member can be assumed by other, equally important members. The community indices based on this concept provide not only a condensed measure of the community structure, but also allow insight into how the community functions. The most common community indices are the Diversity and Equitability indices.

2.2 Number of Taxa

The number of species which form a benthic community is one of the basic attributes of each community. However, animals are rarely identified to the level of species, thus the term “number of taxa” is used in this report. This term means the number of taxa which were identified in the particular sample. It represents only some approximation of the true number of taxa in the community, and is always lower than the latest one, due to an existing positive relationship between the size of the sample and the measured number of taxa. The number of taxa is sometimes called diversity, which is a confusion of terms. In ecology, diversity has a different meaning, which is precisely mathematically described.



2.3 Shannon-Weaver Diversity Index

Diversity indices incorporate both species richness and evenness into a single value. Their advantage is providing a synthetic insight into both the community structure and the function, since a more even distribution of individuals among taxa supports the number of meaningful interactions within the community, and enhances community stability. The impossibility of directly determining the relative importance of the two components from one number is often pointed out as their weakness. This can be, however, overcome by separate calculation of the Equitability (evenness) Index. The Shannon-Weaver Diversity Index (H’) is probably the most widely used index in community ecology. It is based on information theory (Shannon and Weaver 1949) and was adapted to ecology by MacArthur (1955) and Margalef (1958). Each community consists of S number of taxa and N number of individuals. The index measures the average degree of uncertainty in predicting to what taxon an individual, chosen at random from a community described by its characteristic S and N, will belong. This uncertainty (source of information) increases as the number of taxa increases and as the distribution of individuals among the taxa becomes even. The equation for the Shannon-Weaver index is:

,

i=1

si iH = -

NN

NN∑ ⎛

⎝⎜⎞⎠⎟

⎛⎝⎜

⎞⎠⎟

⎡

⎣⎢

⎤

⎦⎥ln

where:

s = number of taxa in the sample unit, Ni = number of individuals belonging to the ith taxon, N = total number of individuals in the sample.

H’ = 0 if there is only one taxon in the sample, and H’ is maximal when each taxon in the sample is represented by the same number of individuals (individuals are distributed evenly among sampled taxa).

2.4 Equitability Index

One of the primary variables incorporated in the Shannon-Weaver Diversity Index is the equitability (evenness) with which individuals are distributed amongst taxa. In order to quantify the evenness component of diversity, the Equitability Index by Pielou (1977) was used:

E = H (S)

,

ln

where: H’ = Shannon-Weaver diversity value, and S = total number of taxa in the sample.

A more equitable distribution of individuals amongst taxa (a higher E) indicates a more stable community.



2.5 References

MacArthur, R.H. 1955. Fluctuations of Animal Populations and a Measure of Community Stability. Ecology 36: 433-536.

Margalef, R. 1958. Information Theory in Ecology. General Systematics 3: 36-71.

Pielou, E.C. 1977. Mathematical Ecology. Willey, New York, NY.

Shannon, C.E. and W. Weaver. 1949. The Mathematical Theory of Information. University of Illinois Press Urbana, IL.

Lake habitat near Site A3 (19 September 2010)


Water Body Survey Information Site No.: A3 Basin: A Water Body Name: Hay Lake Stream Order: Lake UTM Location: 12U, E511220, N6149883 Access: Argo/Boat Survey Date – Fall: 19 September 2010 Habitat Type: Depositional

Chemical Data Water Temperature (oC) 8.94 pH 7.49 Dissolved Oxygen (mg/l) 14.81 Conductivity (µS/cm) 195

Sampling Gear and Site Conditions Sampling Gear Used Ekman Preservative Formalin Mesh Size (µm) 500 Macrophyte Cover (%) - Benthic Algae (N/L/M/H) H

Bed Material (%) Organics 5 Small Cobble (64-128mm) - Clay, Silt, Sand (<2mm) 95 Large Cobble (128-256mm) - Small Gravel (2-16mm) - Boulder (>256mm) - Large Gravel (16-64mm) -

Benthic Samples Sample Label

Distance from Bank (m) Depth (m) Water

Velocity (m/s) Sampler

Fullness (%) Number of Jars

Site 7(1) 500 3.17 0 100 1 Site 7(2) 500 3.17 0 100 1 Site 7(3) 500 3.17 0 50 1 Site 7(4) 500 3.17 0 100 1 Site 7(5) 500 3.17 0 100 1

Comments

Sample taken from boat. Easily sieved.

CLIENT: Devon NEC Corporation DATE: Apr 2012 PROJECT: Pike 1 Project JOB No.: CE04050

SUMMARY OF BENTHIC SAMPLING DATA Site A3 FIGURE: H3-1


Typical substrate near Site A5 (19 September 2010)

Water Body Survey Information Site No.: A5 Basin: A Water Body Name: Kirby Lake Stream Order: Lake UTM Location: 12U, E514652, N6146935 Access: Argo/Boat Survey Date – Fall: 19 September 2010 Habitat Type: Depositional


Sampling Gear and Site Conditions Sampling Gear Used Ekman Preservative Formalin Mesh Size (µm) 500 Macrophyte Cover (%) 0 Benthic Algae (N/L/M/H) H







Comments

Sample contained a high sand and algal content. Easily sieved.



Typical stream channel near Site A7 (17 September 2010)

Typical substrate near Site A7 (17 September 2010)

Water Body Survey Information Site No.: A7 Basin: A Water Body Name: Watercourse A-1 Stream Order: 2 UTM Location: 12U, E514963, N6153756 Access: Argo Survey Date – Fall: 17 September 2010 Habitat Type: Depositional


Sampling Gear and Site Conditions Sampling Gear Used Ekman Preservative Formalin Mesh Size (µm) 500 Macrophyte Cover (%) 25 Benthic Algae (N/L/M/H) L

Bed Material (%) Organics 2 Small Cobble (64-128mm) - Clay, Silt, Sand (<2mm) 90 Large Cobble (128-256mm) - Small Gravel (2-16mm) 8 Boulder (>256mm) - Large Gravel (16-64mm) -





5-1 1.41 0.47 0.13 25 2 5-2 1.21 0.5 0.02 30 3 5-3 1.19 0.57 0.08 25 3 5-4 1.05 0.52 0.05 25 3 5-5 1.25 0.51 0.04 25 3

Comments

Eckman would only work in areas with high quantities of macrophytes/organics.



Typical stream habitat near Site B1 (20 September 2010)

Typical sandy substrate near Site B1 (20 September 2010)

Water Body Survey Information Site No.: B1 Basin: B Water Body Name: Sandy River Stream Order: 4 UTM Location: 12U, E523236, N6139033 Access: Argo Survey Date – Fall: 20 September 2010 Habitat Type: Depositional


Sampling Gear and Site Conditions Sampling Gear Used Ekman Preservative Formalin Mesh Size (µm) 500 Macrophyte Cover (%) - Benthic Algae (N/L/M/H) N

Bed Material (%) Organics - Small Cobble (64-128mm) - Clay, Silt, Sand (<2mm) 100 Large Cobble (128-256mm) - Small Gravel (2-16mm) - Boulder (>256mm) - Large Gravel (16-64mm) -





19 – 1 3.5 0.15 0.19 5 1 19 – 2 3.8 0.18 0.16 10 3 19 – 3 3.3 0.17 0.16 10 3 19 – 4 3.4 0.16 0.16 10 2 19 – 5 4.0 0.30 0.18 2 1

Comments


SUMMARY OF BENTHIC SAMPLING DATA Site B1 FIGURE: H3-4



Water Body Survey Information Site No.: B4 Basin: B Water Body Name: Watercourse B-15 Stream Order: 1 UTM Location: 12U, E523236, N6139033 Access: Argo Survey Date – Fall: 21 September 2010 Habitat Type: Depositional


Sampling Gear and Site Conditions Sampling Gear Used Ekman Preservative Formalin Mesh Size (µm) 500 Macrophyte Cover (%) 15 Benthic Algae (N/L/M/H) N






Site 16(1) 0.50 0.40 0 50 2 Site 16(2) 0.47 0.43 0 50 2 Site 16(3) 0.61 0.51 0 50 2 Site 16(4) 0.55 0.55 0 30 2 Site 16(5) 0.50 0.47 0 30 2

Comments

Sandy/organic substrate.



Typical lake habitat at Site B11 (15 September 2010)


Water Body Survey Information Site No.: B11 Basin: B Water Body Name: Lake B-2 Stream Order: Lake UTM Location: 12U, E510005, N6141780 Access: Argo/Boat Survey Date – Fall: 15 September 2010 Habitat Type: Depositional









Comments

No macrophytes, increased fines that could be sieved.





Water Body Survey Information Site No.: B14 Basin: B Water Body Name: Lake B-3 Stream Order: Lake UTM Location: 12U, E509013, N6135870 Access: Argo/Boat Survey Date – Fall: 16 September 2010 Habitat Type: Depositional


Sampling Gear and Site Conditions Sampling Gear Used Ekman Preservative Formalin Mesh Size (µm) 500 Macrophyte Cover (%) 90 Benthic Algae (N/L/M/H) M







Comments




Typical stream substrate near Site B17 (19 September 2010)

Water Body Survey Information Site No.: B17 Basin: B Water Body Name: Watercourse B-16 Stream Order: 2 UTM Location: 12U, E502888, N6136428 Access: Argo Survey Date – Fall: 19 September 2010 Habitat Type: Erosional


Sampling Gear and Site Conditions Sampling Gear Used Hess Preservative Formalin Mesh Size (µm) 500 Macrophyte Cover (%) 20 Benthic Algae (N/L/M/H) M

Bed Material (%) Organics 5 Small Cobble (64-128mm) 15 Clay, Silt, Sand (<2mm) 40 Large Cobble (128-256mm) 5 Small Gravel (2-16mm) 10 Boulder (>256mm) 5 Large Gravel (16-64mm) 10





27-1 0.45 0.37 0.22 10 1 27-2 0.75 0.42 0.44 10 1 27-3 1.47 0.49 0.38 15 2 27-4 2.05 0.37 0.34 15 2 27-5 1.60 0.51 0.25 5 1

Comments

Instream vegetation present in clumps throughout study area. Benthic sample site consisted of less macrophytes than other portions of the survey area.



Benthic sampling at Site C1 (21 September 2010)

Typical stream habitat near Site C1 (21 September 2010)

Water Body Survey Information Site No.: C1 Basin: C Water Body Name: Monday Creek Stream Order: 2 UTM Location: 12U, E505036, N6148783 Access: Argo Survey Date – Fall: 21 September 2010 Habitat Type: Depositional








Site 30(1) 0.20 0.71 0.14 50 2 Site 30(2) 0.20 0.70 0.14 50 1 Site 30(3) 0.20 0.65 0.14 50 1 Site 30(4) 0.20 0.61 0.14 50 1 Site 30(5) 0.20 0.64 0.14 70 1

Comments

Sandy substrate and low organic content.


SUMMARY OF BENTHIC SAMPLING DATA Site C1 FIGURE: H3-9

Appendix H4

Aquatic Habitat Site Descriptions



AQUATIC HABITAT CATALOGUE SHEET DEFINITIONS

Channel Pattern TM = tortuous meanders ME = regular meanders IM = irregular meanders IR = irregular wandering SI = sinuous ST = straight

Coupling

DC = decoupled PC = partially coupled CO = coupled

Islands

N = none O = occasional I = irregular F = frequent S = split AN = anastomosing

Confinement

EN = entrenched CO = confined FC = frequently confined OC = occasionally confined UN = unconfined NA = not applicable

Bars N = none SIDE = sediment deposition intermittent along the sides of streams DIAG = mid-stream sediment deposition diagonally aligned to stream axis MID = mid-stream sediment deposition aligned parallel to stream axis SPAN = sediment deposition continuous along the sides of stream BR = sediment deposition forms a number of small channels separated by bars

Shape U = undercut banks V = vertical S = sloping O = overhanging

Texture F = fines G = gravels C = cobbles B = boulders

Riparian Stage INT = initial SHR = shrub PS = pole-sapling stage YF = young forest MF = mature forest

Riparian Vegetation

N = none G = grasses SHR = shrubs C = coniferous D = deciduous M = mixed C and D types



CATCHMENT A (HAY LAKE AND KIRBY LAKE CATCHMENTS)

Site A1 Description Site A1 is located on an unnamed tributary (Watercourse A) to Christina Lake which drains Hay and Kirby lakes. The channel is unconfined and flows in an irregular meandering pattern. Along the surveyed section, the watercourse had a mean channel width of 8.1 m and a mean wetted width of 5.1 m. The recorded water depths within the study area ranged from 0.24 to 0.50 m in spring 2010 and 0.32 to 0.61 m in fall 2010. The surveyed section was characterized by a moderate gradient channel that was dominated by shallow run habitat with the sporadic pool and riffle habitat. Pools within the study area were considered moderate to high quality with depths exceeding 1.0 m. Channel bed materials within the surveyed reach were predominately fines (66%), followed by cobble (17%), boulder (9%) and gravel (8%). Coarse substrates were typically associated with increased gradient and velocity habitats (i.e., riffles). Banks within the study area were composed of fine material and were typically vertical in shape. The banks in the surveyed reach varied in height from 0.31 to 1.59 m. Riparian areas were undisturbed and predominately comprised of native grasses. Banks in the surveyed section were frequently undercut, creating overhanging vegetation and stream shading. Total available cover for fish species was moderate (20%) and composition varied by season. In spring 2010, large woody debris, small woody debris, undercut banks and depth of watercourse comprised the majority of the fish cover. In fall 2010, instream vegetation, overhanging vegetation and undercut banks dominated the available cover. The water varied from slightly alkaline to neutral (pH of 7.90 in spring 2010 and pH of 7.08 in fall 2010), with an average conductivity of 133 µS/cm and DO concentrations of 9.72 mg/L, 18.61 mg/L and 12.69 mg/L in the spring, fall and winter 2010, respectively. Turbidity was consistently low during all seasons (3.24 and 2.14 NTU). All measured water quality parameters are within CCME guidelines for the protection of aquatic life (CCME 2007). Overall fish habitat is good with a high potential for fish usage year round. Rearing and holding habitat is good due to adequate cover and flow. Spawning potential is good for sucker species and forage fish due to a diversity of velocities and substrates within the studied reach. Spawning habitat for salmonids is poor because suitable substrate is frequently embedded with fines. Instream vegetation and areas of reduced velocity provide moderate spawning habitat for northern pike. Overwintering habitat in the surveyed section is good. Areas displaying moderate velocity ensure DO levels stay sufficient over the winter (12.60 mg/L on 9 March 2011). Four high quality pools were identified with depths exceeding 1.0 m which may serve as refuge habitat. No permanent barriers were observed throughout the studied reach. No fish were captured during sampling conducted spring and fall 2010. Longnose sucker individuals of spawning age were observed in spring 2010. No fish were observed fall 2010.

Water Body Survey Information Site No.: A1 Basin: A Water Body Name: Watercourse A Stream Order: 3 UTM Location: 12U, E0511406, N6158107 Site Length (m): 200 Spring Survey: 19 May 2010 Fall Survey: 21 September 2010 Winter Survey: 09 March 2011

Chemical Data Parameter Spring Fall Winter Water Temperature (oC) 13.50 6.24 -0.12 pH 7.90 7.08 7.43 Dissolved Oxygen (mg/l) 9.72 18.61 12.69 Turbidity (NTU) 3.24 2.14 - Conductivity (µS/cm) 164 101 132

Physical Data Channel Characteristics Pattern: IM Islands: O Bars: N Coupling: DC Confinement: UN Channel Measurements Transect Season T1 T2 T3 Average

Channel Width (m) Spring 9.33 7.08 8.00 8.14 Fall 9.33 7.08 8.00 8.14

Wetted Width (m) Spring 5.26 3.10 6.42 4.93 Fall 5.00 5.00 6.00 5.33

Water Depth (m) Spring 0.37 0.40 0.36 0.38 Fall 0.34 0.54 0.50 0.46

Pool/Riffle/Run/Flat (%) Spring 0/3/97/0 0/0/100/0 2/20/78/0 1/8/91/0 Fall 0/5/95/0 0/0/100/0 0/3/97/0 0/3/97/0

Bed Materials (%) Organics 0 1 0 0 Fines 71 75 50 65 Small Gravel 1 2 5 3 Large Gravel 3 5 5 4 Cobble 15 15 25 19 Boulder 10 2 15 9 Water Body Banks

Bank Height (m) Left 0.90 1.19 0.98 1.02 Right 1.27 1.59 1.15 1.34

Bank Features Shape Texture Riparian Stage

Left V F G - Right V F G -

Cover Data

Cover Type Spring (Total Cover: 32%) Fall (Total Cover: 8%) % Composition % Composition

Undercut Bank 25 2 Large Woody Debris 30 8 Surface Turbulence 3 3 Instream Vegetation 0 60 Small Woody Debris 0 20 Boulder 6 17 Overhanging Vegetation 3 8 Depth Cover 13 2 Turbidity 0 0 Subterranean 0 0

Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring MT NFC Fall MT NFC BPEF NFC

Comments No barriers to fish movement observed. Longnose suckers observed. Substrate was highly embedded and banks were slumping in several areas. Spare overwintering areas observed.

Typical run habitat found at transect 2 (21 September 2010)

Typical rifle habitat found downstream of transect 3 (21 September 2010)

CLIENT: Devon NEC Corporation DATE: April 2012 PROJECT: Pike 1 Project JOB No.: CE04050

SUMMARY OF PHYSICAL AND CHEMICAL DATA Site A1 FIGURE: H4-1




Site A2 Description Site A2 is located on the outlet channel (Watercourse A) of Hay Lake. The channel is unconfined and flows in a straight pattern. Along the surveyed section, the watercourse had a mean channel width of 11.5 m and a mean wetted width of 18.8 m. The recorded water depths within the surveyed section ranged from 0.20 to 0.80 m in spring 2010 and 0.14 to 0.92 m in fall 2010. The surveyed section was characterized by a low gradient channel that was dominated by shallow run and flat habitat. Beaver activity in the area has backed up water widening the wetted width of the stream. Channel bed materials within the surveyed reach were predominately fines (60%) and organics (40%). Banks within the surveyed section were composed of fine material and were typically sloping in shape. The banks in the surveyed reach varied in height from 0.14 to 0.45 m. Riparian areas were comprised of flooded sedges and native grasses. Total available cover for fish species was low (10%). Cover was dominated by instream vegetation, overhanging vegetation and woody debris. The water varied from slightly alkaline to slightly acidic (pH of 7.88 in spring 2010 and pH of 6.40 in fall 2010), with an average conductivity of 213 µS/cm. Dissolved oxygen concentrations measured 12.07 mg/L and 16.67 mg/L in the spring and fall 2010, respectively. Turbidity was consistently low during both seasons (3.76 and 3.84 NTU). All measured water quality parameters are within CCME guidelines for the protection of aquatic life (CCME 2007). Overall fish habitat is moderate. Rearing and holding habitat is moderate to good for forage fish, juvenile sucker species and select juvenile sport fish. The surveyed area lacks sufficient depth and cover diversity to support adult sport fish and sucker species. Spawning potential is poor for sucker species and salmonids due to a lack of coarse substrates and preferred velocity. Instream vegetation and areas of reduced velocity provide moderate spawning habitat for northern pike. Overwintering habitat in the surveyed section is poor. The watercourse lacks depth and displayed an abundance of decomposing aquatic vegetation in spring 2010. Decomposing vegetation, shallow depths and organic substrate would lead to deteriorating DO levels over winter. During the fish inventory conducted in 2010, juvenile northern pike and white sucker were captured.

Water Body Survey Information Site No.: A2 Basin: A Water Body Name: Watercourse A Stream Order: 2 UTM Location: 12U, E0511602, N6150774 Site Length (m): 150 Survey Date – Spring: 14 May 2010 Survey Date – Fall: 20 September 2010

Chemical Data Parameter Spring Fall Water Temperature (oC) 16.25 7.53 pH 7.88 6.40 Dissolved Oxygen (mg/l) 12.07 16.67 Turbidity (NTU) 3.76 3.84 Conductivity (µS/cm) 204 221

Physical Data Channel Characteristics Pattern: ST Islands: O Bars: N Coupling: DC Confinement: UN Channel Measurements Transect Season T1 T2 T3 Average

Channel Width (m) Spring 15 15 8 12.7 Fall 17 16 79 37.3

Wetted Width (m) Spring 30 30 12 24 Fall 17 16 79 37.3






Left S F G - Right S F G -

Cover Data



Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring MT WHSC(1) Fall MT NFC BPEF NRPK(1); WHSC(1)

Comments Shallow, wide creek with organic substrate. Little cover available to fish. Slow run habitat with numerous flats. No visible barriers to fish migration.

Typical slow run/flat habitat upstream of transect 3 (20 September 2010)

Typical flat habitat found within the study area. Note large channel/wetted width (20 September 2010)






Site A3 Description Site A3 is located on Hay Lake. The lake had a well defined outlet channel that flows north towards Christina Lake and receives input from three unnamed watercourses. The lake has a uniform depth (maximum of 4.4 m) over sand and organic substrates, which supports a diverse macrophyte community. Submergent vegetation includes Richardson’s pondweed (Potamogeton richardsonii), narrow-leaf pondweed (Potamogeton spp.) and chara (Chara spp.). Dominant floating-leaf species were yellow water lily (Nuphar variegatum) and common duckweed (Lemna minor). Bulrush (Scirpus spp.) and common cattail (Typha latifolia) were present along the perimeter of the waterbody. Black spruce (Picea mariana), balsam poplar (Populus balsamifera), white birch (Betula papyrifera), native shrubs and grasses surround the lake. The water varied from near neutral to slightly alkaline (average pH of 7.51 in spring/summer/fall 2010, 6.93 in winter 2010/2011 and 8.14 in fall 2011), with an average conductivity of 202 µS/cm and DO concentrations of 12.60 mg/L, 9.15 mg/L and 14.81 mg/L in spring, summer and fall 2010, respectively. Turbidity was consistently low during all seasons, averaging 1.37 NTU. Dissolved oxygen levels were depleted to 3.73 mg/L over the winter due to an abundance of decomposing aquatic vegetation and relatively shallow depth. The CCME guidelines state that a minimum DO level of 5.5 mg/L is required to sustain warm water biota in freshwater systems (CCME 2007), therefore Hay Lake may suffer from occasional winterkills. Overall fish habitat is good within the waterbody. The surveyed section has the potential to provide holding and rearing habitat for northern pike due to the abundance of littoral areas and aquatic vegetation. Rearing and holding potential is good for forage fish, as the waterbody has an abundance of diverse cover. Spawning potential is poor for sucker species and salmonids due to a lack of coarse substrates and preferred velocity. Spawning habitat for forage fish and northern pike is good based on the presence of aquatic vegetation, high cover and abundance of littoral habitat. Overwintering potential in Hay Lake is poor to moderate. The lake has adequate depth to prevent freezing to bottom, however, DO levels may drop below critical levels during productive years. No migration barriers were observed in the vicinity of Hay Lake. During the fish inventory conducted in 2010, adult northern pike and white sucker were captured within Hay Lake. Mean density of invertebrates collected in benthic grabs from Site A3 was 504 individuals/m2 and ranged from 217 to 913 individuals/m2 (Volume 2, Table 9.5-7). Site A3 had the second lowest benthic invertebrate density of ALSA sampling sites (Volume 2, Figure 9.5-2). Overall, non-insects dominated the invertebrate samples, comprising 71% of the mean taxa; insects comprised 29% Non-insects were well distributed among five main taxa, including Copepoda (oar-footed plankton), Cladocera (water fleas), Oligochaeta, Bivalvia (clams) and Ostracoda (seed shrimp) (comprised 19, 16, 14, 10, and 9% of the total mean invertebrates sampled, respectively) Similar to Site A7, insects at Site A3 were predominantly Diptera (comprised 28%



of total mean invertebrates); of which, most were Chironomidae (24% of total mean invertebrates) (Volume 2, Figure 9.5-3). Other insect families represented included Chaoboridae (phantom midges) and Isotomidae (springtails), each comprising 2% of the total mean invertebrates (Volume 3, Appendix H6). No EPT were collected at Site A3. Taxonomic richness was 11, with five dominant, one subdominant and five adominant taxa (Volume 2, Figure 9.5-4). Of these taxa, Chironomidae were most abundant (24% relative abundance), followed by the Copepoda order Calanoida (the lowest practical taxa level for this group), Naididae, the Cladocera order Daphnidae (the lowest practical taxa level for this group), and Sphaeriidae (fingernail clams) (19, 16, 14 and 10%, respectively). Diversity (H’) and evenness (E) indices were the highest of all ALSA benthic sampling sites at 2.02 and 0.84, respectively. Although richness was relatively low, the invertebrates in the community were well distributed among the delineated taxa.

Water Body Survey Information Site No.: A3 Basin: A Water Body Name: Hay Lake UTM Location: 12U, E510967, N6149274 Survey Date

Spring: 15 May 2010 Summer: 30 Jul 2010 Fall: 19 Sept 2010 Winter: 8 Mar 2011 Chemical Data

Parameter Spring Summer Fall Winter Water Temperature (oC) 12.64 19.93 8.94 2.92 pH 7.08 7.95 7.49 7.60 Dissolved Oxygen (mg/l) 12.60 9.15 14.81 3.73 Turbidity (NTU) 1.62 0.76 1.72 - Conductivity (µS/cm) 200 192 195 137

Physical Data Basin Characteristics Lake Basin Genesis: - Hillslope Coupling: DC Shoreline Type: Sand/Gravel Cover Type Parameter Spring Summer Fall Winter Emergent Vegetation (% Cover) 3 - - -

Dominant Species: Reeds; duckweed

bulrush; duckweed

Bulrush; duckweed -

Submergent Vegetation (% Cover) - - - -

Dominant Species: Lily sp. Chara; narrow leaf pondweed Lily sp. -

Dissolved Oxygen and Depth Profile Spring Summer

Profile UTM: 12U, E510967, N6149271 Profile UTM: 12U, E510995, N6149403 Temp#1: 12.64 DO: 12.60 Temp#1: 19.89 DO: 9.37 Temp#2: 12.05 DO: 12.40 Temp#2: 19.89 DO: 9.17 Temp#3: 11.89 DO: 12.31 Temp#3: 19.87 DO: 8.97 Temp#4: 11.85 DO: 12.17 Temp#4: 19.10 DO: 6.27 Temp#5: 11.67 DO: 10.39 Temp#5: 18.88 DO: 5.88 Total Depth (m) 3.81 Temp#6: 18.50 DO: 1.12

Secchi Depth (m) 2.20 Total Depth (m) 3.81 Secchi Depth (m) -

Fall Winter Profile UTM: 12U, E510701, N6149463 Profile UTM: 12U, E511352, N6150269

Temp#1: 9.06 DO: 14.66 Temp#1: 0.52 DO: 5.22 Temp#2: 9.06 DO: 14.66 Temp#2: 1.03 DO: 5.09 Temp#3: 9.05 DO: 14.67 Temp#3: 2.30 DO: 4.43 Temp#4: 9.35 DO: 14.32 Temp#4: 2.92 DO: 3.73

Total Depth (m) 4.05 Temp#5: 3.63 DO: 2.58 Secchi Depth (m) 1.9 Temp#6: 4.01 DO: 0.97

Temp#7: 4.31 DO: 0.52 Total Depth (m) 3.5 Secchi Depth (m) -

Fish Capture Data Season Fish Capture Method Fish Collection Summary

Spring MT NFC BEF - GN NRPK(42)

Summer MT NFC BEF NRPK(1) GN NRPK(16); WHSC(1)

Fall MT NFC BEF NRPK(4) GN NRPK(5)

Comments Sandy shoreline with areas of vegetation and cobble. Shallow lake with uniform habitat and substrate. Northern pike seemed to gather in deeper areas near the middle of the lake. Bulrush dominated the emergent vegetation community along the shoreline.

Mats of yellow water lily (30 Jul 2010)

Bulrush dominates the emergent vegetation near shore (30 Jul 2010)



Pike 1 Project

Fish Habitat Map

Site A3 � Hay Lake

Figure

H4�3A

MAY 15, 2012

PROVIDED BY:

FINAL MAPPING BY:

AMEC

AMEC

0405L01.PDF




Site A4 Description Site A4 is located on a section of Watercourse A that connects Hay and Kirby lakes. The channel is unconfined and demonstrates an irregular meandering pattern. Along the surveyed section, the watercourse had a mean channel width of 0.92 m and mean wetted width of 0.93 m. The recorded water depths within the surveyed section ranged from 0.07 to 0.44 m in spring 2010 and 0.20 to 0.97 m in fall 2010. The surveyed section was characterized by a low gradient channel comprised of shallow run habitat. Channel bed materials within the surveyed reach were predominately fines (87%), followed by organics (10%), gravel (3%) and trace amounts of cobble. Coarse substrates within the surveyed section were embedded with fines. Banks within the study area were composed of fine material and were typically vertical or undercut in shape. The banks in the surveyed reach varied in height from 0.18 to 0.69 m. Riparian areas were undisturbed and predominately comprised of native grasses and shrubs. Banks in the surveyed section were frequently undercut, creating overhanging vegetation and stream shading. Total available cover for fish species was high (20% in spring 2010 and 90% in fall 2010). Composition varied by season. In spring 2010, undercut banks, instream vegetation and overhanging vegetation comprised the majority of the fish cover. In fall 2010, overhanging vegetation, undercut banks and depth of watercourse dominated the available cover. The water was consistently near neutral (pH of 7.11 in spring 2010 and pH of 6.71 in fall 2010), with an average conductivity of 170 µS/cm and DO concentrations of 10.81 mg/L and 18.69 mg/L in the spring and fall 2010, respectively. Turbidity was consistently low during both seasons (3.09 and 5.76 NTU). All measured water quality parameters are within CCME guidelines for the protection of aquatic life (CCME 2007). Overall fish habitat is poor to moderate within the watercourse. Rearing and holding habitat is poor for sport fish and adult sucker species due to the small size of the channel and lack of preferred habitat complexes. Rearing and holding potential is moderate for forage fish as the watercourse had low velocity and an abundance of cover. Spawning potential is poor for sucker species and salmonids due to a lack of coarse substrates. Spawning habitat for forage fish and northern pike is moderate based on the presence of aquatic vegetation, abundance of cover and reduced velocity areas. Overwintering habitat in the surveyed section is poor due to lack of depth and adequate flow. Overwintering potential may exist in surrounding lake habitats given migration is possible. No permanent barriers were observed throughout the studied reach; however, 400 m downstream of the surveyed site, a large beaver impoundment was observed that may impede fish movement between Hay and Kirby lakes. During the fish inventory conducted in spring and fall 2010, brook stickleback and white sucker were captured within Watercourse A.

Water Body Survey Information Site No.: A4 Basin: A Water Body Name: Watercourse A Stream Order: 1 UTM Location: 12U, E0513219, N6148978 Site Length (m): 150 Survey Date – Spring: 14 May 2010 Survey Date – Fall: 20 September 2010


Physical Data Channel Characteristics Pattern: IM Islands: N Bars: N Coupling: DC Confinement: UN Channel Measurements Transect Season T1 T2 T3 Average









Cover Data



Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring MT BRST(5); WHSC(4) Fall MT BRST(1) BPEF NFC

Comments Narrow, small creek with evidence of substantial beaver activity. Large, approximately 400m long beaver dam D/S of site approximately 800m. Overhanging vegetation dominated in fall. Culvert at road crossing is imbedded with substrate at inlet and perched at outlet. May act as a migration barrier for small forage fish. No other substantial barriers were observed throughout the study area.

Typical channel habitat upstream of transect 1 (14 May 2010)

Typical channel habitat in fall. Note the predominant overhanging vegetation (20 September 2010)





CATCHMENT A (HAY LAKE AND KIRBY LAKE CATCHMENTS) Site A5 Description Site A5 is located on Kirby Lake. The lake had a well defined outlet channel that flows northwest towards Hay Lake and receives input from two unnamed watercourses. The lake has a maximum depth of 11.0 m and the substrate is dominated by sand, which supports a diverse macrophyte community. Submergent vegetation includes Richardson’s pondweed, narrow-leaf pondweed and northern watermilfoil (Myriophyllum exalbescens). Yellow water lily was the only floating-leaf species present. Bulrush and common cattail were abundant along the perimeter of the waterbody. White spruce (Picea glauca), aspen (Populus tremuloides), balsam poplar, native shrubs and grasses surround the lake. The water varied from near neutral to slightly alkaline (average pH of 7.70 in spring/summer/fall 2010, 7.68 in winter 2010/2011 and 8.72 in fall 2011), with an average conductivity of 206 µS/cm and DO concentrations of 13.84 mg/L, 9.89 mg/L and 12.87 mg/L in spring, summer and fall 2010, respectively. Turbidity was consistently low during all seasons, averaging 2.35 NTU. Dissolved oxygen levels remained high over the winter (10.51 mg/L on 9 March 2011) due to the relatively large volume compared to other lakes in the ALSA. All measured water quality parameters are within CCME guidelines for the protection of aquatic life (CCME 2007). Overall fish habitat is good within the waterbody. The surveyed section has the potential to provide holding and rearing habitat for a variety of lake-dwelling species due to the diversity of the habitat. Kirby Lake contains an abundance of aquatic vegetation and littoral habitat preferred by northern pike and yellow perch. In addition, the lake contains a large pelagic zone preferred by lake whitefish. Rearing and holding potential is high for forage fish, as the waterbody had an abundance of cover (i.e., aquatic macrophytes). Spawning potential is poor for sucker species and salmonids due to a lack of coarse substrates and preferred velocity. Spawning habitat for forage fish, northern pike and yellow perch is good based on the presence of aquatic vegetation, high cover and abundance of littoral habitat. Spawning habitat for lake whitefish is good due to an abundance of preferred depth and substrate. Overwintering potential in Kirby Lake is good. The lake has adequate depth to prevent freezing to bottom and maintains sufficient oxygen levels over winter to support the resident fish population. During the fish inventory conducted in 2010, all life stages of lake whitefish, northern pike, white sucker and yellow perch were captured within Kirby Lake. Mean density of invertebrates collected from benthic grabs at Site A5 was 600 individuals/m2 and ranged from 174 to 1,087 individuals/m2. Site A5 had the third lowest benthic invertebrate density of ALSA sampling sites. Overall, insects dominated the invertebrate samples, comprising 62% of the mean taxa; non-insects comprised 38%. Insects were only represented by Diptera, which included Chironomidae (comprised 32% of the total mean invertebrates collected) and Chaoboridae (30%). Of the non-insects, the main groups were Oligochaeta, Bivalvia, and Ostracoda; each comprising 10% of the total mean invertebrates. Taxonomic richness was nine, with five dominant, no subdominant and four adominant taxa (Volume 3, Appendix H6). Of these taxa, Chironomidae and Chaoboridae were most abundant (32 and 30% relative abundance, respectively), followed by the Naididae, Sphaeriidae, and the Ostracoda family Candonidae (at 10% each). Site A5’s diversity (D = 1.71) and evenness (ED = 0.78) indices were above the ALSA average (Volume 2, Table 9.5-7; Figure 9.5-4). Although richness was low, the abundance of invertebrates within the taxa groups was relatively even.

Water Body Survey Information Site No.: A5 Basin: A Water Body Name: Kirby Lake UTM Location: 12U, E513288, N6146058 Survey Date

Spring: 13 May 2010 Summer: 1 Aug 2010 Fall: 18 Sept 2010 Winter: 9 Mar 2011 Chemical Data


Physical Data Basin Characteristics Lake Basin Genesis: - Hillslope Coupling: DC Shoreline Type: Sand/Gravel Cover Type Parameter Spring Summer Fall Winter Emergent Vegetation (% Cover) - - 4 -

Dominant Species: Reeds Bulrush; cattails Bulrush; cattails - Submergent Vegetation (% Cover) - - 25 -

Dominant Species: - Richardson’s pondweed

Richardson’s pondweed -


Profile UTM: 12U, E514517, N6147828 Profile UTM: 12U, E514192, N6147304 Temp DO Temp DO Temp DO Temp DO

1 – 7.86 15.25 7 – 7.73 14.51 1 – 20.38 9.57 7 – 18.47 7.18 2 – 7.86 14.96 8 – 7.69 14.46 2 – 20.04 9.15 8 – 18.16 6.19 3 – 7.79 14.81 9 – 7.66 14.42 3 – 19.77 9.32 9 – 17.13 2.13 4 – 7.75 14.72 10 – 7.36 14.20 4 – 19.68 9.13 10 – 16.88 1.22 5 – 7.75 14.60 11 – 7.39 13.83 5 – 19.63 8.65 11 – 16.82 1.17 6 – 7.73 14.59 6 – 18.76 7.94 12 – 16.24 0.29

Total Depth (m) 10.70 Total Depth (m) 10.21 Secchi Depth (m) 3.0 Secchi Depth (m) -


Temp DO Temp DO Temp DO Temp DO 1 – 10.53 12.98 7 – 10.40 13.01 1 – 0.46 11.96 7 – 2.36 8.49 2 – 10.53 12.98 8 – 10.51 13.00 2 – 0.56 11.87 8 – 2.64 7.44 3 – 10.43 13.08 9 – 10.52 12.98 3 – 1.32 11.54 9 – 3.03 6.06 4 – 10.37 13.15 10 – 10.54 12.96 4 – 1.81 11.17 10 – 3.32 3.79 5 – 10.34 13.18 11 – 10.59 12.90 5 – 2.04 10.51 11 – 3.43 1.67 6 – 10.31 13.12 6 – 2.27 9.35


Fish Capture Data Season Fish Capture Method Fish Collection Summary

Spring MT YLPR(29) BEF - GN -

Summer MT YLPR(13) BEF YLPR(5) GN LKWH(7); WHSC(6); YLPR(119)

Fall MT NFC BEF WHSC(5); YLPR(13) GN LKWH(14); NRPK(8)

Comments Rocky shoreline with woody debris and structure. Bottom is comprised of mostly sand mixed with some coarse substrates. Lake appears to be well mixed during all open water seasons. Yellow perch and northern pike found in the littoral areas; lake whitefish found in the pelagic zone.

Facing west from the shoreline. Note the large island in the middle of the lake (18 Sept 2010)

Typical shoreline with overhanging large woody debris (18 Sept 2010)



Pike 1 Project

Fish Habitat Map

Site A5 � Kirby Lake

Figure

H4 � 5A

MAY 15, 2012

PROVIDED BY:

FINAL MAPPING BY:

AMEC

AMEC

04050L01.PDF




Site A6 Description Site A6 is located on a low-level drainage (Watercourse A-5) that potentially connects a small unnamed lake to Kirby Lake. The surveyed section displayed no distinct channel or evidence of scour. Fisheries potential within the watercourse is low. The area resembles a fen type habitat and contains no distinct channel; therefore, no fisheries inventory was completed.

Water Body Survey Information Site No.: A6 Basin: A Water Body Name: Watercourse A-5 Stream Order: 1 UTM Location: 12U, E0516437, N6145535 Site Length (m): - Survey Date: 15 May 2010

Chemical Data Parameter Spring

Water Temperature (oC) - pH -

Dissolved Oxygen (mg/l) - Turbidity (NTU) -

Conductivity (µS/cm) - Physical Data

Channel Characteristics Pattern: - Islands: - Bars: - Coupling: - Confinement: - Channel Measurements Transect Season T1 T2 T3 Average Channel Width (m) Spring - - - - Wetted Width (m) Spring Dry Dry Dry Dry Water Depth (m) Spring Pool/Riffle/Run/Flat (%) Spring - - - - Bed Materials (%) Organics - - - - Fines - - - - Small Gravel - - - - Large Gravel - - - - Small Cobble - - - - Large Cobble - - - - Boulder - - - - Water Body Banks

Bank Height (m) Left - - - - Right - - - -


Left - - - - Right - - - -

Cover Data


Undercut Bank - - Large Woody Debris - - Surface Turbulence - - Instream Vegetation - - Small Woody Debris - - Boulder - - Overhanging Vegetation - - Depth Cover - - Turbidity - - Subterranean - -

Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring - -

Comments No channel or evidence of scour. Fen with tamarack trees and willows.

Downstream view of Site A6 (15 May 2010)

Upstream view of Site A6 (15 May 2010)






Site A7 Description Site A7 is located on Watercourse A-1 that flows northwest draining into Watercourse A. The channel is occasionally confined and demonstrates an irregular wandering pattern. Along the surveyed section, the watercourse had a mean channel width of 4.0 m and mean wetted width of 4.6 m. The recorded water depths within the surveyed section ranged from 0.28 to 0.83 m in spring 2010 and 0.22 to 0.99 m in fall 2010. The surveyed section was characterized by a low gradient channel that was comprised of slow run and flat habitat. Beaver activity is prominent in the area, but no current migration barriers exist at the surveyed location. Channel bed materials within the surveyed reach were predominately fines (84%), followed by organics (8%), boulder (5%), gravel (2%) and cobble (1%). Coarse substrates were embedded with fines. Banks within the surveyed section were composed of fine material and were typically undercut or vertical in shape. The banks in the surveyed reach varied in height from 0.15 to 1.14 m. Riparian areas were undisturbed and predominately comprised of native grasses. Total available cover for fish species was moderate (23%). Cover was dominated by instream vegetation, depth of watercourse, overhanging vegetation and woody debris. The water varied from slightly alkaline to near neutral (pH of 7.81 in spring 2010 and pH of 6.94 in fall 2010), with an average conductivity of 106 µS/cm and DO concentrations of 7.70 mg/L, 13.66 mg/L and 5.49 mg/L in the spring, fall and winter 2010, respectively. Turbidity was consistently low during all seasons (1.28 and 2.24 NTU). All measured water quality parameters were within CCME guidelines for the protection of aquatic life (CCME 2007). Overall fish habitat is moderate to good with the potential to support forage fish year round. Rearing and holding habitat is good due to diverse cover types and depth. Spawning potential is poor for sucker species and salmonids due to a lack of coarse substrates and preferred velocity. Instream vegetation and areas of reduced velocity provide moderate spawning habitat for northern pike. Overwintering habitat in the surveyed section is moderate. Areas of adequate depth ensure DO levels stay sufficient to support forage fish and other small warm water species over the winter (5.50 mg/L on 8 March 2011). During the fish inventory conducted in spring and fall 2010, three forage fish species and one sucker species were captured. Species captured included brook stickleback, finescale dace, pearl dace and white sucker. Mean density of invertebrates collected in benthic grabs from Site A7 was 36,287 individuals/m2, ranging from 29,304 to 44,609 individuals/m2 (Volume 2, Table 9.5-7). Site A7 had the highest benthic invertebrate density of ALSA sampling sites. Overall, insects dominated the invertebrate samples, comprising 81% of the mean taxa; non-insects comprised 19% (Volume 2, Figure 9.5-2). Insects were mainly represented by Diptera (true flies), specifically Chironomidae



(comprised 75% of the total mean invertebrates collected) and Ceratopogonidae (biting midges; 5%) (Volume 2, Figure 9.5-3). Mean %EPT was low at 0.5% of the invertebrates sampled. Correspondingly, Site A7 had a low mean EPT:C value of 0.01 indicating a chironomid-dominated community with respect to these four insect groups. Of the non-insects, the main group was Oligochaeta (aquatic worms) comprising 12% of total mean. Taxonomic richness was 28; however, one taxon, Chironomidae, comprised most of the invertebrate community (75% relative abundance). Other notably abundant family-level taxa included Ceratopogonidae (12% = a dominant taxon) and the Oligochaeta family Naididae (sludge worms; 5% = subdominant) (Volume 3, Appendix H6). There were also five adominant taxa. Diversity (H’) and evenness (E) were 1.04 and 0.31, respectively (Volume 2, Figure 9.5-4). Both index values were the lowest of all ALSA benthic sampling sites. Although richness was relatively high, the sampled invertebrates were poorly distributed among the delineated taxa as Chironomidae dominated the overall community.

Water Body Survey Information Site No.: A7 Basin: A Water Body Name: Watercourse A-1 Stream Order: 2 UTM Location: 12U, E0514936, N6153809 Site Length (m): 200 Spring Survey: 17 May 2010 Fall Survey: 17 September 2010 Winter Survey: 08 March 2011

Chemical Data Parameter Spring Fall Winter Water Temperature (oC) 13.14 7.84 0.35 pH 7.81 6.94 7.99 Dissolved Oxygen (mg/l) 7.70 13.66 5.49 Turbidity (NTU) 1.28 2.24 - Conductivity (µS/cm) 128 83 120

Physical Data Channel Characteristics Pattern: IR Islands: O Bars: SIDE Coupling: PC Confinement: OC Channel Measurements Transect Season T1 T2 T3 Average









Cover Data



Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring MT BRST(11); PRDC(60) Fall MT BRST(8); FNDC(188); WHSC(2) BPEF NFC

Comments Undercut banks at several areas within study reach. Broken beaver impoundment downstream of T2. Overwintering areas in thalweg and beaver impoundment area. Lots of instream vegetation present and hundreds of small cyprinids observed in creek. No permanent barriers observed throughout study reach.

Broken beaver impoundment downstream of transect 2 (17 May 2010)

Typical slow run habitat upstream of transect 2 (17 September 2010)





CATCHMENT B (SANDY RIVER CATCHMENT)

Site B1 Description Site B1 is located on the Sandy River and is the furthest downstream site sampled within the Sandy River watershed. The channel is unconfined and demonstrates a meandering pattern. Along the surveyed section, the watercourse had a mean channel width of 19.7 m and mean wetted width of 14.3 m. The recorded water depths within the surveyed section ranged from 0.28 to 0.87 m in spring 2010 and 0.52 to 1.19 m in fall 2010. The surveyed section was characterized by a low gradient channel that was dominated by moderate velocity run habitat with the sporadic pool. Pools within the surveyed section were considered moderate to high quality having depths exceeding 1.0 m. Channel bed materials within the surveyed reach were predominately fines (88%), followed by gravel (4%), boulder (4%), cobble (3%) and organics (1%). Banks within the surveyed section were composed of fine material and were typically vertical in shape. The banks in the surveyed reach varied in height from 0.91 to 2.50 m. Riparian areas were undisturbed and predominately comprised of native grasses and shrubs. Banks in the study reach were heavily vegetated and frequently undercut, creating overhanging vegetation. Total available cover for fish species was moderate (19%) and diverse. Cover was comprised of woody debris, overhanging vegetation, depth of watercourse, boulder and undercut banks. The water varied from slightly alkaline to near neutral (pH of 7.80 in spring 2010 and pH of 7.36 in fall 2010), with an average conductivity of 137 µS/cm and DO concentrations of 8.87 mg/L and 13.86 mg/L in spring and fall 2010, respectively. Turbidity was consistently low during all seasons (1.53 and 3.82 NTU). All measured water quality parameters are within CCME guidelines for the protection of aquatic life (CCME 2007). Overall fish habitat is good with a high potential for fish usage year round. Rearing and holding habitat is good for a variety of species due to adequate cover, diverse substrates and moderate flow. Spawning potential is moderate for sucker species due to a diversity of velocities and substrates within the studied reach. Spawning habitat for salmonids is poor because suitable substrate is frequently embedded with fines. Woody debris and areas of reduced velocity provide moderate spawning habitat for forage fish. Overwintering habitat in the surveyed section is moderate to good. Areas displaying moderate velocity and adequate depth likely ensure DO levels stay sufficient over the winter. No permanent barriers were observed throughout the studied reach. Pearl dace were the only species captured during the fish inventory conducted spring and fall 2010. White suckers were observed spawning in spring 2010. No fish were observed fall 2010.



Site B1 had the lowest mean invertebrate density of all sampling sites at 200 individuals/m2, ranging from 43 to 304 individuals/m2 (Volume 2, Table 9.5-7; Figure 9.5-2). Generally, the invertebrate community was represented equally by both insects and non-insects (comprised 48 and 52% of the mean total taxa sampled, respectively). Non-insects were represented by three main taxa, including Oligochaeta (comprised 26% of mean total invertebrates), Bivalvia (17%) and Tanaidacea (tanaids; 4%) (Volume 3, Appendix H6). Insects at Site B1 were predominantly Diptera (48% of mean total taxa), specifically Chironomidae (39%), Empididae (dagger flies; 4%) and indeterminate Diptera (4%) (Volume 2, Figure 9.5-3). Other insect taxa represented included Plecoptera (indeterminate), comprising 4% of the total mean. As a result, Site B1 had a low mean %EPT and EPT:C value of 2.9% and 0.20, respectively; indicating a chironomid-dominated community with respect to these four insect groups. Site B1 had the lowest taxonomic richness of all sampling sites at seven, with three dominant, no subdominant and four adominant taxa (Volume 2, Figure 9.5-4). Of the dominant taxa, Chironomidae were most abundant (39% relative abundance), followed by Sphaeriidae (17%) and Naididae (13%). Although Site B1 had low richness, the diversity index (H’) was moderate at 1.58 and evenness (E) was relatively high at 0.81 (Volume 2, Figure 9.5-4).

Water Body Survey Information Site No.: B1 Basin: B Water Body Name: Sandy River Stream Order: 4 UTM Location: NAD 83 Zone 12, E523302, N6139004 Site Length (m): 200 Survey Date – Spring: 18 May 2010 Survey Date – Fall: 20 September 2010


Physical Data Channel Characteristics Pattern: ME Islands: N Bars: N Coupling: DC Confinement: UN Channel Measurements Transect Season T1 T2 T3 Average

Channel Width (m) Spring 19 18 18 18 Fall 30 17 16 21

Wetted Width (m) Spring 15 14 15 14.7 Fall 16 17.44 8.5 13.98



Bed Materials (%) Organics 2 1 1 1.3 Fines 93 95 75 87.6 Small Gravel 0 0 3 1 Large Gravel 0 0 5 1.67 Cobble 0 0 13 4.33 Boulder 5 4 3 4 Water Body Banks



Left V F G/SHR - Right V F G/SHR -

Cover Data



Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring MT PRDC(1) Fall MT NFC BPEF NFC

Comments No permanent barriers to fish migration. Area lacks adequate depths (areas >1.0 m) for overwintering. Slumping banks were present throughout study reach. Spawning suckers were observed in spring.

Downstream view from transect 3 (18 May 2010)

Upstream view from transect 3. Note the low water level (20 September 2010)


SUMMARY OF PHYSICAL AND CHEMICAL DATA Site B1 FIGURE: H4-8

Pike 1 Project

Fish Habitat Map

Site B1 � Sandy River

Figure

H4�8A

MAY 15, 2012

PROVIDED BY:

FINAL MAPPING BY:

AMEC

AMEC

04050L01.PDF




Site B2 Description Site B2 is located on an unnamed tributary (Watercourse B-7) to the Sandy River. The channel is unconfined and demonstrates a sinuous pattern. Along the surveyed section, the watercourse had a mean channel width of 16.7 m and mean wetted width of 5.1 m. The recorded water depths within the surveyed section ranged from 0.10 to 1.44 m in spring 2010 and 0.27 to 0.98 m in fall 2010. The surveyed section was characterized by a low gradient channel that was comprised of low velocity, shallow run and flat habitat. Large channel widths within the surveyed section were due to beaver impoundment downstream of the surveyed reach. Channel bed materials within the surveyed reach were predominately organics. Banks within the surveyed section were composed of fine material and were typically sloping in shape. The banks in the surveyed reach varied in height from 0.18 to 0.98 m. Riparian areas were undisturbed and predominately comprised of native grasses and shrubs. Banks in the surveyed section were heavily vegetated, creating overhanging vegetation and stream shading. Total available cover for fish species was moderate (18%). Cover was dominated by overhanging vegetation, depth of watercourse, woody debris and undercut banks. The water varied from alkaline to slightly acidic (pH of 8.10 in spring 2010 and pH of 6.64 in fall 2010), with an average conductivity of 128 µS/cm and DO concentrations of 7.31 mg/L and 8.14 mg/L in spring and fall 2010, respectively. Turbidity was low during spring (1.81 NTU) but was elevated during the fall sampling (15.2 NTU). All measured water quality parameters are within CCME guidelines for the protection of aquatic life (CCME 2007). Overall fish habitat is moderate to good. The habitat is well suited for forage fish that prefer organic substrates and slow velocities. Rearing and holding habitat is moderate to good for forage fish and northern pike due to vegetation cover and reduced velocity. The surveyed section lacks preferred habitat complexes and adequate flow to support salmonid rearing and holding. Spawning potential is poor for sucker species and salmonids due to a lack of coarse substrates and preferred velocity. Instream vegetation and areas of reduced velocity provide moderate spawning habitat for northern pike and good spawning habitat for forage fish. Overwintering habitat in the surveyed section is moderate. Areas of adequate depth are present; however overwintering potential is limited by flow requirements. Migration is poor within the surveyed reach as beaver dams were present upstream and downstream of the site. This may limit habitat usage by migratory species (i.e., northern pike). During the fish inventory conducted in spring and fall 2010, three forage fish species were captured. Species captured included brook stickleback, finescale dace and pearl dace.

Water Body Survey Information Site No.: B2 Basin: B Water Body Name: Watercourse B-9 Stream Order: 1 UTM Location: 12U, E520819, N6140932 Site Length (m): 200 Survey Date – Spring: 18 May 2010 Survey Date – Fall: 20 September 2010


Physical Data Channel Characteristics Pattern: SI Islands: AN Bars: N Coupling: DC Confinement: UN Channel Measurements Transect Season T1 T2 T3 Average


Wetted Width (m) Spring 12 6 3 7 Fall 1.85 2.59 0.25 1.56






Left S F G/SHR - Right S F G/SHR -

Cover Data



Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring MT BRST(76); FTMN(10); PRDC(560) Fall MT BRST(9); FNDC(9) BPEF BRST(9); FNDC(4)

Comments Migration is poor, beaver dams present upstream and downstream of site. Channel definition is poor at T1; better at T2 and T3. Overwintering potential is limited by flow. Left hand channel has good definition and flow. Transects shifted slightly from spring to fall to document better defined channel.

Downstream view from transect 3 (18 May 2010)

Downstream view from transect 2 (20 September 2010)






Site B3 Description Site B3 is located on an unnamed lake (Lake B-1) that drains into a tributary to the Sandy River. The lake had a poorly defined outlet channel that flows generally south towards the Sandy River. The waterbody has no defined inputs and a muskeg shoreline. The lake has a maximum depth of approximately 2.0 m and the substrate is dominated by sphagnum moss and organics, supporting a diverse macrophyte community. Submergent vegetation is predominantly Richardson’s pondweed and narrow-leaf pondweed. Yellow water lily was the only floating-leaf species present but covered over 50% of the water surface in summer and fall 2010. Dominant emergent species were common cattails and native sedges. Vegetation surrounding the lake included black spruce, tamarack (Larix laricina), muskeg, native shrubs and grasses. The water was consistently near neutral (average pH of 7.02 in spring/summer/fall 2010 and 6.96 in winter 2010/2011), with an average conductivity of 151 µS/cm and DO concentrations of 12.48 mg/L, 7.86 mg/L and 12.94 mg/L in spring, summer and fall 2010, respectively. Turbidity was consistently low during all seasons, averaging 3.25 NTU. Dissolved oxygen levels were depleted to 0.56 mg/L over the winter due to a high abundance of aquatic vegetation and relatively shallow depth. The CCME guidelines state that a minimum DO level of 5.5 mg/L is required to sustain warm water biota in freshwater systems, therefore the unnamed lake likely suffers from frequent winterkills (CCME 2007). During the water quality sampling in winter 2010/2011, a deceased brook stickleback was observed on the lake sediment, serving as evidence to the effect of low DO levels on resident fish species. Overall fish habitat is moderate within the waterbody. The surveyed section has the potential to provide holding and rearing habitat to northern pike due to the abundance of shallow littoral area and aquatic vegetation. Rearing and holding potential is high for forage fish, as the waterbody had an abundance of diverse cover. Spawning potential within the waterbody is poor for sucker species and salmonids due to a lack of depth, coarse substrates and preferred velocity. Spawning habitat for forage fish and northern pike is good based on the presence of aquatic vegetation, high cover and abundance of littoral habitat. Oxygen levels dropped during ice cover, therefore overwintering potential is low. Northern pike habitat usage is dependent on their ability to migrate up Watercourse B-10 from the Sandy River. Migration potential up Watercourse B-10 is low based on its poorly defined channel. During the fish inventory conducted in 2010, two forage fish species were captured: brook stickleback and finescale dace.

Water Body Survey Information Site No.: B3 Basin: B Water Body Name: Lake B-1 UTM Location: 12U, E516634, N6141843 Survey Date


Parameter Spring Summer Fall Winter Water Temperature (oC) 17.20 19.26 10.57 2.13 pH 7.93 6.13 6.99 6.96 Dissolved Oxygen (mg/l) 12.48 7.86 12.94 0.56 Turbidity (NTU) - 4.89 1.61 - Conductivity (µS/cm) 171 135 131 167

Physical Data Basin Characteristics Lake Basin Genesis: - Hillslope Coupling: DC Shoreline Type: Wetland Cover Type Parameter Spring Summer Fall Winter Emergent Vegetation (% Cover) 10 - 10 -

Dominant Species: Sedges Sedges; cattails Sedges; cattails; arrowhead -

Submergent Vegetation (% Cover) 10 - 10 -

Dominant Species: Lily sp.; Chara; Richardson’s

Lily sp.; Sphagnum

Lily sp.; Chara; Richardson’s -


Profile UTM: 12U, E516634, N6141843 Profile UTM: 12U, E516794, N6141853 Temp#1: - DO: - Temp#1: 19.26 DO: 7.86 Temp#2: - DO: - Temp#2: 19.25 DO: 7.72 Temp#3: - DO: - Temp#3: 19.60 DO: 7.37 Temp#4: - DO: - Temp#4: 19.40 DO: 5.35

Total Depth (m) 2.0 Total Depth (m) 1.40 Secchi Depth (m) - Secchi Depth (m) -

Fall Winter

Profile UTM: 12U, E516471, N6141807 Profile UTM: 12U, E516475, N6141823 Temp#1: 10.58 DO: 12.93 Temp#1: - DO: - Temp#2: 10.56 DO: 12.94 Temp#2: - DO: - Total Depth (m) 1.34 Total Depth (m) 1.50

Secchi Depth (m) 1.34 Secchi Depth (m) - Fish Capture Data

Season Fish Capture Method Fish Collection Summary

Spring MT BRST(2); FNDC(424) BEF - GN NFC

Summer MT BRST(44); FNDC(327) BEF NFC GN NFC

Fall MT BRST(86); FNDC(581) BEF BRST(17); FNDC(39) GN -

Comments Bog/Muskeg shoreline. Lake is shallow (max depth of 2 m) with a flat bottom. Good habitat for forage fish. Lake bottom is comprised of sphagnum moss in the summer/fall.

Looking south from shoreline. Note the presence of yellow water lily. (17 Sept 2010)

Cattails dominating shoreline emergent vegetation (18 May 2010)






Site B4 Description Site B4 is located on an unnamed tributary (Watercourse B-15) to the Sandy River. The channel is unconfined and demonstrates an irregular meandering pattern. Along the surveyed section, the watercourse had a mean channel width of 29.9 m and mean wetted width of 5.5 m. The recorded water depths within the surveyed section ranged from 0.05 to 0.41 m in spring 2010 and 0.43 to 0.90 m in fall 2010. The surveyed section was characterized by a low gradient channel that was comprised of low velocity, shallow run and flat habitat. Large channel widths within the surveyed section were due to beaver impoundment downstream of surveyed reach. Channel bed materials within the surveyed reach were predominately organics (93%) and fines (7%). Banks within the surveyed section were composed of fine material and were typically sloping in shape. The banks in the surveyed reach varied in height from 0.25 to 1.80 m. Riparian areas were undisturbed and predominately comprised of native grasses. Banks in the surveyed section were typically low, leading to high amounts of flooded vegetation during high water stages. Total available cover for fish species was low (8%). Cover was dominated by instream and overhanging vegetation. The water varied from slightly alkaline to slightly acidic (pH of 8.00 in spring 2010 and pH of 6.54 in fall 2010), with an average conductivity of 136 µS/cm and DO concentrations of 8.62 mg/L and 14.60 mg/L in spring and fall 2010, respectively. Turbidity was consistently low during both seasons (3.90 and 0.07 NTU). All measured water quality parameters are within CCME guidelines for the protection of aquatic life (CCME 2007). Overall fish habitat is moderate to good. The habitat is well suited for forage fish that prefer fine substrates. Rearing and holding habitat is moderate to good for forage fish and northern pike due to vegetation cover and depth. The study area lacks preferred habitat complexes and adequate flow to support salmonid rearing and holding. Spawning potential is poor for sucker species and salmonids due to a lack of coarse substrates and preferred velocity. Instream vegetation and areas of reduced velocity provide moderate spawning habitat for northern pike and good spawning habitat for forage fish. Overwintering habitat in the surveyed section is moderate. Areas of adequate depth are present, however velocity is low. Migration is poor within the surveyed reach as beaver dams were present upstream and downstream of the site. This may limit habitat usage by migratory species (i.e., northern pike). During the fish inventory conducted in spring and fall 2010, four forage fish species were captured. Species captured included brook stickleback, finescale dace, fathead minnow and pearl dace.



Density of invertebrates collected in benthic grabs from Site B4 was second highest amongst sampling sites with a mean of 20,462 individuals/m2. Invertebrate abundance had a wide variation between replicate samples, ranging from 7,870 to 40,565 individuals/m2 (Volume 2, Table 9.5-7). Overall, insects dominated the invertebrate samples, comprising 66% of the mean taxa collected; non-insects comprised 34% (Volume 2, Figure 9.5-2). Insects were mainly represented by Diptera, specifically Chironomidae (comprised 56% of total mean invertebrates) and Ceratopogonidae (8%) (Volume 2, Figure 9.5-3). Other insect families represented included the Ephemeroptera family Caenidae, the Coleoptera (beetles) family Haliplidae (crawling water beetles), the Odonata (dragonflies) family Libellulidae (skimmers/perchers), and the Trichoptera family Hydroptilidae (purse-case caddisflies) (each comprised ≤1% of the total mean invertebrates). Correspondingly, Site B4 had a low mean %EPT and EPT:C value of 2.6% and 0.06, respectively; indicating a chironomid-dominated community with respect to these four insect groups. Of the non-insects, the main group was Oligochaeta, comprising 23% of the total mean invertebrates sampled. Taxonomic richness was 23, including two dominant, one subdominant, and eight adominant taxa (Volume 3, Appendix H6). Of these taxa, Chironomidae was most abundant (56% relative abundance), followed by Naididae (23%), Ceratopogonidae (8%) and Sphaeriidae (4%). Diversity (H’) and evenness (E) was 1.45 and 0.46, respectively (Volume 2, Figure 9.5-4). Richness and diversity values were moderate for ALSA study sites and invertebrates at Site B4 had moderate distribution among the delineated taxa.


Chemical Data Parameter Spring Fall Water Temperature (oC) 20.6 9.42 pH 8 6.54 Dissolved Oxygen (mg/l) 8.62 14.6 Turbidity (NTU) 3.9 0.07 Conductivity (µS/cm) 134 137


Channel Width (m) Spring 41 47 1.65 29.8 Fall 41 47 2.29 30.1

Wetted Width (m) Spring 14 2.5 1 5.83 Fall 7 6 2.29 5.09







Cover Data



Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring MT BRST(20); FNDC(317); FTMN(39); PRDC(72) Fall MT BRST(5); FNDC(162) BPEF BRST(2); FNDC(23); PRDC(3)

Comments Migration is poor; beaver dams present upstream and downstream of surveyed reach. Channel cover is dominated by overhanging and instream vegetation.

Upstream view from transect 3 (18 May 2010)

Downstream view from transect 1 (14 September 2010)






Site B5 Description Site B5 is located on an unnamed tributary (Watercourse B-9) to the Sandy River. The channel is frequently confined and demonstrates an irregular wandering pattern. Along the surveyed section, the watercourse had a mean channel width of 6.7 m and mean wetted width of 4.3 m. The recorded water depths within the study area ranged from 0.11 to 0.49 m in spring 2010 and 0.04 to 0.35 m in fall 2010. The surveyed section was characterized by a shallow, moderate gradient channel that contained distinct riffle/run complexes. Channel bed materials within the surveyed reach were predominately fines (43%), followed by gravel (37%), cobble (13%), organics (4%) and boulder (3%). Banks within the study area were composed of fine material and varied between sloping and vertical. The banks in the surveyed reach varied in height from 0.42 to 0.98 m. Riparian areas were undisturbed and predominately comprised of native grasses and shrubs. Banks in the study reach were heavily vegetated and frequently undercut, creating overhanging vegetation. Total available cover for fish species was moderate (15%) and diverse. Cover was comprised of woody debris, overhanging vegetation, boulder, undercut banks and surface turbulence. The water varied from alkaline to near neutral (pH of 8.09 in spring 2010 and pH of 7.04 in fall 2010), with an average conductivity of 230 µS/cm and DO concentrations of 9.35 mg/L and 14.22 mg/L in spring and fall 2010, respectively. Turbidity was consistently low during both seasons (0.34 and 0.67 NTU). All measured water quality parameters are within CCME guidelines for the protection of aquatic life (CCME 2007). Overall fish habitat is moderate to good. Habitat is well suited for a variety of forage fish species. Rearing and holding habitat is moderate as the area had adequate cover and diverse habitat types but lacks depth. Spawning habitat for salmonids and suckers is moderate due to suitable substrates and preferred riffle habitat. Spawning potential for northern pike is low, as the area lacks floodable vegetation. Woody debris and low velocity provide good spawning habitat for forage fish. Overwintering habitat in the surveyed section is poor due to lack of depth and adequate flow. No permanent barriers were observed throughout the studied reach. During the fish inventory conducted in spring and fall 2010, three forage fish species were captured: brook stickleback, finescale dace and pearl dace.



Physical Data Channel Characteristics Pattern: IR Islands: N Bars: SIDE/MID Coupling: DC Confinement: FC Channel Measurements Transect Season T1 T2 T3 Average


Wetted Width (m) Spring 5.4 5 2.55 4.3 Fall 3.2 4.4 5 4.2



Bed Materials (%) Organics 7 2 5 4.7 Fines 70 18 40 42.7 Small Gravel 10 20 30 20 Large Gravel 6 30 15 17 Cobble 5 25 9 13 Boulder 2 5 1 2.7 Water Body Banks



Left V/S F SHR/G - Right V/S F SHR/G -

Cover Data



Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring MT BRST(8); PRDC(374) Fall MT BRST(5); FNDC(23) BPEF BRST(1); FNDC(5)

Comments No barriers to fish movement observed. Area lacks depth suitable for overwintering. Diverse habitat types.

Typical riffle upstream of transect 2 (16 September 2010)

Large woody debris and run habitat upstream of transect 3 (16 September 2010)






Site B6 Description Site B6 is located on the Sandy River, approximately 12 km upstream of Site B1. The channel is unconfined and demonstrates a meandering pattern. Along the surveyed section, the watercourse had a mean channel width of 14.7 m and mean wetted width of 12.1 m. The recorded water depths within the study area ranged from 0.33 to 0.95 m in spring 2010 and 0.49 to 1.80 m in fall 2010. The surveyed section was characterized by a moderate gradient channel that contained distinct riffle/run/pool complexes. Pools within the study area were considered moderate to high quality having depths exceeding 1.0 m. Channel bed materials within the surveyed reach were predominately fines (45%), followed by cobble (31%), gravel (16%), boulder (7%) and organics (1%). Banks within the study area were composed of fine material and were typically vertical in shape. The banks in the surveyed reach varied in height from 0.99 to 2.70 m. Riparian areas were undisturbed and predominately comprised of native grasses and coniferous trees. Banks in the study reach were heavily vegetated and frequently undercut, leading to overhanging vegetation. Total available cover for fish species was moderate (24%) and diverse. Cover was comprised of woody debris, overhanging vegetation, depth of watercourse, boulder, undercut banks and surface turbulence. The water varied from slightly alkaline to near neutral (pH of 7.80 in spring 2010 and pH of 7.11 in fall 2010), with an average conductivity of 126 µS/cm and DO concentrations of 8.59 mg/L and 14.19 mg/L in spring and fall 2010, respectively. Turbidity was consistently low during both seasons (3.18 and 1.70 NTU). All measured water quality parameters are within CCME guidelines for the protection of aquatic life (CCME 2007). Overall fish habitat is good with a high potential for fish usage year round. Rearing and holding habitat is good for a variety of species due to adequate cover, diverse habitat and moderate flow. Spawning potential is good for sucker species due to the presence of preferred riffle habitat and coarse substrates within the studied reach. Spawning habitat for salmonids is poor because coarse substrate was large (i.e., large cobbles and boulders) and embedded. Woody debris and areas of reduced velocity provide moderate spawning habitat for forage fish. Overwintering habitat in the surveyed section is moderate to good. Areas displaying moderate velocity and adequate depth likely ensure DO levels stay sufficient over the winter. No permanent barriers were observed throughout the studied reach. During the fish inventory conducted in spring and fall 2010, juvenile northern pike and pearl dace were captured. In addition, during the spring fish inventory, white suckers were observed staging and spawning in close proximity to riffle sections within the study reach.

Water Body Survey Information Site No.: B6 Basin: B Water Body Name: Sandy River Stream Order: 4 UTM Location: 12U, E516230, N6137977 Site Length (m): 200 Spring Survey: 16 May 2010 Summer Survey: 6 August 2010 Fall Survey: 16 September 2010

Chemical Data Parameter Spring Summer Fall Water Temperature (oC) 11.7 17.68 7.66 pH 7.8 6.32 7.11 Dissolved Oxygen (mg/l) 8.59 7.85 14.19 Turbidity (NTU) 3.18 - 1.7 Conductivity (µS/cm) 145 105 107

Physical Data Channel Characteristics Pattern: ME Islands: O Bars: N Coupling: DC Confinement: UN Channel Measurements Transect Season T1 T2 T3 Average


Wetted Width (m) Spring 13 15 7.5 11.8 Fall 12 14.8 10 12.3



Bed Materials (%) Organics 3 1 1 1.7 Fines 50 35 50 45 Small Gravel 5 6 7 6 Large Gravel 7 10 13 10 Cobble 27 40 25 30.7 Boulder 8 8 4 6.7 Water Body Banks

Bank Height (m) Left 1.59 1.42 1.18 1.4 Right 2.7 1 1.15 1.6


Left V F C/G - Right V F C/G -

Cover Data



Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring MT NFC Summer MT NFC BPEF PRDC(5) Fall MT NRPK(1) BPEF NFC

Comments No barriers to fish migration were observed within the study reach. Longnose suckers were observed spawning and staging throughout the study area in spring. Cover is diverse and plentiful.

Typical run habitat upstream of transect 3 (16 May 2010)

Typical riffle habitat upstream of transect 2 (16 May 2010)



Pike 1 Project

Fish Habitat Map


Figure

H4�13A

MAY 15, 2012

PROVIDED BY:

FINAL MAPPING BY:

AMEC

AMEC

04050L01.PDF




Site B7 Description Site B7 is located on the unnamed tributary (Watercourse B-12) of the Sandy River. The channel is confined and demonstrates an irregular meandering pattern. Along the surveyed section, the watercourse had a mean channel width of 9.7 m and mean wetted width of 7.0 m. The recorded water depths within the study area ranged from 0.07 to 0.76 m in spring 2010 and 0.19 to 0.85 m in fall 2010. The surveyed section was characterized by a moderate gradient channel that contained distinct riffle/run complexes. Channel bed materials within the surveyed reach were predominately cobble (43%), followed by fines (32%), gravel (15%), boulder (8%) and organics (2%). Banks within the study area were composed of fine material and varied between vertical and sloping. The banks in the surveyed reach varied in height from 0.32 to 1.67 m. Riparian areas were undisturbed and predominately comprised of native grasses and shrubs. Banks in the study reach were heavily vegetated, creating overhanging vegetation. Total available cover for fish species was low (10%) and diverse. Cover was comprised of woody debris, overhanging vegetation, depth of watercourse, boulder, undercut banks and surface turbulence. The water varied from slightly alkaline to near neutral (pH of 7.80 in spring 2010 and pH of 7.34 in fall 2010), with an average conductivity of 149 µS/cm and DO concentrations of 9.94 mg/L and 14.00 mg/L in spring and fall 2010, respectively. Turbidity was consistently low during both seasons (1.25 NTU in both). All measured water quality parameters are within CCME guidelines for the protection of aquatic life (CCME 2007). Overall fish habitat is moderate to good. Habitat is well suited for a variety of forage fish species. Rearing and holding habitat is moderate as the area had adequate cover and diverse habitat types but lacks depth. Spawning potential is moderate for sucker species due to the presence of preferred riffle habitat and coarse substrates within the studied reach. Spawning habitat for salmonids is poor as the coarse substrate is frequently embedded with fines. Spawning potential for northern pike is moderate, as areas of floodable vegetation are present on the margins of the river. Woody debris and diverse cover provide good spawning habitat for forage fish. Overwintering habitat in the surveyed section is poor due to lack of depth. No permanent barriers were observed throughout the studied reach. During the fish inventory conducted in spring and fall 2010, finescale dace, pearl dace, spoonhead sculpin and white sucker were captured within the study area.


Chemical Data Parameter Spring Fall Water Temperature (oC) 13.3 8.76 pH 7.8 7.34 Dissolved Oxygen (mg/l) 9.94 14 Turbidity (NTU) 1.25 1.25 Conductivity (µS/cm) 144 153

Physical Data Channel Characteristics Pattern: IM Islands: N Bars: N Coupling: DC Confinement: CO Channel Measurements Transect Season T1 T2 T3 Average


Wetted Width (m) Spring 7.21 4.8 8 6.67 Fall 7.65 7.42 7.02 7.36



Bed Materials (%) Organics 5 1 2 2.7 Fines 50 35 10 31.7 Small Gravel 2 2 8 4 Large Gravel 8 14 10 10.7 Cobble 30 40 60 43.3 Boulder 5 8 10 7.7 Water Body Banks



Left V F G - Right S F G -

Cover Data



Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring MT BRST(3); FNDC(178); WHSC(1) Fall MT FNDC(20) BPEF FNDC(8); SPSC(1)

Comments Old beaver dams present throughout the study reach but have been previously breached. No barriers to migration were present. Area lacks depth but displays moderate velocity.

Typical run downstream of transect 2 (15 September 2010)

Typical riffle downstream of transect 3 (15 May 2010)






Site B8 Description Site B8 is located on the inlet channel (Watercourse B-13) of an unnamed lake that drains into the Sandy River. The channel is unconfined and demonstrates a meandering pattern. Along the surveyed section, the watercourse had a mean channel width of 1.9 m and mean wetted width of 1.6 m. The recorded water depths within the study area ranged from 0.29 to 0.70 m in fall 2010 and 0.10 to 0.59 m in spring 2011. The surveyed section was characterized by a low gradient channel that was comprised of low velocity run habitat. Channel bed materials within the surveyed reach were comprised of fines (80%) and organics (20%). Banks within the study area were composed of fine material and varied between vertical and sloping. The banks in the surveyed reach varied in height from 0.08 to 0.58 m. Riparian areas were undisturbed and predominately comprised of native grasses and shrubs. Banks in the study reach were loosely defined and heavily vegetated, creating an abundance of floodable vegetation along the stream margins. Total available cover for fish species was low (10%) and diverse. Cover was comprised of overhanging vegetation, depth of watercourse, instream vegetation, woody debris, and undercut banks. The water was consistently slightly acidic (average pH of 6.45), with an average conductivity of 94 µS/cm and DO concentrations of 12.96 mg/L and 6.19 mg/L in fall 2010 and spring 2011, respectively. Turbidity was consistently low during both seasons (averaging 3.21 NTU). All measured water quality parameters are within CCME guidelines for the protection of aquatic life (CCME 2007). Overall fish habitat is moderate to good. Habitat is well suited for a variety of forage fish species. Rearing and holding habitat is moderate as the area had adequate cover and diverse habitat types but lacks depth. Spawning potential is moderate for salmonids and sucker species because of the lack of suitable substrates and velocities. Spawning potential for northern pike is moderate, as areas of floodable vegetation are present on the margins of the river. Woody debris and diverse cover provide good spawning habitat for forage fish. Overwintering habitat in the surveyed section is poor due to lack of depth. No permanent barriers were observed throughout the studied reach. During the fish inventory conducted in fall 2010 and spring 2011, brook stickleback and finescale dace were captured.

Water Body Survey Information Site No.: B8 Basin: B Water Body Name: Watercourse B-13 Stream Order: 1 UTM Location: 12U, E512372, N6137146 Site Length (m): 200 Survey Date – Fall: 19 September 2010 Survey Date – Spring: 1 June 2011

Chemical Data Parameter Spring Fall Water Temperature (oC) 13.38 2.75 pH 5.97 6.93 Dissolved Oxygen (mg/l) 6.19 12.96 Turbidity (NTU) 0 6.42 Conductivity (µS/cm) 80 108



Wetted Width (m) Spring 1.75 0.8 0.75 1.1 Fall 1.8 1.4 3 2.1


Pool/Riffle/Run/Flat (%) Spring 0/0/100/0 0/0/100/0 0/0/100/0 0/0/100/0 Fall 0/0/100/0 2/0/95/3 0/0/0/100 0.7/0/65/34

Bed Materials (%) Organics 20 10 35 22 Fines 80 90 65 78 Small Gravel 0 0 0 0 Large Gravel 0 0 0 0 Large Cobble 0 0 0 0 Boulder 0 0 0 0 Water Body Banks




Cover Data



Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring MT BRST(6); FNDC(5) Fall MT NFC BPEF BRST(5)

Comments No barriers to fish movement. Stream flows through a low-lying drainage/bog/wetland environment. Channel is defined and incised.

Typical channel habitat present at Site B8 (1 June 2011)

Connectivity with a shallow lake downstream of transect 1 (1 June 2011)






Site B9 Description Site B9 is located on a low-level drainage (Watercourse B-14) that connects to the Sandy River. The study area resembles a typical fen with no distinct channel or evidence of deposition or scour. Fisheries potential within the drainage was low. Therefore, no fisheries inventory was completed.

Water Body Survey Information Site No.: B9 Basin: B Water Body Name: Watercourse B-14 Stream Order: 1 UTM Location: 12U, E521269, N6139390 Site Length (m): - Survey Date: 17 May 2010


Water Temperature (oC) - pH -

Dissolved Oxygen (mg/l) - Turbidity (NTU) -

Conductivity (µS/cm) - Physical Data

Channel Characteristics Pattern: - Islands: - Bars: - Coupling: - Confinement: - Channel Measurements Transect Season T1 T2 T3 Average Channel Width (m) Spring - - - - Wetted Width (m) Spring Dry Dry Dry Dry Water Depth (m) Spring Pool/Riffle/Run/Flat (%) Spring - - - - Bed Materials (%) Organics - - - - Fines - - - - Small Gravel - - - - Large Gravel - - - - Cobble - - - - Boulder - - - - Water Body Banks

Bank Height (m) Left - - - - Right - - - -


Left - - - - Right - - - -

Cover Data



Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring - -

Comments Site was dry.

Upstream of Site B9 (17 May 2010)

Downstream of Site B9 (17 May 2010)






Site B10 Description Site B10 is located on the Sandy River near the middle of the catchment. The channel is unconfined and demonstrates a meandering pattern. Along the surveyed section, the watercourse had a mean channel width of 8.3 m and mean wetted width of 5.5 m. The recorded water depths within the study area ranged from 0.19 to 0.85 m in spring 2010 and 0.44 to 1.10 m in fall 2010. The surveyed section was characterized by a low gradient channel that was comprised of moderate velocity run habitat with the sporadic pool. Channel bed materials within the surveyed reach were comprised of fines (94%) and organics (6%). Banks within the study area were composed of fine material and were typically vertical in shape. The banks in the surveyed reach varied in height from 0.42 to 1.13 m. Riparian areas were undisturbed and predominately comprised of native grasses and shrubs. Total available cover for fish species was low (9%). Cover was dominated by instream vegetation, depth of watercourse, small woody debris and undercut banks. The water was consistently slightly alkaline (pH of 8.10 in spring 2010 and pH of 7.63 in fall 2010), with an average conductivity of 118 µS/cm and DO concentrations of 9.53 mg/L and 15.76 mg/L in the spring and fall 2010, respectively. Turbidity was slightly higher in spring than it was in fall, but still relatively low during both seasons (5.02 and 1.72 NTU). All measured water quality parameters are within CCME guidelines for the protection of aquatic life (CCME 2007). Overall fish habitat is moderate within the Sandy River. Rearing and holding habitat is poor for sport fish and adult sucker species due to the lack of preferred habitat complexes. Rearing and holding potential is moderate for forage fish as the watercourse had some instream vegetation and woody debris. Spawning potential is poor for sucker species and salmonids due to a lack of coarse substrates. Spawning habitat for forage fish and northern pike is moderate based on the presence of instream vegetation and low velocity areas. Overwintering habitat in the surveyed section is moderate to good, as the area contains habitat of adequate depth and flow. No permanent barriers were observed throughout the studied reach. No fish were captured during sampling conducted spring and fall 2010. Adult white sucker individuals were observed in spring 2010. No fish were observed fall 2010.

Water Body Survey Information Site No.: B10 Basin: B Water Body Name: Sandy River Stream Order: 3 UTM Location: 12U, E510437, N6139228 Site Length (m): 200 Survey Date – Spring: 17 May 2010 Survey Date – Fall: 18 September 2010


Physical Data Channel Characteristics Pattern: ME Islands: O Bars: SIDE Coupling: DC Confinement: UN Channel Measurements Transect Season T1 T2 T3 Average


Wetted Width (m) Spring 6 4.35 5 5.1 Fall 6.99 4.97 5.9 5.95


Pool/Riffle/Run/Flat (%) Spring 2/0/98/0 0/0/100/0 0/0/100/0 0.67/0/99.3/0 Fall 2/0/98/0 0/0/100/0 0/0/0/100 0.67/0/66/33.3

Bed Materials (%) Organics 5 7 7 6.3 Fines 95 93 93 93.6 Small Gravel 0 0 0 0 Large Gravel 0 0 0 0 Cobble 0 0 0 0 Boulder 0 0 0 0 Water Body Banks




Cover Data



Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring MT NFC Fall MT NFC BPEF NFC

Comments Reach demonstrates poor habitat diversity. Longnose sucker was observed. Instream vegetation provides fish cover. Old beaver dams provide depth cover and slack water. No barriers to fish migration were observed throughout the study area.

Typical run habitat upstream of transect 3 (17 May 2010)

Typical run habitat downstream of transect 1 (18 September 2010)






Site B11 Description Site B11 is located on an unnamed lake (Lake B-2) in the upper reaches of the Sandy River watershed. The lake had a well defined outlet channel that flows south towards another unnamed lake connected to a tributary to the Sandy River. The waterbody receives inputs from two unnamed watercourses (flowing from the north and west) and borders an unnamed lake to the northeast. The lake has a maximum depth of approximately 4.9 m and the substrate is dominated by fines, which supports a diverse macrophyte community. Submergent vegetation includes coontail (Ceratophyllum demersum), Richardson’s pondweed, northern watermilfoil and narrow-leaf pondweed. Yellow water lily was the only floating-leaf species present. Vegetation surrounding the lake is variable due to topography. White spruce and jackpine pine (Pinus banksiana) are dominant on the north side of the lake, whereas black spruce, tamarack, muskeg, native shrubs and grasses are dominant on the south side of the lake. The water was consistently near neutral (average pH of 6.85 in spring/summer/fall 2010 and 7.37 in winter 2010/2011), with an average conductivity of 109 µS/cm and DO concentrations of 13.84 mg/L, 8.02 mg/L and 12.35 mg/L in spring, summer and fall 2010, respectively. Turbidity was consistently low during all seasons, averaging 2.86 NTU. Dissolved oxygen levels were depleted to 2.19 mg/L over the winter due to a high abundance of aquatic vegetation and relatively shallow depth. The CCME guidelines state that a minimum DO level of 5.5 mg/L is required to sustain warm water biota in freshwater systems, therefore the unnamed lake may suffer from occasional winterkills (CCME 2007). Overall fish habitat is moderate to good within the waterbody. The study area has the potential to provide holding and rearing habitat to northern pike due to the abundance of littoral areas and aquatic vegetation. Rearing and holding potential is high for forage fish, as the waterbody had an abundance of diverse cover. Spawning potential within the waterbody is poor for sucker species and salmonids due to a lack of coarse substrates and preferred velocity. Sucker spawning most likely takes place within an inlet channel to the lake. Spawning habitat for forage fish and northern pike is good based on the presence of aquatic vegetation, high cover and abundance of littoral habitat. Oxygen levels dropped during ice cover, therefore overwintering potential is low. Overwintering habitat may exist in surrounding areas given migration is possible. A beaver dam acts as a migration barrier preventing fish from accessing the unnamed lake bordering the northwest edge. No other migration barriers were found in the vicinity of the waterbody. During the fish inventory conducted in 2010, all life stages of northern pike were captured from the unnamed lake. Additionally, adult longnose sucker and white sucker were also captured from within the waterbody.



Mean invertebrate density for Site B11 was also relatively low compared to other ALSA sites at 7,087 individuals/m2 and ranged from 4,696 to 11,043 (Volume 2, Table 9.5-7). Non-insects dominated the benthic community at this site, comprising 62% of the total mean invertebrates sampled; insects comprised 38% (Volume 2, Figure 9.5-2). Bivalvia and Amphipoda (scuds) made up most of the non-insect portion, comprising 29 and 14% of the total mean invertebrates, respectively. Insects were predominantly Chironomidae, which comprised 36% of total mean invertebrates. Other insect families represented included Ceratopogonidae, Chaoboridae, Ephemeroptera families Caenidae (squaregill mayflies) and Baetidae (small minnow mayflies), and Isotomidae (each comprised ≤ 1% of total mean invertebrates) (Volume 3, Appendix H6). Correspondingly, mean %EPT and EPT:C were low at 0.5% and 0.02, respectively. Taxonomic richness was 22, consisting of three dominant, two subdominant and six adominant taxa (Volume 2, Figure 9.5-4). Dominant taxa included Chironomidae (36%), Sphaeriidae (29%) and the Amphipoda family Gammaridae (gammarids; 14%). Diversity (H’) was relatively high at 1.81 and evenness (E) was moderate at 0.59. Generally, richness and the distribution of benthic invertebrates among represented taxa was moderate at Site B11 compared to other ALSA sites.




Physical Data Basin Characteristics Lake Basin Genesis: - Hillslope Coupling: DC Shoreline Type: Sand/Gravel Cover Type Parameter Spring Summer Fall Winter Emergent Vegetation (% Cover) - - 6 -

Dominant Species: Sedges; grasses Sedges; willow Sedges; lily sp. - Submergent Vegetation (% Cover) - - 40 -

Dominant Species: Lily sp.; Richardson’s

Water lily; Richardson’s

Milfoil; Coontail; Richardson’s -


Profile UTM: 12U, E510091, N6141701 Profile UTM: 12U, E510313, N6141650 Temp#1: 15.52 DO: 10.67 Temp#1: 20.1 DO: 7.98 Temp#2: 15.51 DO: 10.64 Temp#2: 19.2 DO: 7.63 Temp#3: 15.13 DO: 10.14 Temp#3: 19.1 DO: 7.84 Temp#4: 10.74 DO: 7.17 Temp#4: 17.4 DO: 4.76 Temp#5: 10.49 DO: 6.36 Temp#5: 15.1 DO: 0.43 Total Depth (m) 3.66 Total Depth (m) 4.36

Secchi Depth (m) 1.50 Secchi Depth (m) -


Temp#1: 10.96 DO: 12.54 Temp#1: 0.60 DO: 2.89 Temp#2: 10.94 DO: 12.55 Temp#2: 0.97 DO: 2.19 Temp#3: 10.93 DO: 12.56 Temp#3: 2.26 DO: 1.39 Temp#4: 10.50 DO: 13.01 Temp#4: 3.32 DO: 0.71 Temp#5: 10.52 DO: 12.98 Temp#5: 3.95 DO: 0.46 Temp#6: 10.54 DO: 12.96 Total Depth (m) 3.4 Total Depth (m) 4.91 Secchi Depth (m) -

Secchi Depth (m) 1.80 Fish Capture Data


Spring MT NFC BEF - GN LNSC(17); NRPK(5)

Summer MT NRPK(1) BEF NRPK(5) GN NRPK(1); WHSC(3)

Fall MT NFC BEF NFC GN WHSC(12)

Comments Trappers cabin on the southeast shore in the trees. Connectivity to upper lake is restricted by a large beaver dam. North side of lake is conifers and highland forest. South side of the lake is dominated by bog, muskeg and black spruce. Lake is not deep enough to support a lake whitefish population.

Looking east from shoreline. Note the presence of yellow water lily. (14 Sept 2010)

Beaver dam preventing connectivity between the lakes (18 May 2010)



Pike 1 Project

Fish Habitat Map

Site B11 � Lake B�2

Figure

H4�18A

MAY 15, 2012

PROVIDED BY:

FINAL MAPPING BY:

AMEC

AMEC

04050L01.PDF




Site B12 Description Site B12 is located on an unnamed outlet channel (Watercourse B-16-1) to an unnamed lake (Lake B-12) in the Sandy River watershed. The channel is unconfined and demonstrates a sinuous pattern. Along the surveyed section, the watercourse had a mean channel width of 42 m and mean wetted width of 20.5 m. The recorded water depths within the study area ranged from 0.30 to 0.53 m in spring 2010 and 0.32 to 0.68 m in fall 2010. The surveyed section was characterized by a low gradient channel that was comprised of slow velocity, shallow run habitat. A beaver activity impounded water in areas along the stream. Channel bed materials within the surveyed reach were comprised of organics. Banks within the study area were composed of fine material and were typically sloping in shape. The banks in the surveyed reach varied in height from 0.40 to 0.70 m. Riparian areas were predominately comprised of low-lying native grasses. Total available cover for fish species was low (10%). Cover was dominated by instream vegetation, overhanging vegetation and undercut banks. The water was slightly alkaline (pH of 8.00 in spring 2010 and pH of 7.69 in fall 2010), with an average conductivity of 107 µS/cm and DO concentrations of 8.26 mg/L and 13.53 mg/L in the spring and fall 2010, respectively. Turbidity was consistently low during both seasons (1.34 and 1.58 NTU). All measured water quality parameters are within CCME guidelines for the protection of aquatic life (CCME 2007). Overall fish habitat is poor to moderate within the watercourse. Rearing and holding habitat is poor for sport fish and adult sucker species due to the lack of preferred habitat complexes. Rearing and holding potential is moderate for forage fish as the watercourse had low velocity and instream vegetation. Spawning potential is poor for sucker species and salmonids due to a lack of coarse substrates. Spawning habitat for forage fish and northern pike is moderate based on the presence of instream vegetation, floodable grasses on the margins of the channel and low velocity. Overwintering habitat in the surveyed section is poor due to lack of depth and adequate flow. Overwintering potential may exist in surrounding lake habitats given migration is possible. No permanent barriers were observed throughout the studied reach. During the fish inventory conducted in spring and fall 2010, Brook stickleback was the only species captured or observed. During an aerial reconnaissance conducted in the spring of 2011, large bodied fish were observed congregating along the length of the watercourse.

Water Body Survey Information Site No.: B12 Basin: B Water Body Name: Watercourse B-16-1 Stream Order: 1 UTM Location: 12U, E508975, N6143860 Site Length (m): 200 Survey Date – Spring: 17 May 2010 Survey Date – Fall: 18 September 2010


Physical Data Channel Characteristics Pattern: SI Islands: N Bars: N Coupling: DC Confinement: UN Channel Measurements Transect Season T1 T2 T3 Average


Wetted Width (m) Spring 6 7 7 6.67 Fall 30 30 43 34.3



Bed Materials (%) Organics 100 100 100 100 Fines 0 0 0 0 Small Gravel 0 0 0 0 Large Gravel 0 0 0 0 Small Cobble 0 0 0 0 Large Cobble 0 0 0 0 Boulder 0 0 0 0 Water Body Banks




Cover Data



Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring MT BRST(1) Fall MT NFC BPEF NFC

Comments Channel is incised, well defined and situated within low-lying grasses. Beaver dam was observed upstream of transect 3 but does not appear to hinder migration. Substrate was dominated by organics and fines. Area lacks depth required for overwintering and generally resembles a wetland.

Typical channel habitat downstream of transect 1 (17 May 2010)

Typical channel habitat downstream of transect 1 (18 September 2010)






Site B13 Description Site B13 is located on an unnamed tributary (Watercourse B-16) to an unnamed lake (Lake B-2). The channel is unconfined and demonstrates a meandering pattern. Along the surveyed section, the watercourse had a mean channel width of 9.3 m and mean wetted width of 5.8 m. The recorded water depths within the study area ranged from 0.55 to 1.14 m in spring 2010 and 0.31 to 0.93 m in fall 2010. The surveyed section was characterized by a low gradient channel that was comprised of moderate velocity run habitat with the sporadic pool. Channel bed materials within the surveyed reach were predominately fines (91%) and organics (9%). Banks within the study area were composed of fine material and were typically vertical in shape. The banks in the surveyed reach varied in height from 0.69 to 1.86 m. Riparian areas were undisturbed and predominately comprised of native grasses and shrubs. Banks in the study reach were heavily vegetated, creating overhanging vegetation and stream shading. Total available cover for fish species was moderate (25%). Cover was dominated by instream vegetation, overhanging vegetation, depth of watercourse, and undercut banks. The water varied from slightly alkaline to near neutral (pH of 8.10 in spring 2010 and pH of 7.21 in fall 2010), with an average conductivity of 104 µS/cm and DO concentrations of 9.70 mg/L and 14.53 mg/L in spring and fall 2010, respectively. Turbidity was consistently low during both seasons (1.54 and 1.23 NTU). All measured water quality parameters are within CCME guidelines for the protection of aquatic life (CCME 2007). Overall fish habitat is moderate to good with the potential to support forage fish year round. Rearing and holding habitat is good due to diverse cover types and depth. Spawning potential is poor for sucker species and salmonids due to a lack of coarse substrates and preferred velocity. Instream vegetation, floodable vegetation and areas of reduced velocity provide moderate spawning habitat for northern pike and good spawning habitat for forage fish. Overwintering habitat in the surveyed section is moderate. Areas of adequate depth and moderate velocity are present within the surveyed reach. A beaver dam spanning the channel was observed upstream of the surveyed site posing a temporary barrier to fish passage. No other potential migration barriers were observed. During the fish inventory conducted in spring and fall 2010, two forage fish species (brook stickleback, finescale dace) and one sucker species (white sucker) were captured.





Wetted Width (m) Spring 6 5.5 6 5.8 Fall 6.38 6.3 4.58 5.8







Cover Data



Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring MT BRST(207) Fall MT BRST(13); FNDC(7); WHSC(4) BPEF BRST(1); WHSC(1)

Comments Beaver dam observed but does not act as a migration barrier to fish passage. Undercut banks present in study reach. Areas of depth are present but flow is slow. Instream and overhanging vegetation provide fish cover.

Beaver dam upstream of transect 3 (17 May 2010)

Typical channel habitat downstream of transect 2. Note the undercut right bank (17 May 2010)






Site B14 Description Site B14 is located on an unnamed lake (Lake B-3) that drains into Watercourse B-18. The lake had a poorly defined outlet channel that flows southeast towards an unnamed tributary to the Sandy River. The input to the waterbody consists of a large muskeg drainage bordering the northwest corner. The lake has a maximum depth of approximately 1.5 m and the substrate is dominated by organic matter, supporting a large macrophyte community. Submergent vegetation is predominantly Richardson’s pondweed, sphagnum moss (Sphagnum spp.) and northern watermilfoil. Yellow water lily was the only floating-leaf species present and was concentrated along the margins of the lake. Vegetation surrounding the lake included black spruce, tamarack, native shrubs and grasses. Shoreline was frequently undercut and covered with sphagnum moss, providing cover for small fish species. The water was slightly alkaline (average pH of 7.74), with an average conductivity of 244 µS/cm and DO concentrations of 14.92 mg/L and 9.85 mg/L in fall 2010 and spring 2011, respectively. Turbidity was consistently low during all seasons, averaging 1.15 NTU. Dissolved oxygen levels were depleted to 1.62 mg/L over the winter due to a high abundance of aquatic vegetation and relatively shallow depth. The CCME guidelines state that a minimum DO level of 5.5 mg/L is required to sustain warm water biota in freshwater systems (CCME 2007), therefore the unnamed lake likely suffers from frequent winterkills. Overall fish habitat is moderate within the waterbody. The study area has the potential to provide holding and rearing habitat to northern pike due to the abundance of shallow littoral area and aquatic vegetation. Rearing and holding potential is high for forage fish, as the waterbody had an abundance of undercut bank, vegetation and depth cover. Spawning potential within the waterbody is poor for sucker species and salmonids due to a lack of depth, coarse substrates and preferred velocity. Spawning habitat for forage fish and northern pike is good based on the presence of aquatic vegetation and abundance of littoral habitat. Oxygen levels dropped during ice cover, therefore overwintering potential is low. Northern pike habitat usage is dependent on their ability to migrate in from surrounding watercourses. All connector channels associated with the lake are poorly defined and obstructed with vegetation, therefore migration potential is low. During the fish inventory conducted in fall 2010 and spring 2011, three forage fish species were captured: brook stickleback, fathead minnow and pearl dace. Mean density of invertebrates collected in benthic grabs from Site B14 was 19,165 individuals/m2 with a wide range of abundance between replicates (5,530 to 34,861 individuals/m2) (Volume 2, Table 9.5-7). Site B14 had the third highest benthic invertebrate density of ALSA sampling sites (Volume 2, Figure 9.5-2). Generally, the invertebrate community was represented equally by both insects and non-insects (comprised 49 and 51% of mean total taxa sampled, respectively). Non-insects were mostly comprised of



Oligochaeta (19% of mean total invertebrates), followed by Hirudinea (8%), Amphipoda (7%), and Copepoda (6%) (Volume 3, Appendix H6). Insects were mostly represented by Diptera (48% of mean total taxa), specifically Chironomidae (46%) (Volume 2, Figure 9.5-3). Site B14 had a low mean %EPT and EPT:C value of 2.1% and 0.05, respectively; emphasizing the large proportion of chironomids at this site. Taxonomic richness was 23, with two dominant, three subdominant and eight adominant taxa (Volume 2, Figure 9.5-4). The abundance ranking order for dominant and subdominant taxa was: Chironomidae (39% relative abundance), Naididae (17%), Erpobdellidae (leeches; 8%), Gammaridae (7%) and the Copepoda order Cyclopoida (the lowest practical taxa level for this group; 5%). Diversity (H’) was relatively high for ALSA benthic sampling sites at 1.89; evenness (E) was moderate at 0.60.


Fall: 16 Sept 2010 Winter: 12 Mar 2011 Spring: 2 Jun 2011 Chemical Data

Parameter Fall Winter Spring Water Temperature (oC) 8.86 1.47 18.56 pH 8.03 7.08 8.10 Dissolved Oxygen (mg/l) 14.92 1.62 9.85 Turbidity (NTU) 2.29 - - Conductivity (µS/cm) 230 296 205

Physical Data Basin Characteristics Lake Basin Genesis: - Hillslope Coupling: DC Shoreline Type: Wetland/Muskeg Cover Type Parameter Fall Winter Spring Emergent Vegetation (% Cover) - - Sparse

Dominant Species: Sedges; Lily sp. - Lily sp. Submergent Vegetation (% Cover) - - Sparse

Dominant Species: Richardson’s; Sphagnum - Richardson’s; Chara Dissolved Oxygen and Depth Profile


Temp#1: 8.86 DO: 10.67 Temp#1: - DO: - Temp#2: 8.89 DO: 10.64 Temp#2: - DO: -


Spring Profile UTM: 12U, E508933, N6135416

Temp#1: - DO: - Temp#2: - DO: - Temp#3: - DO: - Temp#4: - DO: - Temp#5: - DO: - Temp#6: - DO: -

Total Depth (m) 1.00 Secchi Depth (m) -

Fish Capture Data


Fall MT BRST(28); FNDC(2); FTMN(7) BEF BRST(7); PRDC(1) GN NFC

Winter MT - BEF - GN -

Spring MT BRST(157); FTMN(45) BEF - GN -

Comments Shallow lake with one outlet. Uniform depth, typical muskeg lake. Submergent vegetation covers entire bottom of lake. Lake is poor quality habitat to large bodied species. Lake bottom consists of decomposing organic matter.

Looking east from boat launch (16 Sept 2010)

Typical muskeg shoreline (2 Jun 2011)



Pike 1 Project

Fish Habitat Map


Figure

H4�21A

MAY 15, 2012

PROVIDED BY:

FINAL MAPPING BY:

AMEC

AMEC

04050L01.PDF




Site B15 Description Site B15 is located on an unnamed lake (Lake B-4) that has no defined outlets and is surrounded by muskeg. The lake has a maximum depth of approximately 1.7 m and the substrate is dominated by organic matter, supporting a diverse macrophyte community. Submergent vegetation is predominantly Richardson’s pondweed, sphagnum moss (Sphagnum spp.) and chara. Yellow water lily was the only floating-leaf species present and was concentrated along the margins of the lake. Dominant emergent species were bulrush and native sedges. Vegetation surrounding the lake included black spruce, tamarack, native shrubs and grasses. Shoreline was frequently undercut and covered with sphagnum moss, providing cover for small fish species. The water was slightly alkaline (average pH of 7.66), with an average conductivity of 201 µS/cm and DO concentrations of 14.11 mg/L and 9.30 mg/L in fall 2010 and spring 2011, respectively. Turbidity was consistently low during all seasons, averaging 1.24 NTU. Dissolved oxygen levels were depleted to 1.65 mg/L over the winter due to a high abundance of decaying organic matter and shallow depth. The CCME guidelines state that a minimum DO level of 5.5 mg/L is required to sustain warm water biota in freshwater systems (CCME 2007), therefore the unnamed lake likely suffers from frequent winterkills. Overall fish habitat is moderate within the waterbody. The study area has the potential to provide holding and rearing habitat for northern pike due to the abundance of shallow littoral area and aquatic vegetation. Rearing and holding potential is high for forage fish, as the waterbody had an abundance of undercut bank, vegetation and depth cover. Spawning potential within the waterbody is poor for sucker species and salmonids due to a lack of depth, coarse substrates and preferred velocity. Spawning habitat for forage fish and northern pike is good based on the presence of aquatic vegetation and abundance of littoral habitat. Oxygen levels dropped during ice cover, therefore overwintering potential is low. Northern pike habitat usage is dependent on their ability to migrate in from surrounding watercourses. No connector channels were observed, therefore migration potential is low. During the fish inventory conducted in fall 2010 and spring 2011, brook stickleback and finescale dace were captured from the unnamed lake.


Fall: 16 Sept 2010 Winter: 12 Mar 2011 Spring: 2 Jun 2011 Chemical Data

Parameter Fall Winter Spring Water Temperature (oC) 9.51 0.53 17.73 pH 8.30 7.03 7.66 Dissolved Oxygen (mg/l) 14.11 1.65 9.30 Turbidity (NTU) 2.48 - - Conductivity (µS/cm) 218 201 183

Physical Data Basin Characteristics Lake Basin Genesis: - Hillslope Coupling: DC Shoreline Type: Wetland/Muskeg Cover Type Parameter Fall Winter Spring Emergent Vegetation (% Cover) - - Sparse

Dominant Species: Bulrush; sedges; lily - Lily sp. Submergent Vegetation (% Cover) - - Sparse

Dominant Species: Richardson’s; Sphagnum; milfoil - Richardson’s

Dissolved Oxygen and Depth Profile Fall Winter

Profile UTM: 12U, E507732, N6136070 Profile UTM: 12U, E507882, N6135275 Temp#1: 9.51 DO: 14.11 Temp#1: - DO: -

Temp#2: 10.74 DO: 12.71 Temp#2: - DO: - Temp#3: 10.84 DO: 12.53 Temp#3: 8.89 DO: 10.64 Total Depth (m) 1.71 Total Depth (m) 1.50

Secchi Depth (m) 1.71 Secchi Depth (m) - Spring

Profile UTM: 12U, E507914, N6135288 Temp#1: - DO: - Temp#2: - DO: - Temp#3: - DO: - Temp#4: - DO: - Temp#5: - DO: - Temp#6: - DO: -

Total Depth (m) - Secchi Depth (m) -

Fish Capture Data


Fall MT BRST(17); FNDC(5) BEF BRST(31); FNDC(20) GN -

Winter MT - BEF - GN -

Spring MT BRST(341); FNDC(181) BEF - GN NFC

Comments Typical muskeg lake, shallow/uniform depth and no transition zones. Bulrush stands are present along the margins of the waterbody. Only connectivity to the lake appears to be the muskeg shoreline.

Typical muskeg shoreline (2 Jun 2011)

Gill net set during spring sampling (2 Jun 2011)



Pike 1 Project

Fish Habitat Map


Figure

H4�22A

MAY 15, 2012

PROVIDED BY:

FINAL MAPPING BY:

AMEC

AMEC

04050L01.PDF




Site B16 Description Site B16 is located in the upper reaches of the Sandy River. The channel is occasionally confined and demonstrates an irregular meandering pattern. Along the surveyed section, the watercourse had a mean channel width of 12.3 m and mean wetted width of 5.1 m. The recorded water depths within the study area ranged from 0.27 to 1.79 m in spring 2010 and 0.69 to 1.43 m in fall 2010. The surveyed section was characterized by a low gradient channel that was comprised predominantly of low velocity run habitat with the sporadic pool observed. Some surface turbulence was achieved by water flowing over small beaver dams. Channel bed materials within the surveyed reach were comprised of fines (96%) and organics (4%). Banks within the study area were composed of fine material and varied between vertical and sloping. The banks in the surveyed reach varied in height from 0.63 to 2.48 m. Riparian areas were undisturbed and predominately comprised of native grasses and shrubs. Banks in the study reach were heavily vegetated and frequently undercut, leading to overhanging vegetation. Total available cover for fish species was moderate (18%). Cover was dominated by overhanging vegetation, depth of watercourse, woody debris and undercut banks. The water varied from slightly alkaline to neutral (pH of 8.00 in spring 2010 and pH of 7.22 in fall 2010), with an average conductivity of 136 µS/cm and DO concentrations of 10.92 mg/L and 13.80 mg/L in spring and fall 2010, respectively. Turbidity was consistently low during both seasons (2.86 and 0.37 NTU). All measured water quality parameters are within CCME guidelines for the protection of aquatic life (CCME 2007). Overall fish habitat is moderate to good. The habitat is well suited for forage fish that prefer fine substrates. Rearing and holding habitat is moderate to good for forage fish and northern pike due to low velocity, vegetation cover and depth. The study area lacks preferred substrate and adequate flow to support salmonid rearing and holding. Spawning potential is poor for sucker species and salmonids due to a lack of clean, coarse substrates and preferred velocity. Woody debris and areas of reduced velocity provide good spawning habitat for forage fish. Small areas of floodable vegetation along stream margins may provide some spawning habitat for northern pike. Overwintering habitat in the surveyed section is poor. Areas of adequate depth are present, however velocity is low. No permanent barriers to fish migration were observed throughout the studied reach. During the fish inventory conducted in spring and fall 2010, three forage fish species were captured. Species captured included brook stickleback, finescale dace and pearl dace.

Water Body Survey Information Site No.: B16 Basin: B Water Body Name: Sandy River Stream Order: 3 UTM Location: 12U, E509396, N6133964 Site Length (m): 200 Survey Date – Spring: 15 May 2010 Survey Date – Fall: 15 September 2010


Physical Data Channel Characteristics Pattern: IM Islands: O Bars: SIDE Coupling: DC Confinement: OC Channel Measurements Transect Season T1 T2 T3 Average




Pool/Riffle/Run/Flat (%) Spring 0/10/90/0 0/4/96/0 2/4/94/0 0.7/6/93/0 Fall 10/5/85/0 0/0/100/0 0/0/100/0 3.3/1.7/95/0

Bed Materials (%) Organics 5 2 4 3.7 Fines 95 98 95 96 Small Gravel 0 0 0 0 Large Gravel 0 0 0 0 Large Cobble 0 0 0 0 Boulder 0 0 1 0.3 Water Body Banks



Left V F G - Right V F SHR/G -

Cover Data



Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring MT BRST(20); PRDC(7); WHSC(1) Fall MT BRST(1); FNDC(1) BPEF BRST(1)

Comments No barriers to fish migration. Highly embedded substrate. Beaver activity has created riffle sections, but does not impede fish passage at current levels.

Typical run habitat downstream of transect 1 (15 May 2010)

Riffle created by old beaver impoundment (15 May 2010)



Pike 1 Project

Fish Habitat Map


Figure

H4�23A

MAY 15, 2012

PROVIDED BY:

FINAL MAPPING BY:

AMEC

AMEC

04050L01.PDF




Site B17 Description Site B17 is located an unnamed tributary (Watercourse B-16) to an unnamed lake (Lake B-2). The site is located approximately 10 km upstream from B13. The channel is confined by steep valley walls and demonstrates an irregular meandering pattern. Along the surveyed section, the watercourse had a mean channel width of 5.3 m and mean wetted width of 4.4 m. The recorded water depths within the study area ranged from 0.37 to 0.60 m in fall 2010 and 0.08 to 0.68 m in spring 2011. The surveyed section was characterized by a moderate gradient channel that contained distinct riffle/run/pool complexes. Channel bed materials within the surveyed reach were predominately fines (38%), followed by cobble (37%), gravel (15%) and boulder (10%). Coarse substrates were typically associated with relatively higher velocity habitat (i.e., riffles). Banks within the study area were composed of fine material and varied between sloping and vertical. The banks in the surveyed reach varied in height from 0.15 to 0.73 m. Riparian areas were undisturbed and predominately comprised of native grasses, shrubs and conifers. Banks in the study reach were frequently undercut and heavily vegetated, creating overhanging vegetation and stream shading. Total available cover for fish species was moderate (25%) and diverse. Cover was comprised of instream vegetation, overhanging vegetation, woody debris, depth of watercourse and undercut banks. The water was consistently acidic (pH of 6.54 in fall 2010 and pH of 5.96 in spring 2011), with an average conductivity of 67 µS/cm and DO concentrations of 14.59 mg/L and 9.47 mg/L in fall 2010 and spring 2011, respectively. Turbidity was consistently low during all seasons (average of 1.29 NTU). CCME guidelines state that pH levels between 6.5 and 9.0 are required to sustain warm water biota in freshwater systems, therefore, fish utilizing these areas may require physiological adaptations to cope with the acidic conditions. Forage fish (i.e., brook stickleback) have a high tolerance to poor water quality. Overall fish habitat is good with a high potential for fish usage year round. Rearing and holding habitat is good for a variety of species due to adequate cover, diverse habitat and moderate flow. Spawning potential is good for sucker species due to the presence of preferred riffle habitat and coarse substrates within the studied reach. Spawning habitat for salmonids is good due to suitable substrates and sufficient velocity. Woody debris, instream vegetation and areas of reduced velocity provide good spawning habitat for forage fish. Overwintering habitat in the surveyed section is moderate. Pool areas displaying adequate depth and moderate velocity likely ensure DO levels stay sufficient over the winter. No permanent barriers were observed throughout the studied reach. During the fish inventory conducted in fall 2010 and spring 2011, brook stickleback and finescale dace were captured from the unnamed tributary.



Due to the more compact and coarser (has a higher proportion of gravel) substrate at Site B17 compared to other ALSA sampling sites, Hess sampling was conducted instead of benthic grabs. Site B17 was the only Hess sampling site in the ALSA. At this site, mean density of invertebrates was 10,085 individuals/m2, ranging from 1,835 to 21,600 individuals/m2 (Volume 2, Table 9.5-7). Overall, insects dominated the invertebrate samples, comprising 89% of the mean taxa; non-insects comprised 11% (Volume 2, Figure 9.5-2). Insects were mainly represented by Diptera, specifically Chironomidae (comprised 60% of total mean invertebrates collected) and Empididae (7%) (Volume 2, Figure 9.5-3). Other common insect taxa included Coleoptera (11% of total mean invertebrates), Trichoptera (6%), Ephemeroptera (2%) and Plecoptera (1%). Site B17 had the highest mean %EPT of ALSA sites at 8.4% of the total invertebrates sampled. However, mean EPT:C was still low at 0.18, emphasizing the greater proportion of chironomids at this site. Of the non-insects, the main groups were Bivalvia (comprised 5% of total mean invertebrates), Oligochaeta (3%), and Acari (mites; 3%). Site B17 had the highest taxonomic richness of all ALSA sites sampled: 39. Of these taxa, one was dominant, three were subdominant and eight were adominant (Volume 2, Figure 9.5-4; Volume 3, Appendix H6). The ranking order of dominant and subdominant taxa according to abundance was: Chironomidae (46% relative abundance), the Coleoptera family Elmidae (riffle beetles; 8%), Empididae (7%), and Sphaeriidae (5%). Diversity (H’) was moderate for ALSA benthic sampling sites at 1.65; evenness (E) was relatively low at 0.45. There was poor distribution of invertebrates among the relatively high number of delineated taxa.

Water Body Survey Information Site No.: B17 Basin: B Water Body Name: Watercourse B-16 Stream Order: 2 UTM Location: 12U, E502872, N6136416 Site Length (m): 200 Survey Date – Spring: 1 June 2011 Survey Date – Fall: 19 September 2010

Chemical Data Parameter Spring Fall Water Temperature (oC) 13.9 5.23 pH 5.96 6.54 Dissolved Oxygen (mg/l) 9.47 14.59 Turbidity (NTU) 0 2.58 Conductivity (µS/cm) 67 66

Physical Data Channel Characteristics Pattern: IR Islands: O Bars: N Coupling: DC Confinement: OC Channel Measurements Transect Season T1 T2 T3 Average

Channel Width (m) Spring 3.45 5.5 5.4 4.78 Fall 5.1 5.5 7 5.9




Bed Materials (%) Organics 0 0 0 0 Fines 30 45 40 38 Small Gravel 10 5 0 5 Large Gravel 25 5 0 10 Large Cobble 30 35 45 37 Boulder 5 10 15 10 Water Body Banks



Left S F SHR/G - Right S F SHR/G -

Cover Data



Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring MT BRST(5); FNDC(47) Fall MT BRST(8); FNDC(1) BPEF BRST(5); FNDC(6)

Comments Well defined channel. Good gradient along the surveyed reach has created pool/riffle/run complexes. Creek is frequently confined by steep valley.

Typical run habitat upstream of transect 1 (19 September 2010)

Large woody debris located downstream of transect 2 (19 September 2010)





CATCHMENT C (MONDAY CREEK CATCHMENT)

Site C1 Description Site C1 is located on Monday Creek, approximately 5.5 km downstream from Site C5. The channel is unconfined and demonstrates a sinuous pattern. Along the surveyed section, the watercourse had a mean channel width of 6.9 m and mean wetted width of 6.7 m. The recorded water depths within the study area ranged from 0.42 m to greater than 2 m in fall 2010 and 0.33 to 1.14 m in spring 2011. The surveyed section was characterized by a low gradient channel that was comprised of deep, low velocity run and flat habitat. Channel bed materials within the surveyed reach were predominately fines (92%), followed by organics (6%), cobble (1%) and boulder (1%). Banks within the study area were typically vertical and composed of fine material. The banks in the surveyed reach varied in height from 0.21 to 3.30 m. Riparian areas were undisturbed and predominately comprised of native grasses and shrubs. Banks in the study reach were vertical and heavily vegetated, creating an abundance of overhanging vegetation. Total available cover for fish species was moderate (15%). Cover was dominated by overhanging vegetation, depth of watercourse, instream vegetation and undercut banks. Turbidity cover was also significant in spring 2011. The water was consistently near neutral (average pH of 6.86), with an average conductivity of 97 µS/cm and DO concentrations of 19.18 mg/L and 9.85 mg/L in fall 2010 and spring 2011, respectively. Turbidity was low during fall 2010 sampling (1.61 NTU) but increased in spring 2011 due to isolated bank slumping (visual observation). All measured water quality parameters are within CCME guidelines for the protection of aquatic life (CCME 2007). Overall fish habitat is good with the potential to support a variety of species year round. Rearing and holding habitat is good for forage fish, sucker species and northern pike due to low velocity, depth and vegetative cover. The study area lacks preferred substrate and adequate flow to support salmonid rearing and holding. Spawning potential is poor for sucker species and salmonids due to a lack of clean, coarse substrates and preferred velocity. Instream vegetation, depth cover and low velocity provide good spawning habitat for forage fish. Isolated areas of floodable vegetation along stream margins provide moderate spawning habitat for northern pike. Overwintering habitat in the surveyed section is good due to adequate depth and areas displaying moderate velocity. No permanent barriers to fish migration were observed throughout the studied reach. During the fish inventory conducted in fall 2010 and spring 2011, three forage fish species and one sucker species were captured. Species captured included brook stickleback, lake chub, spoonhead sculpin and white sucker.



Density of invertebrates collected in benthic grabs from Site C1 was 12,530 individuals/m2, ranging from 2,783 to 26,783 individuals/m2 (Volume 2, Table 9.5-7). Overall, insects dominated the invertebrate samples, comprising 65% of the mean taxa collected; non-insects comprised 35% (Volume 2, Figure 9.5-2). Like all ALSA sites, insects were mainly represented by Diptera (65% of the total mean invertebrates collected), and like most ALSA sites, Chironomidae comprised most of the Diptera portion (61% of total mean invertebrates) (Volume 2, Figure 9.5-3). Trichoptera had low abundance at this site and there were no Ephemeroptera or Plecoptera present. Correspondingly, mean %EPT and EPT:C were low at 0.2% and less than 0.01, respectively. Of the non-insects, the main groups were Oligochaeta (comprised 21% of total mean invertebrates) and Acari (12%). Taxonomic richness was 17 at site C1. Of these taxa, there were three dominant, zero subdominant, and three adominant taxa (Volume 3, Appendix H6). Of the dominant taxa, Chironomidae was most abundant (61% relative abundance), followed by Naididae (20%), and indeterminate Hydrachnidia (water mites; 11%). Diversity (H’) and evenness (E) were relatively low at 1.19% and 0.42, respectively (Volume 2, Figure 9.5-4).

Water Body Survey Information Site No.: C1 Basin: C Water Body Name: Monday Creek Stream Order: 2 UTM Location: 12U, E0505037, N6148779 Site Length (m): 200 Survey Date – Spring: 30 May 2011 Survey Date – Fall: 21 September 2010

Chemical Data Parameter Spring Fall Water Temperature (oC) 9.96 5.86 pH 6.11 7.60 Dissolved Oxygen (mg/l) 9.85 19.18 Turbidity (NTU) - 1.61 Conductivity (µS/cm) 42 152

Physical Data Channel Characteristics Pattern: IM Islands: N Bars: SIDE Coupling: DC Confinement: UN Channel Measurements Transect Season T1 T2 T3 Average









Cover Data



Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring MT BRST(6) Fall MT BRST(1); LKCH(1); SPSC(1); WHSC(1) BPEF NFC

Comments Watercourse is well defined with vertical, incised banks. Occasional section of bank is slumping. Habitat is slow moving run with good depth.

Typical run habitat downstream of transect 1 (21 September 2010)

Typical run habitat within the surveyed reach (30 May 2011)


SUMMARY OF PHYSICAL AND CHEMICAL DATA Site C1 FIGURE: H4-25

Pike 1 Project

Fish Habitat Map

Site C1 � Monday Creek

Figure

H4�25A

MAY 15, 2012

PROVIDED BY:

FINAL MAPPING BY:

AMEC

AMEC

04050L01.PDF




Site C2 Description Site C2 is located on an unnamed tributary (Watercourse C-1) to Monday Creek. The unnamed tributary drains a small unnamed waterbody located approximately 2 km upstream of the confluence with Monday Creek. The channel is unconfined and demonstrates an irregular meandering pattern. Along the surveyed section, the watercourse had a mean channel width of 0.59 m and mean wetted width of 0.58 m. In addition, the studied reach contains areas where the channel becomes unconfined and inundates the surrounding muskeg. The recorded water depths within the study area ranged from 0.10 to 0.32 m in fall 2010. The surveyed section was characterized by a narrow, low gradient channel that was dominated by low velocity run habitat. Channel bed materials within the surveyed reach were comprised of fines (63%) and organics (37%). Banks within the study area were typically sloping and composed of fine material. The banks in the surveyed reach varied in height from 0.15 to 0.30 m. Riparian areas were comprised of native grasses and shrubs. Total available cover for fish species was moderate (35%). Cover was dominated by overhanging vegetation, woody debris, and instream vegetation. The water was near neutral (pH of 6.74) with an average conductivity of 96 µS/cm and a DO concentration of 10.79 mg/L. Turbidity was low during fall 2010 (3.68 NTU). All measured water quality parameters are within CCME guidelines for the protection of aquatic life (CCME 2007). Overall fish habitat is poor within the watercourse. Rearing and holding habitat is poor for sport fish and adult sucker species due to the small size of the channel and lack of preferred habitat complexes. Rearing and holding potential is poor to moderate for forage fish as the watercourse had low velocity and high cover, but is frequently shallow and undefined. Spawning potential is poor for sucker species and salmonids due to a lack of coarse substrates. Spawning habitat for forage fish is moderate based on the presence of instream vegetation, moderate cover and reduced velocity areas. Overwintering habitat in the surveyed section is poor due to lack of depth and adequate flow. The channel is highly braided and becomes undefined in areas limiting migration potential for most species. No fish were captured or observed during the sampling conducted fall 2010.

Water Body Survey Information Site No.: C2 Basin: C Water Body Name: Watercourse C-1 Stream Order: 1 UTM Location: 12U, E0505949, N6148241 Site Length (m): 150 Survey Date: 22 September 2010

Chemical Data Parameter Fall

Water Temperature (oC) 4.07 pH 6.74

Dissolved Oxygen (mg/l) 10.79 Turbidity (NTU) 3.68

Conductivity (µS/cm) 96 Physical Data

Channel Characteristics Pattern: IM Islands: N Bars: N Coupling: DC Confinement: UN Channel Measurements Transect Season T1 T2 T3 Average Channel Width (m) Fall 0.62 0.56 0.58 0.59 Wetted Width (m) Fall 0.62 0.54 0.58 0.58 Water Depth (m) Fall 0.15 0.25 0.26 0.22 Pool/Riffle/Run/Flat (%) Fall 0/0/95/5 0/0/100/0 0/0/100/0 0/0/98/2 Bed Materials (%) Organics 10 10 90 37 Fines 90 90 10 63 Small Gravel 0 0 0 0 Large Gravel 0 0 0 0 Small Cobble 0 0 0 0 Large Cobble 0 0 0 0 Boulder 0 0 0 0 Water Body Banks




Cover Data


Undercut Bank - 1 Large Woody Debris - 0 Surface Turbulence - 0 Instream Vegetation - 10 Small Woody Debris - 4 Boulder - 0 Overhanging Vegetation - 80 Depth Cover - 5 Turbidity - 0 Subterranean - 0

Fish Capture Data Season Fish Capture Method Fish Collection Summary Fall MT - BPEF NFC

Comments Fish passage is poor. Creek alternated between channelized and braided along the surveyed reach. Watercourse displays good flows in areas it is channelized. In braided areas, water fans out through riparian mosses and muskeg. Watercourse was too narrow to deploy minnow traps. Increased sampling effort was accomplished via backpack electrofishing. Due to the narrow nature of the watercourse, it was difficult to submerge the cathode and electrode along much of the surveyed length. The watercourse was only sampled once due to its low fisheries potential.

Typical channel downstream of transect 1 (22 September 2010)

Typical channel upstream of transect 1 (22 September 2010)






Site C3 Description Site C3 is located on an unnamed tributary (Watercourse C-2) to Monday Creek. The channel is unconfined and demonstrates a sinuous pattern. Along the surveyed section, the watercourse had a mean channel width of 42.6 m and mean wetted width of 36.7 m. The channel is frequently braided and incised. The recorded water depths within the study area ranged from 0.12 to 1.65 m in fall 2010 and 0.15 to 1.40 m in spring 2011. The surveyed section was characterized by a low gradient channel that was comprised of low velocity run and flat habitat. Large channel widths within the surveyed section were due to beaver impoundment downstream of the surveyed reach. Channel bed materials within the surveyed reach were comprised of fines (63%) and organics (37%). Banks within the study area were typically vertical and composed of fine material. The banks in the surveyed reach varied in height from 0.08 to 1.00 m. Riparian areas were comprised of native grasses and frequently inundated. Total available cover for fish species was moderate (35%). Cover was dominated by overhanging vegetation, depth of watercourse, instream vegetation and undercut banks. The water varied from near neutral to slightly acidic (pH of 6.95 in fall 2010 and pH of 6.04 in spring 2011), with an average conductivity of 67 µS/cm and DO concentrations of 9.76 mg/L and 6.32 mg/L in fall 2010 and spring 2011, respectively. Turbidity was consistently low during both seasons (average of 1.90 NTU). All measured water quality parameters are within CCME guidelines for the protection of aquatic life (CCME 2007). Overall fish habitat is moderate to good. The habitat is well suited for forage fish that prefer fine substrates. Rearing and holding habitat is moderate to good for forage fish and northern pike due to low velocity, vegetative cover and areas with depth. The study area lacks preferred substrate and adequate flow to support salmonid rearing and holding. Spawning potential is poor for sucker species and salmonids due to a lack of clean, coarse substrates and preferred velocity. Instream vegetation, depth and low velocity provide good spawning habitat for forage fish. Areas of floodable vegetation along stream margins may provide some spawning habitat for northern pike. Overwintering habitat in the surveyed section is poor. The studied reach contains areas of sufficient depth but they lack adequate velocity. Beaver activity was observed throughout the studied reach, however, no permanent barriers to fish migration were observed. During the fish inventory conducted in fall 2010 and spring 2011, brook stickleback and white sucker were captured within the studied reach.

Water Body Survey Information Site No.: C3 Basin: C Water Body Name: Watercourse C-2 Stream Order: 2 UTM Location: 12U, E0505867, N6147080 Site Length (m): 200 Survey Date – Spring: 31 May 2011 Survey Date – Fall: 22 September 2010


Physical Data Channel Characteristics Pattern: SI Islands: SI Bars: N Coupling: DC Confinement: UN Channel Measurements Transect Season T1 T2 T3 Average

Channel Width (m) Spring 11.5 26.5 97 45.0 Fall 15.0 20.0 120 51.7








Cover Data



Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring MT BRST(95); WHSC(1) Fall MT BRST(76); WHSC(6) BPEF BRST(1); WHSC(1)

Comments No barriers to fish movement were observed. Channel is frequently braided and incised. Beaver activity was observed throughout the study area.

Typical braided, incised channel (31 May 2011)

Typical braided flat habitat downstream of transect 3 (22 September 2010)






Site C4 Description Site C4 is located on an unnamed tributary (Watercourse C-3) to Monday Creek. The study area had a small, low-lying draw that conveys water across a cutline for approximately 20 m before becoming highly braided and undefined. Average depth is 0.10 m and substrate is comprised of organics. Fisheries potential within the low-lying draw is low. Flow is minimal and the area resembles typical fen habitat with no distinct channel; therefore, no fisheries inventory was completed.

Water Body Survey Information Site No.: C4 Basin: C Water Body Name: Watercourse C-3 Stream Order: 1 UTM Location: 12U, E0502476, N6147409 Site Length (m): 200 Survey Date: 30 May 2011


Water Temperature (oC) 4.95 pH 5.89

Dissolved Oxygen (mg/l) 9.10 Turbidity (NTU) -

Conductivity (µS/cm) 25 Physical Data

Channel Characteristics Pattern: - Islands: - Bars: - Coupling: - Confinement: - Channel Measurements Transect Season T1 T2 T3 Average Channel Width (m) Spring - 35 - 35 Wetted Width (m) Spring - 35 - 35 Water Depth (m) Spring - 0.15 - 0.15 Pool/Riffle/Run/Flat (%) Spring 0/0/0/100 0/0/0/100 0/0/0/100 0/0/0/100 Bed Materials (%) Organics - 0 - 0 Fines - 100 - 100 Small Gravel - 0 - 0 Large Gravel - 0 - 0 Small Cobble - 0 - 0 Large Cobble - 0 - 0 Boulder - 0 - 0 Water Body Banks

Bank Height (m) Left - 0.30 - 0.30 Right - 0.02 - 0.02



Cover Data

Cover Type Spring (Total Cover: 0%) Fall (Total Cover: %) % Composition % Composition


Comments Low fisheries potential. Watercourse was not sampled due to this low potential. Approximately 20 m downstream from transect 2, channel degrades and flow goes subterranean.

Typical channel present at Site C4 (30 May 2011)

Typical channel present at Site C4 (30 May 2011)






Site C5 Description Site C5 is located on unnamed tributary (Watercourse C-4) to Monday Creek and is the furthest upstream site sampled. The channel is unconfined and demonstrates an irregular meandering pattern. Along the surveyed section, the watercourse had a mean channel width of 8.7 m and mean wetted width of 4.0 m. The recorded water depths within the study area ranged from 0.20 to 0.58 m in fall 2010 and 0.09 to 0.40 m in spring 2011. The surveyed section was characterized by a low gradient channel that was comprised of low velocity run and flat habitat. Channel bed materials within the surveyed reach were comprised of fines. Banks within the study area were typically sloping and composed of fine material. The banks in the surveyed reach varied in height from 0.09 to 0.90 m. Riparian areas were undisturbed and predominately comprised of native grasses. Banks in the study reach were heavily vegetated and the channel width was small, creating an abundance of overhanging vegetation. Total available cover for fish species was moderate (15%). Cover was dominated by overhanging vegetation, instream vegetation, woody debris and undercut banks. The water was consistently slightly acidic (pH of 6.83 in fall 2010 and pH of 6.56 in spring 2011), with an average conductivity of 77 µS/cm and DO concentrations of 13.62 mg/L and 6.50 mg/L in fall 2010 and spring 2011, respectively. Turbidity was consistently low during both seasons (average of 1.29 NTU). All measured water quality parameters are within CCME guidelines for the protection of aquatic life (CCME 2007). Overall fish habitat is moderate to good. The habitat is well suited for forage fish that prefer fine substrates. Rearing and holding habitat is moderate to good for forage fish and northern pike due to low velocity and vegetative cover. The study area lacks preferred substrate and adequate flow to support salmonid rearing and holding. Spawning potential is poor for sucker species and salmonids due to a lack of clean, coarse substrates and preferred velocity. Instream vegetation, woody debris and low velocity provide good spawning habitat for forage fish. Areas of floodable vegetation along stream margins may provide some spawning habitat for northern pike. Overwintering habitat in the surveyed section is poor due to lack of depth and sufficient velocity to keep DO levels elevated. No permanent barriers to fish migration were observed throughout the studied reach. During the fish inventory conducted in fall 2010 and spring 2011, brook stickleback were the only species captured or observed within the study reach.

Water Body Survey Information Site No.: C5 Basin: C Water Body Name: Watercourse C-4 Stream Order: 2 UTM Location: 12U, E0502506, N6145266 Site Length (m): 200 Survey Date – Spring: 30 May 2011 Survey Date – Fall: 21 September 2010



Channel Width (m) Spring 2.30 115 12.0 43.1 Fall 19.0 6.0 12.0 12.3

Wetted Width (m) Spring 1.30 102 1.53 34.9 Fall 17.0 1.61 1.53 6.7







Cover Data



Fish Capture Data Season Fish Capture Method Fish Collection Summary Spring MT BRST(13) Fall MT BRST(2) BPEF NFC

Comments No barriers to fish movement observed. Stream is in a low tract of land that was heavily inundated during the spring. Channel is braided and incised.

Abundance of overhanging vegetation present at transect 2 (21 September 2010)

Typical braided, incised channel (30 May 2011)





References Canadian Council of Ministers of the Environment (CCME). 2007. Canadian Water Quality

Guidelines for the Protection of Aquatic Life: Summary Table. Canadian environmental quality guidelines, 1999, Canadian Council of Ministers of the Environment, Winnipeg. Available Online: http://st-ts.ccme.ca/. Accessed 1 February 2012.

Appendix H5

Fish Capture Information



Table H5-1: Common Name, Scientific Name, and Species Code of Fish Species Found Within the Firebag River Watershed

Common Name Scientific Name Species Code1 Arctic grayling Thymallus arcticus ARGR brook stickleback Culaea inconstans BRST burbot Lota lota BURB emerald shiner Notropis atherinoides EMSH flathead chub Platygobio gracilis FLCH goldeye Hiodon alosoides GOLD lake chub Couesius plumbeus LKCH lake whitefish Coregonus clupeaformis LKWH longnose dace Rhinichthys cataractae LNDC longnose sucker Catostomus catostomus LNSC mountain whitefish Prosopium williamsoni MNWH ninespine stickleback Pungitius pungitius NNST northern redbelly dace Phoxinus eos NRDC northern pike Esox lucius NRPK pearl dace Margariscus margarita PRDC slimy sculpin Cottus cognatus SLSC spoonhead sculpin Cottus ricei SPSC spottail shiner Notropis hudsonius SPSH trout-perch Percopsis omiscomaycus TRPR walleye Sander vitreus WALL white sucker Catostomus commersoni WHSC yellow perch Perca flavescens YLPR

Notes: 1 Species codes as per MacKay et al. (1990).

References MacKay, W.C., G.R. Ash and H.J. Norris. (Editors). 1990. Fish Aging Methods in Alberta.

R.L.&L. Environmental Services Ltd. In Assoc. with Alberta Fish and Wildlife Division and University of Alberta, Edmonton, AB.



Table H5-2: Individual Fish Capture Data, Devon Pike EIA, 2010-2011

Fish ID Water Body Site Date Gear1 Species2 Stage3 Maturity4 Sex5 Length (mm) Weight (g) K Factor6

1 Unnamed Creek 5 17-May-10 MT PRDC A MA U 64 - - 2 Unnamed Creek 5 17-May-10 MT PRDC U UN U 36 - - 3 Unnamed Creek 5 17-May-10 MT PRDC A MA U 61 - - 4 Unnamed Creek 5 17-May-10 MT PRDC U UN U 46 - - 5 Unnamed Creek 5 17-May-10 MT BRST U UN U 62 - - 6 Unnamed Creek 5 17-May-10 MT BRST U UN U 61 - - 7 Unnamed Creek 5 17-May-10 MT BRST U UN U 54 - - 8 Unnamed Creek 5 17-May-10 MT BRST U UN U 50 - - 9 Unnamed Creek 5 17-May-10 MT BRST U UN U 62 - - 10 Unnamed Creek 5 17-May-10 MT BRST U UN U 65 - - 11 Unnamed Creek 5 17-May-10 MT BRST U UN U 51 - - 12 Unnamed Creek 5 17-May-10 MT BRST U UN U 51 - - 13 Unnamed Creek 5 17-May-10 MT BRST U UN U 53 - - 14 Unnamed Creek 5 17-May-10 MT BRST U UN U 45 - - 15 Unnamed Creek 5 17-May-10 MT BRST U UN U 53 - - 16 Unnamed Creek 5 17-May-10 MT PRDC U UN U 25 - - 17 Unnamed Creek 5 17-May-10 MT PRDC U UN U 25 - - 18 Unnamed Creek 5 17-May-10 MT PRDC U UN U 25 - - 19 Unnamed Creek 5 17-May-10 MT PRDC U UN U 25 - - 20 Unnamed Creek 5 17-May-10 MT PRDC U UN U 26 - - 21 Unnamed Creek 5 17-May-10 MT PRDC U UN U 25 - - 22 Unnamed Creek 5 17-May-10 MT PRDC U UN U 28 - - 23 Unnamed Creek 5 17-May-10 MT PRDC U UN U 25 - - 24 Unnamed Creek 5 17-May-10 MT PRDC U UN U 22 - - 25 Unnamed Creek 5 17-May-10 MT PRDC U UN U 29 - - 26 Unnamed Creek 5 17-May-10 MT PRDC U UN U 25 - - 27 Unnamed Creek 5 17-May-10 MT PRDC U UN U 25 - - 28 Unnamed Creek 5 17-May-10 MT PRDC U UN U 25 - - 29 Unnamed Creek 5 17-May-10 MT PRDC U UN U 25 - - 30 Unnamed Creek 5 17-May-10 MT PRDC U UN U 25 - - 31 Unnamed Creek 5 17-May-10 MT PRDC U UN U 26 - - 32 Unnamed Creek 5 17-May-10 MT PRDC U UN U 25 - - 33 Unnamed Creek 5 17-May-10 MT PRDC U UN U 25 - - 34 Unnamed Creek 5 17-May-10 MT PRDC U UN U 28 - - 35 Unnamed Creek 5 17-May-10 MT PRDC U UN U 30 - - 36 Unnamed Creek 5 17-May-10 MT PRDC U UN U 31 - -




37 Unnamed Creek 5 17-May-10 MT PRDC U UN U 25 - - 38 Unnamed Creek 5 17-May-10 MT PRDC U UN U 27 - - 39 Unnamed Creek 5 17-May-10 MT PRDC U UN U 35 - - 40 Unnamed Creek 5 17-May-10 MT PRDC U UN U 28 - - 41 Unnamed Creek 5 17-May-10 MT PRDC U UN U 25 - - 42 Unnamed Creek 5 17-May-10 MT PRDC U UN U 31 - - 43 Unnamed Creek 5 17-May-10 MT PRDC U UN U 35 - - 44 Unnamed Creek 5 17-May-10 MT PRDC U UN U 36 - - 45 Unnamed Creek 5 17-May-10 MT PRDC U UN U 26 - - 46 Unnamed Creek 5 17-May-10 MT PRDC U UN U 30 - - 47 Unnamed Creek 5 17-May-10 MT PRDC U UN U 20 - - 48 Unnamed Creek 5 17-May-10 MT PRDC U UN U 31 - - 49 Unnamed Creek 5 17-May-10 MT PRDC U UN U 24 - - 50 Unnamed Creek 5 17-May-10 MT PRDC U UN U 24 - - 51 Unnamed Creek 5 17-May-10 MT PRDC U UN U 25 - - 52 Unnamed Creek 5 17-May-10 MT PRDC U UN U 30 - - 53 Unnamed Creek 5 17-May-10 MT PRDC U UN U 31 - - 54 Unnamed Creek 5 17-May-10 MT PRDC U UN U 30 - - 55 Unnamed Creek 5 17-May-10 MT PRDC U UN U 22 - - 56 Unnamed Creek 5 17-May-10 MT PRDC U UN U 21 - - 57 Unnamed Creek 5 17-May-10 MT PRDC U UN U 27 - - 58 Unnamed Creek 5 17-May-10 MT PRDC U UN U 25 - - 59 Unnamed Creek 5 17-May-10 MT PRDC U UN U 22 - - 60 Unnamed Creek 5 17-May-10 MT PRDC U UN U 25 - - 61 Unnamed Creek 5 17-May-10 MT PRDC U UN U 25 - - 62 Unnamed Creek 5 17-May-10 MT PRDC U UN U 25 - - 63 Unnamed Creek 5 17-May-10 MT PRDC U UN U 27 - - 64 Unnamed Creek 5 17-May-10 MT PRDC U UN U 30 - - 65 Unnamed Creek 5 17-May-10 MT PRDC U UN U 26 - - 66 Unnamed Creek 5 17-May-10 MT PRDC U UN U 24 - - 67 Unnamed Creek 5 17-May-10 MT PRDC U UN U 30 - - 68 Unnamed Creek 5 17-May-10 MT PRDC U UN U 26 - - 69 Unnamed Creek 5 17-May-10 MT PRDC U UN U 28 - - 70 Unnamed Creek 5 17-May-10 MT PRDC U UN U 30 - - 71 Unnamed Creek 5 17-May-10 MT PRDC U UN U 27 - - 72 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U 55 - - 73 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U 65 - - 74 Unnamed Creek 5 17-Sep-10 MT FNDC A MA U 81 - -




75 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 55 - - 76 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 50 - - 77 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 55 - - 78 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 52 - - 79 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 60 - - 80 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 45 - - 81 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 53 - - 82 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 52 - - 83 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 48 - - 84 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 58 - - 85 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 51 - - 86 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 56 - - 87 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 50 - - 88 Unnamed Creek 5 17-Sep-10 MT FNDC A MA U 72 - - 89 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 60 - - 90 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 45 - - 91 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 53 - - 92 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 55 - - 93 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U 67 - - 94 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 54 - - 95 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 50 - - 96 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 48 - - 97 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 42 - - 98 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 55 - - 99 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 54 - - 100 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 49 - - 101 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U 64 - - 102 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 60 - - 103 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 58 - - 104 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U 62 - - 105 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 52 - - 106 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 45 - - 107 Unnamed Creek 5 17-Sep-10 MT FNDC A MA U 68 - - 108 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 52 - - 109 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 49 - - 110 Unnamed Creek 5 17-Sep-10 MT FNDC A MA U 78 - - 111 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U 63 - - 112 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 51 - -




113 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 50 - - 114 Unnamed Creek 5 17-Sep-10 MT FNDC A MA U 70 - - 115 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 55 - - 116 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 48 - - 117 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 40 - - 118 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 55 - - 119 Unnamed Creek 5 17-Sep-10 MT FNDC A MA U 67 - - 120 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U 61 - - 121 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U 60 - - 122 Unnamed Creek 5 17-Sep-10 MT FNDC A MA U 69 - - 123 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 56 - - 124 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 55 - - 125 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 53 - - 126 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 50 - - 127 Unnamed Creek 5 17-Sep-10 MT FNDC A MA U 90 - - 128 Unnamed Creek 5 17-Sep-10 MT FNDC A MA U 82 - - 129 Unnamed Creek 5 17-Sep-10 MT FNDC A MA U 70 - - 130 Unnamed Creek 5 17-Sep-10 MT FNDC A MA U 74 - - 131 Unnamed Creek 5 17-Sep-10 MT FNDC A MA U 71 - - 132 Unnamed Creek 5 17-Sep-10 MT FNDC A MA U 71 - - 133 Unnamed Creek 5 17-Sep-10 MT FNDC A MA U 61 - - 134 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 51 - - 135 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 51 - - 136 Unnamed Creek 5 17-Sep-10 MT FNDC A MA U 72 - - 137 Unnamed Creek 5 17-Sep-10 MT FNDC A MA U 65 - - 138 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 50 - - 139 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 60 - - 140 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 50 - - 141 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 54 - - 142 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 48 - - 143 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 59 - - 144 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 47 - - 145 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 45 - - 146 Unnamed Creek 5 17-Sep-10 MT FNDC A MA U 66 - - 147 Unnamed Creek 5 17-Sep-10 MT FNDC A MA U 76 - - 148 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U 62 - - 149 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U 59 - - 150 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 55 - -




151 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 48 - - 152 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U 58 - - 153 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 55 - - 154 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U 58 - - 155 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 58 - - 156 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 53 - - 157 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 48 - - 158 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 49 - - 159 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 46 - - 160 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 52 - - 161 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 41 - - 162 Unnamed Creek 5 17-Sep-10 MT FNDC A MA U 70 - - 163 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 53 - - 164 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 46 - - 165 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 54 - - 166 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 55 - - 167 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 52 - - 168 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 52 - - 169 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U 58 - - 170 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U 57 - - 171 Unnamed Creek 5 17-Sep-10 MT FNDC J IM U 53 - - 172 Unnamed Creek 5 17-Sep-10 MT WHSC J IM U 87 - - 173 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 174 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 175 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 176 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 177 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 178 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 179 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 180 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 181 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 182 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 183 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 184 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 185 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 186 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 187 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 188 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - -




189 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 190 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 191 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 192 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 193 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 194 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 195 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 196 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 197 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 198 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 199 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 200 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 201 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 202 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 203 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 204 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 205 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 206 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 207 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 208 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 209 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 210 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 211 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 212 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 213 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 214 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 215 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 216 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 217 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 218 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 219 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 220 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 221 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 222 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 223 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 224 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 225 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 226 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - -




227 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 228 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 229 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 230 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 231 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 232 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 233 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 234 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 235 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 236 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 237 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 238 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 239 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 240 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 241 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 242 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 243 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 244 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 245 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 246 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 247 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 248 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 249 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 250 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 251 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 252 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 253 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 254 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 255 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 256 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 257 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 258 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 259 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 260 Unnamed Creek 5 17-Sep-10 MT FNDC U UN U - - - 261 Unnamed Creek 5 17-Sep-10 MT BRST U UN U - - - 262 Unnamed Creek 5 17-Sep-10 MT BRST U UN U - - - 263 Unnamed Creek 5 17-Sep-10 MT BRST U UN U - - - 264 Unnamed Creek 5 17-Sep-10 MT BRST U UN U - - -




265 Unnamed Creek 5 17-Sep-10 MT BRST U UN U - - - 266 Unnamed Creek 5 17-Sep-10 MT BRST U UN U - - - 267 Unnamed Creek 5 17-Sep-10 MT BRST U UN U - - - 268 Unnamed Creek 5 17-Sep-10 MT BRST U UN U - - - 269 Unnamed Creek 5 17-Sep-10 MT WHSC U UN U - - - 270 Unnamed Creek 6 15-May-10 MT WHSC J IM U 48 - - 271 Unnamed Creek 6 20-Sep-10 BPEF NRPK J IM U 161 37.3 0.89 272 Unnamed Creek 6 20-Sep-10 BPEF WHSC J IM U 94 12.5 1.50 273 Hay Lake 7 15-May-10 GN NRPK A MA U 452 - - 274 Hay Lake 7 15-May-10 GN NRPK A MA U 437 - - 275 Hay Lake 7 15-May-10 GN NRPK A MA U 454 - - 276 Hay Lake 7 15-May-10 GN NRPK U UN U 387 - - 277 Hay Lake 7 15-May-10 GN NRPK U UN U 327 - - 278 Hay Lake 7 15-May-10 GN NRPK U UN U 362 - - 279 Hay Lake 7 15-May-10 GN NRPK A MA U 507 - - 280 Hay Lake 7 15-May-10 GN NRPK A MA U 402 - - 281 Hay Lake 7 15-May-10 GN NRPK A MA U 439 - - 282 Hay Lake 7 15-May-10 GN NRPK A MA U 462 - - 283 Hay Lake 7 15-May-10 GN NRPK A MA U 505 - - 284 Hay Lake 7 15-May-10 GN NRPK A MA U 509 - - 285 Hay Lake 7 15-May-10 GN NRPK U UN U 389 - - 286 Hay Lake 7 15-May-10 GN NRPK A MA U 483 - - 287 Hay Lake 7 15-May-10 GN NRPK A MA U 475 - - 288 Hay Lake 7 15-May-10 GN NRPK A MA U 506 - - 289 Hay Lake 7 15-May-10 GN NRPK A MA U 510 - - 290 Hay Lake 7 15-May-10 GN NRPK A MA U 402 - - 291 Hay Lake 7 15-May-10 GN NRPK A MA U 476 - - 292 Hay Lake 7 15-May-10 GN NRPK A MA U 522 - - 293 Hay Lake 7 15-May-10 GN NRPK A MA U 426 - - 294 Hay Lake 7 15-May-10 GN NRPK A MA U 470 - - 295 Hay Lake 7 15-May-10 GN NRPK U UN U 377 - - 296 Hay Lake 7 15-May-10 GN NRPK A MA U 515 - - 297 Hay Lake 7 15-May-10 GN NRPK U UN U 389 - - 298 Hay Lake 7 15-May-10 GN NRPK A MA U 482 - - 299 Hay Lake 7 15-May-10 GN NRPK A MA U 503 - - 300 Hay Lake 7 15-May-10 GN NRPK A MA U 444 - - 301 Hay Lake 7 15-May-10 GN NRPK A MA U 410 - - 302 Hay Lake 7 15-May-10 GN NRPK U UN F 395 - -




303 Hay Lake 7 15-May-10 GN NRPK A MA U 412 - - 304 Hay Lake 7 15-May-10 GN NRPK U UN U 360 - - 305 Hay Lake 7 15-May-10 GN NRPK U UN U 385 - - 306 Hay Lake 7 15-May-10 GN NRPK U UN U 310 - - 307 Hay Lake 7 15-May-10 GN NRPK A MA U 532 - - 308 Hay Lake 7 15-May-10 GN NRPK A MA U 471 - - 309 Hay Lake 7 15-May-10 GN NRPK A MA U 426 - - 310 Hay Lake 7 15-May-10 GN NRPK A MA F 424 - - 311 Hay Lake 7 15-May-10 GN NRPK A MA U 528 - - 312 Hay Lake 7 15-May-10 GN NRPK A MA U 426 - - 313 Hay Lake 7 15-May-10 GN NRPK U UN M 338 - - 314 Hay Lake 7 15-May-10 GN NRPK U UN U 335 - - 315 Hay Lake 7 30-Jul-10 GN WHSC J IM U 260 - - 316 Hay Lake 7 30-Jul-10 GN NRPK U UN U 485 - - 317 Hay Lake 7 30-Jul-10 GN NRPK U UN U 391 - - 318 Hay Lake 7 30-Jul-10 GN NRPK U UN U 580 - - 319 Hay Lake 7 30-Jul-10 GN NRPK U UN U 310 - - 320 Hay Lake 7 30-Jul-10 GN NRPK U UN U 563 - - 321 Hay Lake 7 30-Jul-10 GN NRPK U UN U 470 - - 322 Hay Lake 7 30-Jul-10 GN NRPK U UN M 490 - - 323 Hay Lake 7 30-Jul-10 GN NRPK U UN M 475 - - 324 Hay Lake 7 30-Jul-10 GN NRPK U UN M 402 - - 325 Hay Lake 7 30-Jul-10 GN NRPK U UN F 500 - - 326 Hay Lake 7 30-Jul-10 GN NRPK U UN M 479 - - 327 Hay Lake 7 30-Jul-10 GN NRPK U UN F 471 - - 328 Hay Lake 7 30-Jul-10 GN NRPK U UN F 458 - - 329 Hay Lake 7 30-Jul-10 GN NRPK U UN M 387 - - 330 Hay Lake 7 30-Jul-10 GN NRPK U UN M 403 - - 331 Hay Lake 7 30-Jul-10 GN NRPK U UN F 404 - - 332 Hay Lake 7 31-Jul-10 BEF NRPK A MA U 545 - - 333 Hay Lake 7 19-Sep-10 BEF NRPK A MA U 496 - - 334 Hay Lake 7 19-Sep-10 BEF NRPK A MA U 438 - - 335 Hay Lake 7 19-Sep-10 BEF NRPK A MA U 450 - - 336 Hay Lake 7 19-Sep-10 BEF NRPK A MA U 409 - - 337 Hay Lake 7 19-Sep-10 GN NRPK A MA U 457 - - 338 Hay Lake 7 19-Sep-10 GN NRPK A MA U 405 - - 339 Hay Lake 7 19-Sep-10 GN NRPK A MA U 454 - - 340 Hay Lake 7 19-Sep-10 GN NRPK A MA U 498 - -




341 Hay Lake 7 19-Sep-10 GN NRPK A MA U 506 - - 342 Unnamed Creek 8 14-May-10 MT WHSC J IM U 68 - - 343 Unnamed Creek 8 14-May-10 MT BRST U UN U 59 - - 344 Unnamed Creek 8 14-May-10 MT WHSC J IM U 62 - - 345 Unnamed Creek 8 14-May-10 MT BRST U UN U 56 - - 346 Unnamed Creek 8 14-May-10 MT WHSC J IM U 60 - - 347 Unnamed Creek 8 14-May-10 MT WHSC J IM U 65 - - 348 Unnamed Creek 8 14-May-10 MT BRST U UN U 72 - - 349 Unnamed Creek 8 14-May-10 MT BRST U UN U 54 - - 350 Unnamed Creek 8 14-May-10 MT BRST U UN U 51 - - 351 Unnamed Creek 8 21-Sep-10 MT BRST A MA U 59 - - 352 Kirby Lake 9 14-May-10 MT YLPR J IM U 128 - - 353 Kirby Lake 9 14-May-10 MT YLPR J IM U 109 - - 354 Kirby Lake 9 14-May-10 MT YLPR J IM U 103 - - 355 Kirby Lake 9 14-May-10 MT YLPR J IM U 119 - - 356 Kirby Lake 9 14-May-10 MT YLPR J IM U 105 - - 357 Kirby Lake 9 14-May-10 MT YLPR J IM U 118 - - 358 Kirby Lake 9 14-May-10 MT YLPR J IM U 112 - - 359 Kirby Lake 9 14-May-10 MT YLPR J IM U 102 - - 360 Kirby Lake 9 14-May-10 MT YLPR J IM U 124 - - 361 Kirby Lake 9 14-May-10 MT YLPR J IM U 131 - - 362 Kirby Lake 9 14-May-10 MT YLPR J IM U 115 - - 363 Kirby Lake 9 14-May-10 MT YLPR J IM U 105 - - 364 Kirby Lake 9 14-May-10 MT YLPR J IM U 130 - - 365 Kirby Lake 9 14-May-10 MT YLPR J IM U 117 - - 366 Kirby Lake 9 14-May-10 MT YLPR J IM U 112 - - 367 Kirby Lake 9 14-May-10 MT YLPR J IM U 120 - - 368 Kirby Lake 9 14-May-10 MT YLPR J IM U 130 - - 369 Kirby Lake 9 14-May-10 MT YLPR J IM U 98 - - 370 Kirby Lake 9 14-May-10 MT YLPR J IM U 123 - - 371 Kirby Lake 9 14-May-10 MT YLPR J IM U 120 - - 372 Kirby Lake 9 14-May-10 MT YLPR J IM U 125 - - 373 Kirby Lake 9 14-May-10 MT YLPR J IM U 115 - - 374 Kirby Lake 9 14-May-10 MT YLPR J IM U 95 - - 375 Kirby Lake 9 14-May-10 MT YLPR J IM U 114 - - 376 Kirby Lake 9 14-May-10 MT YLPR J IM U 92 - - 377 Kirby Lake 9 14-May-10 MT YLPR J IM U 90 - - 378 Kirby Lake 9 14-May-10 MT YLPR J IM U 116 - -




379 Kirby Lake 9 14-May-10 MT YLPR J IM U 94 - - 380 Kirby Lake 9 14-May-10 MT YLPR J IM U 97 - - 381 Kirby Lake 9 1-Aug-10 BEF YLPR J IM U 105 - - 382 Kirby Lake 9 1-Aug-10 BEF YLPR J IM U 132 - - 383 Kirby Lake 9 1-Aug-10 BEF YLPR J IM U 203 - - 384 Kirby Lake 9 1-Aug-10 BEF YLPR J IM U 120 - - 385 Kirby Lake 9 1-Aug-10 BEF YLPR J IM U 94 - - 386 Kirby Lake 9 1-Aug-10 MT YLPR J IM U 90 8.0 1.10 387 Kirby Lake 9 1-Aug-10 MT YLPR J IM U 112 16.0 1.14 388 Kirby Lake 9 1-Aug-10 MT YLPR J IM U 95 12.0 1.40 389 Kirby Lake 9 1-Aug-10 MT YLPR J IM U 91 10.0 1.33 390 Kirby Lake 9 1-Aug-10 MT YLPR J IM U 115 16.0 1.05 391 Kirby Lake 9 1-Aug-10 MT YLPR J IM U 123 21.0 1.13 392 Kirby Lake 9 1-Aug-10 MT YLPR J IM U 81 6.0 1.13 393 Kirby Lake 9 1-Aug-10 MT YLPR J IM U 106 14.0 1.18 394 Kirby Lake 9 1-Aug-10 MT YLPR J IM U 91 8.0 1.06 395 Kirby Lake 9 1-Aug-10 MT YLPR J IM U 95 10.0 1.17 396 Kirby Lake 9 1-Aug-10 MT YLPR J IM U 85 6.0 0.98 397 Kirby Lake 9 1-Aug-10 MT YLPR J IM U 84 6.0 1.01 398 Kirby Lake 9 1-Aug-10 MT YLPR J IM U 80 6.0 1.17 399 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 150 - - 400 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 169 - - 401 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 170 - - 402 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 175 - - 403 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 102 - - 404 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 150 - - 405 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 174 - - 406 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 154 - - 407 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 98 - - 408 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 190 - - 409 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 168 - - 410 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 114 - - 411 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 141 - - 412 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 100 - - 413 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 97 - - 414 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 146 - - 415 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 119 - - 416 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 160 - -




417 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 173 - - 418 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 156 - - 419 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 157 - - 420 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 154 - - 421 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 100 - - 422 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 160 - - 423 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 145 - - 424 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 155 - - 425 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 183 - - 426 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 105 - - 427 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 105 - - 428 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 142 - - 429 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 105 - - 430 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 160 - - 431 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 107 - - 432 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 111 - - 433 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 110 - - 434 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 105 - - 435 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 110 - - 436 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 115 - - 437 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 97 - - 438 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 116 - - 439 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 151 - - 440 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 105 - - 441 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 94 - - 442 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 110 - - 443 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 152 - - 444 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 148 - - 445 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 155 - - 446 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 140 - - 447 Kirby Lake 9 1-Aug-10 GN WHSC A MA U 385 - - 448 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 96 - - 449 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 164 - - 450 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 103 - - 451 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 103 - - 452 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 102 - - 453 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 150 - - 454 Kirby Lake 9 1-Aug-10 GN WHSC A MA U 410 - -




455 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 113 - - 456 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 107 - - 457 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 101 - - 458 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 114 - - 459 Kirby Lake 9 1-Aug-10 GN LKWH A MA U 495 - - 460 Kirby Lake 9 1-Aug-10 GN WHSC A MA U 372 - - 461 Kirby Lake 9 1-Aug-10 GN WHSC A MA U 425 - - 462 Kirby Lake 9 1-Aug-10 GN LKWH J IM U 240 - - 463 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 146 - - 464 Kirby Lake 9 1-Aug-10 GN LKWH U UN U 150 - - 465 Kirby Lake 9 1-Aug-10 GN LKWH U UN U 210 - - 466 Kirby Lake 9 1-Aug-10 GN LKWH U UN U 163 - - 467 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 165 - - 468 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 157 - - 469 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 165 - - 470 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 185 - - 471 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 174 - - 472 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 157 - - 473 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 153 - - 474 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 103 - - 475 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 160 - - 476 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 151 - - 477 Kirby Lake 9 1-Aug-10 GN LKWH U UN U 204 - - 478 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 152 - - 479 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 165 - - 480 Kirby Lake 9 1-Aug-10 GN WHSC A MA U 375 - - 481 Kirby Lake 9 1-Aug-10 GN WHSC A MA U 395 - - 482 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 105 - - 483 Kirby Lake 9 1-Aug-10 GN LKWH U UN U 315 - - 484 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 100 - - 485 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 110 - - 486 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 105 - - 487 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 119 - - 488 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 110 - - 489 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 105 - - 490 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 112 - - 491 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 100 - - 492 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 115 - -




493 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 98 - - 494 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 175 - - 495 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 110 - - 496 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 110 - - 497 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 112 - - 498 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 105 - - 499 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 150 - - 500 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 109 - - 501 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 100 - - 502 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 112 - - 503 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 112 - - 504 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 112 - - 505 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 170 - - 506 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 105 - - 507 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 110 - - 508 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 118 - - 509 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 121 - - 510 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 110 - - 511 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 110 - - 512 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 103 - - 513 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 102 - - 514 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 107 - - 515 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 98 - - 516 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 115 - - 517 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 113 - - 518 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 114 - - 519 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 115 - - 520 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 105 - - 521 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 110 - - 522 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 105 - - 523 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 98 - - 524 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 109 - - 525 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 116 - - 526 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 103 - - 527 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 110 - - 528 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 110 - - 529 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 101 - - 530 Kirby Lake 9 1-Aug-10 GN YLPR U UN U 59 - -




531 Kirby Lake 9 18-Sep-10 BEF YLPR J IM U 41 0.6 0.87 532 Kirby Lake 9 18-Sep-10 BEF WHSC J IM U 59 2.0 0.97 533 Kirby Lake 9 18-Sep-10 BEF WHSC J IM U 64 2.7 1.03 534 Kirby Lake 9 18-Sep-10 BEF YLPR J IM U 35 0.9 2.10 535 Kirby Lake 9 18-Sep-10 BEF WHSC J IM U 61 2.5 1.10 536 Kirby Lake 9 18-Sep-10 BEF WHSC J IM U 58 2.1 1.08 537 Kirby Lake 9 18-Sep-10 BEF YLPR J IM U 35 0.7 1.63 538 Kirby Lake 9 18-Sep-10 BEF YLPR J IM U 36 0.6 1.29 539 Kirby Lake 9 18-Sep-10 BEF YLPR J IM U 36 0.6 1.29 540 Kirby Lake 9 18-Sep-10 BEF YLPR J IM U 41 0.8 1.16 541 Kirby Lake 9 18-Sep-10 BEF WHSC J IM U 57 1.7 0.92 542 Kirby Lake 9 18-Sep-10 BEF YLPR J IM U 31 0.5 1.68 543 Kirby Lake 9 18-Sep-10 BEF YLPR J IM U 41 0.8 1.16 544 Kirby Lake 9 18-Sep-10 BEF YLPR J IM U 40 0.8 1.25 545 Kirby Lake 9 18-Sep-10 BEF YLPR J IM U 36 0.8 1.71 546 Kirby Lake 9 18-Sep-10 BEF YLPR J IM U 37 0.7 1.38 547 Kirby Lake 9 18-Sep-10 BEF YLPR J IM U 42 0.7 0.94 548 Kirby Lake 9 18-Sep-10 BEF YLPR A MA U 161 42.9 1.03 549 Kirby Lake 9 18-Sep-10 GN NRPK A MA U 730 - - 550 Kirby Lake 9 18-Sep-10 GN NRPK A MA U 692 - - 551 Kirby Lake 9 18-Sep-10 GN LKWH U UN U 193 - - 552 Kirby Lake 9 18-Sep-10 GN NRPK A MA U 791 - - 553 Kirby Lake 9 18-Sep-10 GN LKWH A MA U 475 - - 554 Kirby Lake 9 18-Sep-10 GN LKWH A MA U 460 - - 555 Kirby Lake 9 18-Sep-10 GN LKWH A MA U 465 - - 556 Kirby Lake 9 18-Sep-10 GN LKWH A MA U 292 - - 557 Kirby Lake 9 18-Sep-10 GN LKWH A MA U 380 - - 558 Kirby Lake 9 18-Sep-10 GN LKWH A MA U 305 - - 559 Kirby Lake 9 18-Sep-10 GN LKWH A MA U 471 - - 560 Kirby Lake 9 18-Sep-10 GN LKWH A MA U 251 - - 561 Kirby Lake 9 18-Sep-10 GN LKWH A MA U 275 - - 562 Kirby Lake 9 18-Sep-10 GN LKWH A MA U 447 - - 563 Kirby Lake 9 18-Sep-10 GN NRPK A MA U 521 - - 564 Kirby Lake 9 18-Sep-10 GN NRPK A MA U 592 - - 565 Kirby Lake 9 18-Sep-10 GN NRPK A MA U 810 - - 566 Kirby Lake 9 18-Sep-10 GN LKWH A MA U 541 - - 567 Kirby Lake 9 18-Sep-10 GN LKWH J IM U 103 - - 568 Kirby Lake 9 18-Sep-10 GN LKWH A MA U 289 - -




569 Kirby Lake 9 18-Sep-10 GN NRPK A MA U 587 - - 570 Kirby Lake 9 18-Sep-10 GN NRPK A MA U 870 - - 571 Unnamed Creek 11 18-May-10 MT BRST U UN U 61 - - 572 Unnamed Lake 12 18-May-10 GN NRPK A MA U 860 - - 573 Unnamed Lake 12 18-May-10 GN LNSC A MA M 440 - - 574 Unnamed Lake 12 18-May-10 GN LNSC A MA M 480 - - 575 Unnamed Lake 12 18-May-10 GN LNSC A MA F 465 - - 576 Unnamed Lake 12 18-May-10 GN LNSC A MA F 502 - - 577 Unnamed Lake 12 18-May-10 GN LNSC A MA U 415 - - 578 Unnamed Lake 12 18-May-10 GN LNSC A MA M 450 - - 579 Unnamed Lake 12 18-May-10 GN LNSC A MA M 395 - - 580 Unnamed Lake 12 18-May-10 GN LNSC A MA F 480 - - 581 Unnamed Lake 12 18-May-10 GN LNSC A MA M 445 - - 582 Unnamed Lake 12 19-May-10 GN LNSC A MA U 410 - - 583 Unnamed Lake 12 19-May-10 GN NRPK A MA U 610 - - 584 Unnamed Lake 12 19-May-10 GN LNSC A MA U 398 - - 585 Unnamed Lake 12 19-May-10 GN LNSC A MA U 305 - - 586 Unnamed Lake 12 19-May-10 GN LNSC A MA U 455 - - 587 Unnamed Lake 12 19-May-10 GN NRPK U UN U 359 - - 588 Unnamed Lake 12 19-May-10 GN LNSC A MA U 501 - - 589 Unnamed Lake 12 19-May-10 GN NRPK U UN U 346 - - 590 Unnamed Lake 12 19-May-10 GN NRPK A MA F 742 - - 591 Unnamed Lake 12 19-May-10 GN LNSC A MA U 490 - - 592 Unnamed Lake 12 19-May-10 GN LNSC A MA M 427 - - 593 Unnamed Lake 12 19-May-10 GN LNSC A MA M 458 - - 594 Unnamed Lake 12 5-Aug-10 BEF NRPK J IM U 368 - - 595 Unnamed Lake 12 5-Aug-10 BEF NRPK J IM U 320 - - 596 Unnamed Lake 12 5-Aug-10 BEF NRPK J IM U 375 - - 597 Unnamed Lake 12 5-Aug-10 BEF NRPK J IM U 378 - - 598 Unnamed Lake 12 5-Aug-10 BEF NRPK J IM U 360 - - 599 Unnamed Lake 12 5-Aug-10 MT NRPK J IM U 115 8.8 0.58 600 Unnamed Lake 12 5-Aug-10 GN NRPK J IM U 475 - - 601 Unnamed Lake 12 5-Aug-10 GN WHSC A MA U 440 - - 602 Unnamed Lake 12 5-Aug-10 GN WHSC A MA U 465 - - 603 Unnamed Lake 12 5-Aug-10 GN WHSC A MA U 363 - - 604 Unnamed Lake 12 15-Sep-10 GN WHSC A MA U 430 - - 605 Unnamed Lake 12 15-Sep-10 GN WHSC A MA U 415 - - 606 Unnamed Lake 12 15-Sep-10 GN WHSC A MA U 309 - -




607 Unnamed Lake 12 15-Sep-10 GN WHSC A MA U 425 - - 608 Unnamed Lake 12 15-Sep-10 GN WHSC A MA U 444 - - 609 Unnamed Lake 12 15-Sep-10 GN WHSC A MA U 419 - - 610 Unnamed Lake 12 15-Sep-10 GN WHSC A MA U 345 - - 611 Unnamed Lake 12 15-Sep-10 GN WHSC A MA U 425 - - 612 Unnamed Lake 12 15-Sep-10 GN WHSC A MA U 325 - - 613 Unnamed Lake 12 15-Sep-10 GN WHSC A MA U 393 - - 614 Unnamed Lake 12 15-Sep-10 GN WHSC A MA U 410 - - 615 Unnamed Lake 12 15-Sep-10 GN WHSC A MA U 400 - - 616 Unnamed River 13 18-May-10 MT BRST U UN U 52 0.3 0.21 617 Unnamed River 13 18-May-10 MT BRST U UN U 62 2.0 0.84 618 Unnamed River 13 18-May-10 MT BRST U UN U 50 0.5 0.40 619 Unnamed River 13 18-May-10 MT BRST U UN U 60 1.0 0.46 620 Unnamed River 13 18-May-10 MT BRST U UN U 60 1.0 0.46 621 Unnamed River 13 18-May-10 MT BRST U UN U 58 0.8 0.41 622 Unnamed River 13 18-May-10 MT BRST U UN U 52 0.5 0.36 623 Unnamed River 13 18-May-10 MT BRST U UN U 52 1.0 0.71 624 Unnamed River 13 18-May-10 MT BRST U UN U 66 1.0 0.35 625 Unnamed River 13 18-May-10 MT BRST U UN U 55 0.5 0.30 626 Unnamed River 13 18-May-10 MT BRST U UN U 50 1.0 0.80 627 Unnamed River 13 18-May-10 MT BRST U UN U 50 1.0 0.80 628 Unnamed River 13 18-May-10 MT BRST U UN U 55 1.0 0.60 629 Unnamed River 13 18-May-10 MT BRST U UN U 57 0.8 0.43 630 Unnamed River 13 18-May-10 MT BRST U UN U 62 0.8 0.34 631 Unnamed River 13 18-May-10 MT BRST U UN U 52 0.8 0.57 632 Unnamed River 13 18-May-10 MT BRST U UN U 57 0.7 0.38 633 Unnamed River 13 18-May-10 MT BRST U UN U 46 0.3 0.31 634 Unnamed River 13 18-May-10 MT BRST U UN U 60 1.0 0.46 635 Unnamed River 13 18-May-10 MT BRST U UN U 55 0.5 0.30 636 Unnamed River 13 18-May-10 MT BRST U UN U 60 1.0 0.46 637 Unnamed River 13 18-May-10 MT BRST U UN U 62 1.0 0.42 638 Unnamed River 13 18-May-10 MT BRST U UN U 55 0.8 0.48 639 Unnamed River 13 18-May-10 MT BRST U UN U 55 0.4 0.24 640 Unnamed River 13 18-May-10 MT BRST U UN U 58 0.7 0.36 641 Unnamed River 13 18-May-10 MT BRST U UN U 55 1.0 0.60 642 Unnamed River 13 18-May-10 MT BRST U UN U 46 0.4 0.41 643 Unnamed River 13 18-May-10 MT BRST U UN U 58 1.0 0.51 644 Unnamed River 13 18-May-10 MT BRST U UN U 60 2.0 0.93




645 Unnamed River 13 18-May-10 MT BRST U UN U 63 1.0 0.40 646 Unnamed River 13 18-May-10 MT BRST U UN U 65 1.0 0.36 647 Unnamed River 13 18-May-10 MT BRST U UN U 50 0.4 0.32 648 Unnamed River 13 18-May-10 MT BRST U UN U 60 1.0 0.46 649 Unnamed River 13 18-May-10 MT BRST U UN U 59 0.8 0.39 650 Unnamed River 13 18-May-10 MT BRST U UN U 55 1.0 0.60 651 Unnamed River 13 18-May-10 MT BRST U UN U 58 0.8 0.41 652 Unnamed River 13 18-May-10 MT BRST U UN U 52 0.5 0.36 653 Unnamed River 13 18-May-10 MT BRST U UN U 55 1.0 0.60 654 Unnamed River 13 18-May-10 MT BRST U UN U 50 0.4 0.32 655 Unnamed River 13 18-May-10 MT BRST U UN U 48 0.3 0.27 656 Unnamed River 13 18-May-10 MT BRST U UN U 60 1.0 0.46 657 Unnamed River 13 18-May-10 MT BRST U UN U 48 0.6 0.54 658 Unnamed River 13 18-May-10 MT BRST U UN U 42 0.2 0.27 659 Unnamed River 13 18-May-10 MT BRST U UN U 51 0.7 0.53 660 Unnamed River 13 18-May-10 MT BRST U UN U 58 0.8 0.41 661 Unnamed River 13 18-May-10 MT BRST U UN U 55 0.7 0.42 662 Unnamed River 13 18-May-10 MT BRST U UN U 53 0.5 0.34 663 Unnamed River 13 18-May-10 MT BRST U UN U 60 1.0 0.46 664 Unnamed River 13 18-May-10 MT BRST U UN U 55 0.5 0.30 665 Unnamed River 13 18-May-10 MT BRST U UN U 70 2.0 0.58 666 Unnamed River 13 18-May-10 MT BRST U UN U 60 1.0 0.46 667 Unnamed River 13 18-May-10 MT BRST U UN U 60 0.7 0.32 668 Unnamed River 13 18-May-10 MT BRST U UN U 60 1.0 0.46 669 Unnamed River 13 18-May-10 MT BRST U UN U 52 0.6 0.43 670 Unnamed River 13 18-May-10 MT BRST U UN U 50 0.4 0.32 671 Unnamed River 13 18-May-10 MT BRST U UN U 65 1.0 0.36 672 Unnamed River 13 18-May-10 MT BRST U UN U 56 1.0 0.57 673 Unnamed River 13 18-May-10 MT BRST U UN U 61 1.0 0.44 674 Unnamed River 13 18-May-10 MT BRST U UN U - - - 675 Unnamed River 13 18-May-10 MT BRST U UN U - - - 676 Unnamed River 13 18-May-10 MT BRST U UN U - - - 677 Unnamed River 13 18-May-10 MT BRST U UN U - - - 678 Unnamed River 13 18-May-10 MT BRST U UN U - - - 679 Unnamed River 13 18-May-10 MT BRST U UN U - - - 680 Unnamed River 13 18-May-10 MT BRST U UN U - - - 681 Unnamed River 13 18-May-10 MT BRST U UN U - - - 682 Unnamed River 13 18-May-10 MT BRST U UN U - - -




683 Unnamed River 13 18-May-10 MT BRST U UN U - - - 684 Unnamed River 13 18-May-10 MT BRST U UN U - - - 685 Unnamed River 13 18-May-10 MT BRST U UN U - - - 686 Unnamed River 13 18-May-10 MT BRST U UN U - - - 687 Unnamed River 13 18-May-10 MT BRST U UN U - - - 688 Unnamed River 13 18-May-10 MT BRST U UN U - - - 689 Unnamed River 13 18-May-10 MT BRST U UN U - - - 690 Unnamed River 13 18-May-10 MT BRST U UN U - - - 691 Unnamed River 13 18-May-10 MT BRST U UN U - - - 692 Unnamed River 13 18-May-10 MT BRST U UN U - - - 693 Unnamed River 13 18-May-10 MT BRST U UN U - - - 694 Unnamed River 13 18-May-10 MT BRST U UN U - - - 695 Unnamed River 13 18-May-10 MT BRST U UN U - - - 696 Unnamed River 13 18-May-10 MT BRST U UN U - - - 697 Unnamed River 13 18-May-10 MT BRST U UN U - - - 698 Unnamed River 13 18-May-10 MT BRST U UN U - - - 699 Unnamed River 13 18-May-10 MT BRST U UN U - - - 700 Unnamed River 13 18-May-10 MT BRST U UN U - - - 701 Unnamed River 13 18-May-10 MT BRST U UN U - - - 702 Unnamed River 13 18-May-10 MT BRST U UN U - - - 703 Unnamed River 13 18-May-10 MT BRST U UN U - - - 704 Unnamed River 13 18-May-10 MT BRST U UN U - - - 705 Unnamed River 13 18-May-10 MT BRST U UN U - - - 706 Unnamed River 13 18-May-10 MT BRST U UN U - - - 707 Unnamed River 13 18-May-10 MT BRST U UN U - - - 708 Unnamed River 13 18-May-10 MT BRST U UN U - - - 709 Unnamed River 13 18-May-10 MT BRST U UN U - - - 710 Unnamed River 13 18-May-10 MT BRST U UN U - - - 711 Unnamed River 13 18-May-10 MT BRST U UN U - - - 712 Unnamed River 13 18-May-10 MT BRST U UN U - - - 713 Unnamed River 13 18-May-10 MT BRST U UN U - - - 714 Unnamed River 13 18-May-10 MT BRST U UN U - - - 715 Unnamed River 13 18-May-10 MT BRST U UN U - - - 716 Unnamed River 13 18-May-10 MT BRST U UN U - - - 717 Unnamed River 13 18-May-10 MT BRST U UN U - - - 718 Unnamed River 13 18-May-10 MT BRST U UN U - - - 719 Unnamed River 13 18-May-10 MT BRST U UN U - - - 720 Unnamed River 13 18-May-10 MT BRST U UN U - - -




797 Unnamed River 13 18-May-10 MT BRST U UN U - - - 798 Unnamed River 13 18-May-10 MT BRST U UN U - - - 799 Unnamed River 13 18-May-10 MT BRST U UN U - - - 800 Unnamed River 13 18-May-10 MT BRST U UN U - - - 801 Unnamed River 13 18-May-10 MT BRST U UN U - - - 802 Unnamed River 13 18-May-10 MT BRST U UN U - - - 803 Unnamed River 13 18-May-10 MT BRST U UN U - - - 804 Unnamed River 13 18-May-10 MT BRST U UN U - - - 805 Unnamed River 13 18-May-10 MT BRST U UN U - - - 806 Unnamed River 13 18-May-10 MT BRST U UN U - - - 807 Unnamed River 13 18-May-10 MT BRST U UN U - - - 808 Unnamed River 13 18-May-10 MT BRST U UN U - - - 809 Unnamed River 13 18-May-10 MT BRST U UN U - - - 810 Unnamed River 13 18-May-10 MT BRST U UN U - - - 811 Unnamed River 13 18-May-10 MT BRST U UN U - - - 812 Unnamed River 13 18-May-10 MT BRST U UN U - - - 813 Unnamed River 13 18-May-10 MT BRST U UN U - - - 814 Unnamed River 13 18-May-10 MT BRST U UN U - - - 815 Unnamed River 13 18-May-10 MT BRST U UN U - - - 816 Unnamed River 13 18-May-10 MT BRST U UN U - - - 817 Unnamed River 13 18-May-10 MT BRST U UN U - - - 818 Unnamed River 13 18-May-10 MT BRST U UN U - - - 819 Unnamed River 13 18-May-10 MT BRST U UN U - - - 820 Unnamed River 13 18-May-10 MT BRST U UN U - - - 821 Unnamed River 13 18-May-10 MT BRST U UN U - - - 822 Unnamed River 13 18-May-10 MT BRST U UN U - - - 823 Unnamed River 13 18-Sep-10 BPEF BRST J IM U 36 - - 824 Unnamed River 13 18-Sep-10 BPEF WHSC J IM U 46 - - 825 Unnamed River 13 19-Sep-10 MT FNDC J IM U 48 - - 826 Unnamed River 13 19-Sep-10 MT BRST U UN U 55 - - 827 Unnamed River 13 19-Sep-10 MT FNDC J IM U 50 - - 828 Unnamed River 13 19-Sep-10 MT BRST U UN U 50 - - 829 Unnamed River 13 19-Sep-10 MT BRST U UN U 51 - - 830 Unnamed River 13 19-Sep-10 MT WHSC J IM U 50 - - 831 Unnamed River 13 19-Sep-10 MT FNDC J IM U 49 - - 832 Unnamed River 13 19-Sep-10 MT BRST U UN U 50 - - 833 Unnamed River 13 19-Sep-10 MT BRST A MA U 59 - - 834 Unnamed River 13 19-Sep-10 MT WHSC J IM U 48 - -




835 Unnamed River 13 19-Sep-10 MT BRST A MA U 65 - - 836 Unnamed River 13 19-Sep-10 MT BRST A MA U 60 - - 837 Unnamed River 13 19-Sep-10 MT BRST A MA U 65 - - 838 Unnamed River 13 19-Sep-10 MT BRST J IM U 40 - - 839 Unnamed River 13 19-Sep-10 MT BRST A MA U 60 - - 840 Unnamed River 13 19-Sep-10 MT FNDC J IM U 45 - - 841 Unnamed River 13 19-Sep-10 MT FNDC J IM U 47 - - 842 Unnamed River 13 19-Sep-10 MT FNDC J IM U 49 - - 843 Unnamed River 13 19-Sep-10 MT BRST J IM U 57 - - 844 Unnamed River 13 19-Sep-10 MT WHSC J IM U 46 - - 845 Unnamed River 13 19-Sep-10 MT FNDC J IM U 47 - - 846 Unnamed River 13 19-Sep-10 MT BRST J IM U 49 - - 847 Unnamed River 13 19-Sep-10 MT WHSC J IM U 46 - - 848 Unnamed River 13 19-Sep-10 MT BRST J IM U 54 - - 849 Unnamed Creek 16 19-May-10 MT FNDC A MA U 75 4.0 0.95 850 Unnamed Creek 16 19-May-10 MT FNDC A MA U 75 4.0 0.95 851 Unnamed Creek 16 19-May-10 MT FNDC A MA U 70 3.0 0.87 852 Unnamed Creek 16 19-May-10 MT FTMN J IM U 50 0.3 0.24 853 Unnamed Creek 16 19-May-10 MT FNDC A MA U 76 5.0 1.14 854 Unnamed Creek 16 19-May-10 MT FNDC A MA U 65 3.0 1.09 855 Unnamed Creek 16 19-May-10 MT FNDC A MA U 75 5.0 1.19 856 Unnamed Creek 16 19-May-10 MT FNDC A MA U 76 5.0 1.14 857 Unnamed Creek 16 19-May-10 MT BRST U UN U 55 1.0 0.60 858 Unnamed Creek 16 19-May-10 MT FTMN U UN U 45 0.3 0.33 859 Unnamed Creek 16 19-May-10 MT FNDC A MA U 71 3.0 0.84 860 Unnamed Creek 16 19-May-10 MT FNDC A MA U 65 2.0 0.73 861 Unnamed Creek 16 19-May-10 MT FNDC J IM U 51 0.4 0.30 862 Unnamed Creek 16 19-May-10 MT FNDC A MA U 65 2.0 0.73 863 Unnamed Creek 16 19-May-10 MT FNDC A MA U 65 3.0 1.09 864 Unnamed Creek 16 19-May-10 MT FTMN J IM U 48 0.3 0.27 865 Unnamed Creek 16 19-May-10 MT FNDC A MA U 74 5.0 1.23 866 Unnamed Creek 16 19-May-10 MT FNDC A MA U 65 5.0 1.82 867 Unnamed Creek 16 19-May-10 MT BRST J IM U 50 0.4 0.32 868 Unnamed Creek 16 19-May-10 MT PRDC A MA U 61 2.0 0.88 869 Unnamed Creek 16 19-May-10 MT PRDC A MA U 70 4.0 1.17 870 Unnamed Creek 16 19-May-10 MT PRDC A MA U 68 3.0 0.95 871 Unnamed Creek 16 19-May-10 MT FTMN J IM U 56 2.0 1.14 872 Unnamed Creek 16 19-May-10 MT PRDC J IM U 48 0.4 0.36




873 Unnamed Creek 16 19-May-10 MT BRST U UN U 58 1.0 0.51 874 Unnamed Creek 16 19-May-10 MT FNDC A MA U 68 3.0 0.95 875 Unnamed Creek 16 19-May-10 MT PRDC A MA U 65 2.0 0.73 876 Unnamed Creek 16 19-May-10 MT FNDC A MA U 81 6.0 1.13 877 Unnamed Creek 16 19-May-10 MT FNDC J IM U 54 0.4 0.25 878 Unnamed Creek 16 19-May-10 MT FTMN U UN U 49 1.0 0.85 879 Unnamed Creek 16 19-May-10 MT FNDC J IM U 56 0.5 0.28 880 Unnamed Creek 16 19-May-10 MT PRDC J IM U 49 0.2 0.17 881 Unnamed Creek 16 19-May-10 MT FNDC A MA U 60 2.0 0.93 882 Unnamed Creek 16 19-May-10 MT FNDC A MA U 75 6.0 1.42 883 Unnamed Creek 16 19-May-10 MT FNDC A MA U 61 1.0 0.44 884 Unnamed Creek 16 19-May-10 MT PRDC J IM U 50 0.5 0.40 885 Unnamed Creek 16 19-May-10 MT FNDC A MA U 70 5.0 1.46 886 Unnamed Creek 16 19-May-10 MT FNDC J IM U 50 0.4 0.32 887 Unnamed Creek 16 19-May-10 MT FNDC J IM U 54 0.4 0.25 888 Unnamed Creek 16 19-May-10 MT FNDC A MA U 77 6.0 1.31 889 Unnamed Creek 16 19-May-10 MT FTMN J IM U 48 0.3 0.27 890 Unnamed Creek 16 19-May-10 MT FNDC A MA U 65 2.0 0.73 891 Unnamed Creek 16 19-May-10 MT FNDC A MA U 70 4.0 1.17 892 Unnamed Creek 16 19-May-10 MT BRST U UN U 45 0.3 0.33 893 Unnamed Creek 16 19-May-10 MT PRDC J IM U 53 0.3 0.20 894 Unnamed Creek 16 19-May-10 MT FNDC J IM U 53 1.0 0.67 895 Unnamed Creek 16 19-May-10 MT FNDC A MA U 67 4.0 1.33 896 Unnamed Creek 16 19-May-10 MT FNDC A MA U 64 4.0 1.53 897 Unnamed Creek 16 19-May-10 MT FTMN J IM U 54 2.0 1.27 898 Unnamed Creek 16 19-May-10 MT FNDC J IM U 50 0.4 0.32 899 Unnamed Creek 16 19-May-10 MT FNDC J IM U 50 0.4 0.32 900 Unnamed Creek 16 19-May-10 MT FNDC J IM U 50 0.3 0.24 901 Unnamed Creek 16 19-May-10 MT FNDC A MA U 66 3.0 1.04 902 Unnamed Creek 16 19-May-10 MT FNDC A MA U 73 4.0 1.03 903 Unnamed Creek 16 19-May-10 MT FNDC A MA U 68 4.0 1.27 904 Unnamed Creek 16 19-May-10 MT FTMN J IM U 50 1.0 0.80 905 Unnamed Creek 16 19-May-10 MT PRDC J IM U 52 0.5 0.36 906 Unnamed Creek 16 19-May-10 MT FTMN J IM U 42 0.3 0.40 907 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 908 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 909 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 910 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - -




911 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 912 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 913 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 914 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 915 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 916 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 917 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 918 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 919 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 920 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 921 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 922 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 923 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 924 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 925 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 926 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 927 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 928 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 929 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 930 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 931 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 932 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 933 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 934 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 935 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 936 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 937 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 938 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 939 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 940 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 941 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 942 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 943 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 944 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 945 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 946 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 947 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 948 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - -




1177 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 1178 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 1179 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 1180 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 1181 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 1182 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 1183 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 1184 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 1185 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 1186 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 1187 Unnamed Creek 16 19-May-10 MT FNDC U UN U - - - 1188 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1189 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1190 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1191 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1192 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1193 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1194 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1195 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1196 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1197 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1198 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1199 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1200 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1201 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1202 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1203 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1204 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1205 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1206 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1207 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1208 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1209 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1210 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1211 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1212 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1213 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1214 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - -




1215 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1216 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1217 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1218 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1219 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1220 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1221 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1222 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1223 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1224 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1225 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1226 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1227 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1228 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1229 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1230 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1231 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1232 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1233 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1234 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1235 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1236 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1237 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1238 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1239 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1240 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1241 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1242 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1243 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1244 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1245 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1246 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1247 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1248 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1249 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1250 Unnamed Creek 16 19-May-10 MT PRDC U UN U - - - 1251 Unnamed Creek 16 19-May-10 MT BRST U UN U - - - 1252 Unnamed Creek 16 19-May-10 MT BRST U UN U - - -




1253 Unnamed Creek 16 19-May-10 MT BRST U UN U - - - 1254 Unnamed Creek 16 19-May-10 MT BRST U UN U - - - 1255 Unnamed Creek 16 19-May-10 MT BRST U UN U - - - 1256 Unnamed Creek 16 19-May-10 MT BRST U UN U - - - 1257 Unnamed Creek 16 19-May-10 MT BRST U UN U - - - 1258 Unnamed Creek 16 19-May-10 MT BRST U UN U - - - 1259 Unnamed Creek 16 19-May-10 MT BRST U UN U - - - 1260 Unnamed Creek 16 19-May-10 MT BRST U UN U - - - 1261 Unnamed Creek 16 19-May-10 MT BRST U UN U - - - 1262 Unnamed Creek 16 19-May-10 MT BRST U UN U - - - 1263 Unnamed Creek 16 19-May-10 MT BRST U UN U - - - 1264 Unnamed Creek 16 19-May-10 MT BRST U UN U - - - 1265 Unnamed Creek 16 19-May-10 MT BRST U UN U - - - 1266 Unnamed Creek 16 19-May-10 MT BRST U UN U - - - 1267 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1268 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1269 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1270 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1271 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1272 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1273 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1274 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1275 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1276 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1277 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1278 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1279 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1280 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1281 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1282 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1283 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1284 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1285 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1286 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1287 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1288 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1289 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1290 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - -




1291 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1292 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1293 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1294 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1295 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1296 Unnamed Creek 16 19-May-10 MT FTMN U UN U - - - 1297 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 38 - - 1298 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 73 - - 1299 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 28 - - 1300 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 63 - - 1301 Unnamed Creek 16 14-Sep-10 BPEF BRST U UN U 55 - - 1302 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 74 - - 1303 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 34 - - 1304 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 60 - - 1305 Unnamed Creek 16 14-Sep-10 BPEF FNDC A MA U 50 - - 1306 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U 59 - - 1307 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 31 - - 1308 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 75 - - 1309 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 26 - - 1310 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 68 - - 1311 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 34 - - 1312 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 75 - - 1313 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 28 - - 1314 Unnamed Creek 16 15-Sep-10 MT BRST A MA U 70 - - 1315 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 35 - - 1316 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 58 - - 1317 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 30 - - 1318 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U 40 - - 1319 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 32 - - 1320 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 81 - - 1321 Unnamed Creek 16 14-Sep-10 BPEF BRST J IM U 30 - - 1322 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U 53 - - 1323 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 28 - - 1324 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 62 - - 1325 Unnamed Creek 16 14-Sep-10 BPEF PRDC J IM U 26 - - 1326 Unnamed Creek 16 15-Sep-10 MT FNDC J IM U 47 - - 1327 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 31 - - 1328 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 60 - -




1329 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 32 - - 1330 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 58 - - 1331 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 34 - - 1332 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 68 - - 1333 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 38 - - 1334 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 61 - - 1335 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 37 - - 1336 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 69 - - 1337 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 25 - - 1338 Unnamed Creek 16 15-Sep-10 MT FNDC J IM U 50 - - 1339 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 29 - - 1340 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 60 - - 1341 Unnamed Creek 16 14-Sep-10 BPEF PRDC J IM U 29 - - 1342 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 60 - - 1343 Unnamed Creek 16 14-Sep-10 BPEF PRDC J IM U 25 - - 1344 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 121 - - 1345 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 26 - - 1346 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 110 - - 1347 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 26 - - 1348 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 63 - - 1349 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 27 - - 1350 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 64 - - 1351 Unnamed Creek 16 14-Sep-10 BPEF FNDC J IM U 30 - - 1352 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 85 - - 1353 Unnamed Creek 16 15-Sep-10 MT FNDC J IM U 53 - - 1354 Unnamed Creek 16 15-Sep-10 MT BRST A MA U 60 - - 1355 Unnamed Creek 16 15-Sep-10 MT FNDC J IM U 40 - - 1356 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 89 - - 1357 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 54 - - 1358 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 112 - - 1359 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 73 - - 1360 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 64 - - 1361 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U 53 - - 1362 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 70 - - 1363 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 55 - - 1364 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 68 - - 1365 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 64 - - 1366 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 62 - -




1367 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 61 - - 1368 Unnamed Creek 16 15-Sep-10 MT FNDC J IM U 56 - - 1369 Unnamed Creek 16 15-Sep-10 MT FNDC J IM U 56 - - 1370 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 66 - - 1371 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 71 - - 1372 Unnamed Creek 16 15-Sep-10 MT FNDC J IM U 52 - - 1373 Unnamed Creek 16 15-Sep-10 MT FNDC J IM U 45 - - 1374 Unnamed Creek 16 15-Sep-10 MT FNDC J IM U 51 - - 1375 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 67 - - 1376 Unnamed Creek 16 15-Sep-10 MT FNDC J IM U 54 - - 1377 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 86 - - 1378 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 65 - - 1379 Unnamed Creek 16 15-Sep-10 MT BRST J IM U 47 - - 1380 Unnamed Creek 16 15-Sep-10 MT FNDC J IM U 55 - - 1381 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 75 - - 1382 Unnamed Creek 16 15-Sep-10 MT FNDC J IM U 55 - - 1383 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U 61 - - 1384 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U 56 - - 1385 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 90 - - 1386 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 65 - - 1387 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 60 - - 1388 Unnamed Creek 16 15-Sep-10 MT FNDC J IM U 45 - - 1389 Unnamed Creek 16 15-Sep-10 MT FNDC J IM U 55 - - 1390 Unnamed Creek 16 15-Sep-10 MT FNDC J IM U 45 - - 1391 Unnamed Creek 16 15-Sep-10 MT FNDC J IM U 63 - - 1392 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 64 - - 1393 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 63 - - 1394 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 68 - - 1395 Unnamed Creek 16 15-Sep-10 MT FNDC J IM U 51 - - 1396 Unnamed Creek 16 15-Sep-10 MT FNDC A MA U 65 - - 1397 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U - - - 1398 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U - - - 1399 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U - - - 1400 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U - - - 1401 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U - - - 1402 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U - - - 1403 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U - - - 1404 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U - - -




1481 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U - - - 1482 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U - - - 1483 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U - - - 1484 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U - - - 1485 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U - - - 1486 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U - - - 1487 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U - - - 1488 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U - - - 1489 Unnamed Creek 16 15-Sep-10 MT FNDC U UN U - - - 1490 Unnamed Creek 16 15-Sep-10 MT BRST U UN U - - - 1491 Unnamed Creek 16 15-Sep-10 MT BRST U UN U - - - 1492 Unnamed Lake 17 18-May-10 MT FNDC A MA U 70 - - 1493 Unnamed Lake 17 18-May-10 MT FNDC A MA F 77 - - 1494 Unnamed Lake 17 18-May-10 MT FNDC A MA U 81 - - 1495 Unnamed Lake 17 18-May-10 MT FNDC A MA F 82 - - 1496 Unnamed Lake 17 18-May-10 MT FNDC A MA F 74 - - 1497 Unnamed Lake 17 18-May-10 MT FNDC A MA U 76 - - 1498 Unnamed Lake 17 18-May-10 MT FNDC A MA U 76 - - 1499 Unnamed Lake 17 18-May-10 MT FNDC A MA U 48 - - 1500 Unnamed Lake 17 18-May-10 MT FNDC A MA U 70 - - 1501 Unnamed Lake 17 18-May-10 MT FNDC A MA F 80 - - 1502 Unnamed Lake 17 18-May-10 MT FNDC A MA F 75 - - 1503 Unnamed Lake 17 18-May-10 MT FNDC A MA F 79 - - 1504 Unnamed Lake 17 18-May-10 MT FNDC A MA U 50 - - 1505 Unnamed Lake 17 18-May-10 MT FNDC A MA F 83 - - 1506 Unnamed Lake 17 18-May-10 MT FNDC A MA U 61 - - 1507 Unnamed Lake 17 18-May-10 MT FNDC A MA F 75 - - 1508 Unnamed Lake 17 18-May-10 MT FNDC A MA M 52 - - 1509 Unnamed Lake 17 18-May-10 MT FNDC A MA M 60 - - 1510 Unnamed Lake 17 18-May-10 MT FNDC A MA U 73 - - 1511 Unnamed Lake 17 18-May-10 MT FNDC A MA F 81 - - 1512 Unnamed Lake 17 18-May-10 MT FNDC A MA F 75 - - 1513 Unnamed Lake 17 18-May-10 MT FNDC A MA U 68 - - 1514 Unnamed Lake 17 18-May-10 MT FNDC A MA U 70 - - 1515 Unnamed Lake 17 18-May-10 MT FNDC A MA U 82 - - 1516 Unnamed Lake 17 18-May-10 MT FNDC A MA F 82 - - 1517 Unnamed Lake 17 18-May-10 MT FNDC A MA F 78 - - 1518 Unnamed Lake 17 18-May-10 MT FNDC A MA U 52 - -




1519 Unnamed Lake 17 18-May-10 MT FNDC A MA F 64 - - 1520 Unnamed Lake 17 18-May-10 MT FNDC A MA F 61 - - 1521 Unnamed Lake 17 18-May-10 MT FNDC A MA F 83 - - 1522 Unnamed Lake 17 18-May-10 MT FNDC A MA F 81 - - 1523 Unnamed Lake 17 18-May-10 MT FNDC A MA F 80 - - 1524 Unnamed Lake 17 18-May-10 MT FNDC A MA U 51 - - 1525 Unnamed Lake 17 18-May-10 MT FNDC A MA U 48 - - 1526 Unnamed Lake 17 18-May-10 MT FNDC A MA F 83 - - 1527 Unnamed Lake 17 18-May-10 MT FNDC A MA U 63 - - 1528 Unnamed Lake 17 18-May-10 MT FNDC A MA U 67 - - 1529 Unnamed Lake 17 18-May-10 MT FNDC A MA U 65 - - 1530 Unnamed Lake 17 18-May-10 MT FNDC A MA F 77 - - 1531 Unnamed Lake 17 18-May-10 MT FNDC A MA U 75 - - 1532 Unnamed Lake 17 18-May-10 MT FNDC A MA F 81 - - 1533 Unnamed Lake 17 18-May-10 MT FNDC A MA M 65 - - 1534 Unnamed Lake 17 18-May-10 MT FNDC A MA U 70 - - 1535 Unnamed Lake 17 18-May-10 MT FNDC A MA F 85 - - 1536 Unnamed Lake 17 18-May-10 MT FNDC A MA F 74 - - 1537 Unnamed Lake 17 18-May-10 MT FNDC A MA F 80 - - 1538 Unnamed Lake 17 18-May-10 MT FNDC A MA F 81 - - 1539 Unnamed Lake 17 18-May-10 MT FNDC A MA F 82 - - 1540 Unnamed Lake 17 18-May-10 MT FNDC A MA U 70 - - 1541 Unnamed Lake 17 18-May-10 MT FNDC A MA U 77 - - 1542 Unnamed Lake 17 18-May-10 MT FNDC A MA U 65 - - 1543 Unnamed Lake 17 18-May-10 MT FNDC A MA U 69 - - 1544 Unnamed Lake 17 18-May-10 MT FNDC A MA U 67 - - 1545 Unnamed Lake 17 18-May-10 MT FNDC A MA F 80 - - 1546 Unnamed Lake 17 18-May-10 MT FNDC A MA F 90 - - 1547 Unnamed Lake 17 18-May-10 MT FNDC A MA M 80 - - 1548 Unnamed Lake 17 18-May-10 MT FNDC A MA U 90 - - 1549 Unnamed Lake 17 18-May-10 MT FNDC A MA U 80 - - 1550 Unnamed Lake 17 18-May-10 MT FNDC A MA U 70 - - 1551 Unnamed Lake 17 18-May-10 MT FNDC A MA F 82 - - 1552 Unnamed Lake 17 18-May-10 MT FNDC A MA U 79 - - 1553 Unnamed Lake 17 18-May-10 MT FNDC A MA U 78 - - 1554 Unnamed Lake 17 18-May-10 MT FNDC A MA U 65 - - 1555 Unnamed Lake 17 18-May-10 MT FNDC A MA F 74 - - 1556 Unnamed Lake 17 18-May-10 MT FNDC A MA M 55 - -




1557 Unnamed Lake 17 18-May-10 MT FNDC A MA U 78 - - 1558 Unnamed Lake 17 18-May-10 MT FNDC A MA U 79 - - 1559 Unnamed Lake 17 18-May-10 MT FNDC A MA U 76 - - 1560 Unnamed Lake 17 18-May-10 MT FNDC A MA U 75 - - 1561 Unnamed Lake 17 18-May-10 MT FNDC A MA M 65 - - 1562 Unnamed Lake 17 18-May-10 MT FNDC A MA U 80 - - 1563 Unnamed Lake 17 18-May-10 MT FNDC A MA F 80 - - 1564 Unnamed Lake 17 18-May-10 MT FNDC A MA F 76 - - 1565 Unnamed Lake 17 18-May-10 MT FNDC A MA F 75 - - 1566 Unnamed Lake 17 18-May-10 MT BRST A MA U 73 - - 1567 Unnamed Lake 17 18-May-10 MT FNDC A MA F 78 - - 1568 Unnamed Lake 17 18-May-10 MT FNDC A MA F 80 - - 1569 Unnamed Lake 17 18-May-10 MT FNDC A MA U 83 - - 1570 Unnamed Lake 17 18-May-10 MT FNDC A MA M 70 - - 1571 Unnamed Lake 17 18-May-10 MT BRST A MA U 54 - - 1572 Unnamed Lake 17 18-May-10 MT FNDC A MA F 78 - - 1573 Unnamed Lake 17 18-May-10 MT FNDC A MA F 75 - - 1574 Unnamed Lake 17 18-May-10 MT FNDC A MA F 80 - - 1575 Unnamed Lake 17 18-May-10 MT FNDC A MA U 65 - - 1576 Unnamed Lake 17 18-May-10 MT FNDC A MA U 69 - - 1577 Unnamed Lake 17 18-May-10 MT FNDC A MA F 90 - - 1578 Unnamed Lake 17 18-May-10 MT FNDC A MA U 75 - - 1579 Unnamed Lake 17 18-May-10 MT FNDC A MA U 75 - - 1580 Unnamed Lake 17 18-May-10 MT FNDC A MA F 76 - - 1581 Unnamed Lake 17 18-May-10 MT FNDC A MA F 73 - - 1582 Unnamed Lake 17 18-May-10 MT FNDC A MA U 75 - - 1583 Unnamed Lake 17 18-May-10 MT FNDC A MA U 70 - - 1584 Unnamed Lake 17 18-May-10 MT FNDC A MA U 76 - - 1585 Unnamed Lake 17 18-May-10 MT FNDC A MA F 79 - - 1586 Unnamed Lake 17 18-May-10 MT FNDC A MA U 72 - - 1587 Unnamed Lake 17 18-May-10 MT FNDC A MA F 78 - - 1588 Unnamed Lake 17 18-May-10 MT FNDC A MA F 81 - - 1589 Unnamed Lake 17 18-May-10 MT FNDC A MA F 80 - - 1590 Unnamed Lake 17 18-May-10 MT FNDC A MA F 87 - - 1591 Unnamed Lake 17 18-May-10 MT FNDC A MA F 78 - - 1592 Unnamed Lake 17 18-May-10 MT FNDC A MA M 78 - - 1593 Unnamed Lake 17 18-May-10 MT FNDC A MA F 83 - - 1594 Unnamed Lake 17 18-May-10 MT FNDC A MA F 80 - -




1595 Unnamed Lake 17 18-May-10 MT FNDC A MA F 80 - - 1596 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1597 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1598 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1599 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1600 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1601 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1602 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1603 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1604 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1605 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1606 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1607 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1608 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1609 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1610 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1611 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1612 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1613 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1614 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1615 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1616 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1617 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1618 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1619 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1620 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1621 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1622 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1623 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1624 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1625 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1626 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1627 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1628 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1629 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1630 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1631 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1632 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - -




1633 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1634 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1635 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1636 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1637 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1638 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1639 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1640 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1641 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1642 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1643 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1644 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1645 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1646 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1647 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1648 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1649 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1650 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1651 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1652 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1653 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1654 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1655 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1656 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1657 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1658 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1659 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1660 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1661 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1662 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1663 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1664 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1665 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1666 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1667 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1668 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1669 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1670 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - -




1899 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1900 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1901 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1902 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1903 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1904 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1905 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1906 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1907 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1908 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1909 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1910 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1911 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1912 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1913 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1914 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1915 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1916 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1917 Unnamed Lake 17 18-May-10 MT FNDC U UN U - - - 1918 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 41 1.1 1.60 1919 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 52 2.0 1.42 1920 Unnamed Lake 17 4-Aug-10 MT BRST U UN U 54 1.2 0.76 1921 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 51 1.2 0.90 1922 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 44 0.9 1.06 1923 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 42 0.9 1.21 1924 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 54 1.8 1.14 1925 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 21 0.1 1.08 1926 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 42 1.0 1.35 1927 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 55 2.6 1.56 1928 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 53 2.2 1.48 1929 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 60 2.2 1.02 1930 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 54 1.8 1.14 1931 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 47 0.8 0.77 1932 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 44 0.8 0.94 1933 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 49 1.2 1.02 1934 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 42 0.8 1.08 1935 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 41 0.8 1.16 1936 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 57 1.9 1.03




1937 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 62 2.5 1.05 1938 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 61 2.3 1.01 1939 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 60 2.2 1.02 1940 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 76 4.6 1.05 1941 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 42 0.9 1.21 1942 Unnamed Lake 17 4-Aug-10 MT BRST U UN U 37 0.5 0.99 1943 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 54 1.7 1.08 1944 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 56 1.7 0.97 1945 Unnamed Lake 17 4-Aug-10 MT BRST U UN U 52 0.5 0.36 1946 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 56 1.6 0.91 1947 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 56 1.8 1.02 1948 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 36 0.8 1.71 1949 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 47 0.8 0.77 1950 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 45 1.3 1.43 1951 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 52 2.3 1.64 1952 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 62 2.3 0.97 1953 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 65 3.1 1.13 1954 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 48 1.4 1.27 1955 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 52 1.6 1.14 1956 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 57 1.7 0.92 1957 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 53 2.0 1.34 1958 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 69 3.1 0.94 1959 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 52 1.8 1.28 1960 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 56 1.9 1.08 1961 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 54 1.8 1.14 1962 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 62 2.4 1.01 1963 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 48 1.1 0.99 1964 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 58 2.0 1.03 1965 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 53 1.6 1.07 1966 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 47 1.9 1.83 1967 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 49 1.4 1.19 1968 Unnamed Lake 17 4-Aug-10 MT BRST U UN U 48 1.1 0.99 1969 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 61 2.6 1.15 1970 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 44 1.0 1.17 1971 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 63 3.1 1.24 1972 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 57 2.2 1.19 1973 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 55 1.6 0.96 1974 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 51 1.6 1.21




1975 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 58 2.2 1.13 1976 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 46 1.5 1.54 1977 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 43 1.3 1.64 1978 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 42 1.2 1.62 1979 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 60 2.2 1.02 1980 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 59 2.8 1.36 1981 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 50 1.4 1.12 1982 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 52 1.3 0.92 1983 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 47 1.2 1.16 1984 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 44 1.2 1.41 1985 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 54 1.7 1.08 1986 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 43 1.0 1.26 1987 Unnamed Lake 17 4-Aug-10 MT BRST U UN U 47 1.0 0.96 1988 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 57 2.1 1.13 1989 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 51 1.3 0.98 1990 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 60 2.6 1.20 1991 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 61 2.8 1.23 1992 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 44 1.0 1.17 1993 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 64 3.1 1.18 1994 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 45 1.7 1.87 1995 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 56 1.7 0.97 1996 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 68 3.6 1.14 1997 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 60 2.4 1.11 1998 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 54 1.9 1.21 1999 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 60 2.4 1.11 2000 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 55 2.1 1.26 2001 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 54 1.9 1.21 2002 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 47 1.4 1.35 2003 Unnamed Lake 17 4-Aug-10 MT BRST U UN U 54 1.7 1.08 2004 Unnamed Lake 17 4-Aug-10 MT BRST U UN U 47 1.1 1.06 2005 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 50 2.1 1.68 2006 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 49 1.2 1.02 2007 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 50 1.4 1.12 2008 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 52 1.3 0.92 2009 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 55 2.0 1.20 2010 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 64 2.8 1.07 2011 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 54 2.1 1.33 2012 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 45 1.0 1.10




2013 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 54 1.6 1.02 2014 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 48 1.4 1.27 2015 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 70 3.9 1.14 2016 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 62 2.9 1.22 2017 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U 50 1.6 1.28 2018 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2019 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2020 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2021 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2022 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2023 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2024 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2025 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2026 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2027 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2028 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2029 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2030 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2031 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2032 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2033 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2034 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2035 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2036 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2037 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2038 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2039 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2040 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2041 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2042 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2043 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2044 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2045 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2046 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2047 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2048 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2049 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2050 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - -




2051 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2052 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2053 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2054 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2055 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2056 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2057 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2058 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2059 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2060 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2061 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2062 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2063 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2064 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2065 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2066 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2067 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2068 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2069 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2070 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2071 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2072 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2073 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2074 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2075 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2076 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2077 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2078 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2079 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2080 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2081 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2082 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2083 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2084 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2085 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2086 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2087 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2088 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - -




2241 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2242 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2243 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2244 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2245 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2246 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2247 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2248 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2249 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2250 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2251 Unnamed Lake 17 4-Aug-10 MT FNDC U UN U - - - 2252 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2253 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2254 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2255 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2256 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2257 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2258 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2259 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2260 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2261 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2262 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2263 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2264 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2265 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2266 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2267 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2268 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2269 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2270 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2271 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2272 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2273 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2274 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2275 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2276 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2277 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2278 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - -




2279 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2280 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2281 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2282 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2283 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2284 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2285 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2286 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2287 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2288 Unnamed Lake 17 4-Aug-10 MT BRST U UN U - - - 2289 Unnamed Lake 17 14-Sep-10 BEF BRST A MA U 61 - - 2290 Unnamed Lake 17 15-Sep-10 MT FNDC J IM U 55 - - 2291 Unnamed Lake 17 14-Sep-10 BEF BRST A MA U 64 - - 2292 Unnamed Lake 17 15-Sep-10 MT FNDC J IM U 49 - - 2293 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 34 - - 2294 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U 42 - - 2295 Unnamed Lake 17 14-Sep-10 BEF BRST A MA U 64 - - 2296 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U 57 - - 2297 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 31 - - 2298 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U 64 - - 2299 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 32 - - 2300 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U 61 - - 2301 Unnamed Lake 17 14-Sep-10 BEF BRST J IM U 38 - - 2302 Unnamed Lake 17 15-Sep-10 MT BRST A MA U 55 - - 2303 Unnamed Lake 17 14-Sep-10 BEF BRST A MA U 59 - - 2304 Unnamed Lake 17 15-Sep-10 MT BRST A MA U 63 - - 2305 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 31 - - 2306 Unnamed Lake 17 15-Sep-10 MT BRST U UN U 41 - - 2307 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 28 - - 2308 Unnamed Lake 17 15-Sep-10 MT FNDC A MA U 65 - - 2309 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 25 - - 2310 Unnamed Lake 17 15-Sep-10 MT FNDC J IM U 45 - - 2311 Unnamed Lake 17 14-Sep-10 BEF BRST U UN U 42 - - 2312 Unnamed Lake 17 15-Sep-10 MT BRST A MA U 55 - - 2313 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 38 - - 2314 Unnamed Lake 17 15-Sep-10 MT FNDC J IM U 45 - - 2315 Unnamed Lake 17 14-Sep-10 BEF BRST A MA U 63 - - 2316 Unnamed Lake 17 15-Sep-10 MT FNDC A MA U 54 - -




2317 Unnamed Lake 17 14-Sep-10 BEF BRST A MA U 68 - - 2318 Unnamed Lake 17 15-Sep-10 MT BRST A MA U 62 - - 2319 Unnamed Lake 17 14-Sep-10 BEF BRST U UN U 42 - - 2320 Unnamed Lake 17 15-Sep-10 MT BRST A MA U 58 - - 2321 Unnamed Lake 17 14-Sep-10 BEF BRST U UN U 43 - - 2322 Unnamed Lake 17 15-Sep-10 MT FNDC A MA U 54 - - 2323 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 39 - - 2324 Unnamed Lake 17 15-Sep-10 MT BRST U UN U 42 - - 2325 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 39 - - 2326 Unnamed Lake 17 15-Sep-10 MT FNDC A MA U 54 - - 2327 Unnamed Lake 17 14-Sep-10 BEF BRST A MA U 68 - - 2328 Unnamed Lake 17 15-Sep-10 MT FNDC A MA U 61 - - 2329 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 31 - - 2330 Unnamed Lake 17 15-Sep-10 MT FNDC A MA U 62 - - 2331 Unnamed Lake 17 14-Sep-10 BEF BRST U UN U 45 - - 2332 Unnamed Lake 17 15-Sep-10 MT BRST U UN U 58 - - 2333 Unnamed Lake 17 14-Sep-10 BEF BRST U UN U 42 - - 2334 Unnamed Lake 17 15-Sep-10 MT FNDC A MA U 64 - - 2335 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 29 - - 2336 Unnamed Lake 17 15-Sep-10 MT FNDC A MA U 55 - - 2337 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 31 - - 2338 Unnamed Lake 17 15-Sep-10 MT FNDC A MA U 58 - - 2339 Unnamed Lake 17 14-Sep-10 BEF BRST U UN U 42 - - 2340 Unnamed Lake 17 15-Sep-10 MT FNDC J IM U 50 - - 2341 Unnamed Lake 17 14-Sep-10 BEF BRST A MA U 51 - - 2342 Unnamed Lake 17 15-Sep-10 MT BRST U UN U 45 - - 2343 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 25 - - 2344 Unnamed Lake 17 15-Sep-10 MT FNDC A MA U 60 - - 2345 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 31 - - 2346 Unnamed Lake 17 15-Sep-10 MT FNDC A MA U 57 - - 2347 Unnamed Lake 17 14-Sep-10 BEF BRST U UN U 38 - - 2348 Unnamed Lake 17 15-Sep-10 MT BRST A MA U 56 - - 2349 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 35 - - 2350 Unnamed Lake 17 15-Sep-10 MT FNDC A MA U 51 - - 2351 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 36 - - 2352 Unnamed Lake 17 15-Sep-10 MT FNDC A MA U 58 - - 2353 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 31 - - 2354 Unnamed Lake 17 15-Sep-10 MT FNDC A MA U 53 - -




2355 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 32 - - 2356 Unnamed Lake 17 15-Sep-10 MT BRST A MA U 63 - - 2357 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 31 - - 2358 Unnamed Lake 17 15-Sep-10 MT BRST A MA U 64 - - 2359 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 31 - - 2360 Unnamed Lake 17 15-Sep-10 MT BRST U UN U 48 - - 2361 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 32 - - 2362 Unnamed Lake 17 15-Sep-10 MT BRST J IM U 32 - - 2363 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 31 - - 2364 Unnamed Lake 17 15-Sep-10 MT FNDC A MA U 58 - - 2365 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 30 - - 2366 Unnamed Lake 17 15-Sep-10 MT FNDC J IM U 47 - - 2367 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 29 - - 2368 Unnamed Lake 17 15-Sep-10 MT FNDC J IM U 46 - - 2369 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 31 - - 2370 Unnamed Lake 17 15-Sep-10 MT FNDC J IM U 48 - - 2371 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 29 - - 2372 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U 61 - - 2373 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 25 - - 2374 Unnamed Lake 17 15-Sep-10 MT FNDC J IM U 48 - - 2375 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 32 - - 2376 Unnamed Lake 17 15-Sep-10 MT BRST U UN U 53 - - 2377 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 31 - - 2378 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U 58 - - 2379 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 30 - - 2380 Unnamed Lake 17 15-Sep-10 MT BRST A MA U 63 - - 2381 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 38 - - 2382 Unnamed Lake 17 15-Sep-10 MT FNDC J IM U 42 - - 2383 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 29 - - 2384 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U 50 - - 2385 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 31 - - 2386 Unnamed Lake 17 15-Sep-10 MT BRST J IM U 43 - - 2387 Unnamed Lake 17 14-Sep-10 BEF BRST U UN U 38 - - 2388 Unnamed Lake 17 15-Sep-10 MT FNDC J IM U 41 - - 2389 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 31 - - 2390 Unnamed Lake 17 15-Sep-10 MT FNDC J IM U 45 - - 2391 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 33 - - 2392 Unnamed Lake 17 15-Sep-10 MT FNDC A MA U 78 - -




2393 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 29 - - 2394 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U 63 - - 2395 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 30 - - 2396 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U 62 - - 2397 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 30 - - 2398 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U 55 - - 2399 Unnamed Lake 17 14-Sep-10 BEF FNDC J IM U 28 - - 2400 Unnamed Lake 17 15-Sep-10 MT BRST A MA U 71 - - 2401 Unnamed Lake 17 15-Sep-10 MT FNDC A MA U 53 - - 2402 Unnamed Lake 17 15-Sep-10 MT BRST U UN U 58 - - 2403 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U 57 - - 2404 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U 54 - - 2405 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2406 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2407 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2408 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2409 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2410 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2411 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2412 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2413 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2414 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2415 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2416 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2417 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2418 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2419 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2420 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2421 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2422 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2423 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2424 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2425 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2426 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2427 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2428 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2429 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2430 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - -




2431 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2432 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2433 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2434 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2435 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2436 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2437 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2438 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2439 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2440 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2441 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2442 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2443 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2444 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2445 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2446 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2447 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2448 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2449 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2450 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2451 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2452 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2453 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2454 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2455 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2456 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2457 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2458 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2459 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2460 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2461 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2462 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2463 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2464 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2465 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2466 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2467 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2468 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - -




2925 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2926 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2927 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2928 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2929 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2930 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2931 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2932 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2933 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2934 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2935 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2936 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2937 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2938 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2939 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2940 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2941 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2942 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2943 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2944 Unnamed Lake 17 15-Sep-10 MT FNDC U UN U - - - 2945 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2946 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2947 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2948 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2949 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2950 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2951 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2952 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2953 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2954 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2955 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2956 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2957 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2958 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2959 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2960 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2961 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2962 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - -




2963 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2964 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2965 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2966 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2967 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2968 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2969 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2970 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2971 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2972 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2973 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2974 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2975 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2976 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2977 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2978 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2979 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2980 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2981 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2982 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2983 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2984 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2985 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2986 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2987 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2988 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2989 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2990 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2991 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2992 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2993 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2994 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2995 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2996 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2997 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2998 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 2999 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 3000 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - -




3001 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 3002 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 3003 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 3004 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 3005 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 3006 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 3007 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 3008 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 3009 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 3010 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 3011 Unnamed Lake 17 15-Sep-10 MT BRST U UN U - - - 3012 Unnamed Creek 18 18-May-10 MT FTMN J IM U 61 3.0 1.32 3013 Unnamed Creek 18 18-May-10 MT PRDC A MA U 86 4.0 0.63 3014 Unnamed Creek 18 18-May-10 MT PRDC A MA U 68 3.0 0.95 3015 Unnamed Creek 18 18-May-10 MT BRST U UN U 51 0.4 0.30 3016 Unnamed Creek 18 18-May-10 MT PRDC A MA U 72 2.0 0.54 3017 Unnamed Creek 18 18-May-10 MT BRST U UN U 63 1.0 0.40 3018 Unnamed Creek 18 18-May-10 MT PRDC A MA U 80 5.0 0.98 3019 Unnamed Creek 18 18-May-10 MT PRDC J IM U 55 1.0 0.60 3020 Unnamed Creek 18 18-May-10 MT BRST U UN U 64 1.0 0.38 3021 Unnamed Creek 18 18-May-10 MT PRDC A MA U 75 2.0 0.47 3022 Unnamed Creek 18 18-May-10 MT BRST U UN U 70 2.0 0.58 3023 Unnamed Creek 18 18-May-10 MT PRDC A MA U 68 2.0 0.64 3024 Unnamed Creek 18 18-May-10 MT PRDC J IM U 64 3.0 1.14 3025 Unnamed Creek 18 18-May-10 MT BRST U UN U 65 2.0 0.73 3026 Unnamed Creek 18 18-May-10 MT BRST U UN U 64 1.0 0.38 3027 Unnamed Creek 18 18-May-10 MT PRDC A MA U 71 3.0 0.84 3028 Unnamed Creek 18 18-May-10 MT PRDC J IM U 48 0.3 0.27 3029 Unnamed Creek 18 18-May-10 MT FTMN J IM U 58 2.0 1.03 3030 Unnamed Creek 18 18-May-10 MT BRST U UN U 64 1.0 0.38 3031 Unnamed Creek 18 18-May-10 MT BRST U UN U 68 1.0 0.32 3032 Unnamed Creek 18 18-May-10 MT PRDC A MA U 70 3.0 0.87 3033 Unnamed Creek 18 18-May-10 MT PRDC A MA U 70 4.0 1.17 3034 Unnamed Creek 18 18-May-10 MT BRST U UN U 57 0.3 0.16 3035 Unnamed Creek 18 18-May-10 MT BRST U UN U 65 2.0 0.73 3036 Unnamed Creek 18 18-May-10 MT BRST U UN U 70 2.0 0.58 3037 Unnamed Creek 18 18-May-10 MT PRDC J IM U 62 2.0 0.84 3038 Unnamed Creek 18 18-May-10 MT PRDC A MA U 65 2.0 0.73




3039 Unnamed Creek 18 18-May-10 MT BRST U UN U 75 3.0 0.71 3040 Unnamed Creek 18 18-May-10 MT BRST U UN U 70 3.0 0.87 3041 Unnamed Creek 18 18-May-10 MT PRDC A MA U 73 4.0 1.03 3042 Unnamed Creek 18 18-May-10 MT PRDC A MA U 74 5.0 1.23 3043 Unnamed Creek 18 18-May-10 MT BRST U UN U 60 0.5 0.23 3044 Unnamed Creek 18 18-May-10 MT BRST U UN U 68 2.0 0.64 3045 Unnamed Creek 18 18-May-10 MT PRDC J IM U 63 2.0 0.80 3046 Unnamed Creek 18 18-May-10 MT PRDC A MA U 70 3.0 0.87 3047 Unnamed Creek 18 18-May-10 MT BRST U UN U 60 1.0 0.46 3048 Unnamed Creek 18 18-May-10 MT BRST U UN U 66 1.0 0.35 3049 Unnamed Creek 18 18-May-10 MT PRDC J IM U 55 0.5 0.30 3050 Unnamed Creek 18 18-May-10 MT PRDC A MA U 68 3.0 0.95 3051 Unnamed Creek 18 18-May-10 MT BRST U UN U 63 1.0 0.40 3052 Unnamed Creek 18 18-May-10 MT BRST U UN U 66 1.0 0.35 3053 Unnamed Creek 18 18-May-10 MT BRST U UN U 50 0.8 0.64 3054 Unnamed Creek 18 18-May-10 MT BRST U UN U 69 2.0 0.61 3055 Unnamed Creek 18 18-May-10 MT PRDC A MA U 66 3.0 1.04 3056 Unnamed Creek 18 18-May-10 MT PRDC A MA U 70 4.0 1.17 3057 Unnamed Creek 18 18-May-10 MT BRST U UN U 61 0.8 0.35 3058 Unnamed Creek 18 18-May-10 MT BRST U UN U 60 0.7 0.32 3059 Unnamed Creek 18 18-May-10 MT BRST U UN U 63 1.0 0.40 3060 Unnamed Creek 18 18-May-10 MT PRDC J IM U 62 1.0 0.42 3061 Unnamed Creek 18 18-May-10 MT BRST U UN U 63 1.0 0.40 3062 Unnamed Creek 18 18-May-10 MT PRDC J IM U 55 0.4 0.24 3063 Unnamed Creek 18 18-May-10 MT PRDC A MA U 72 4.0 1.07 3064 Unnamed Creek 18 18-May-10 MT PRDC A MA U 73 4.0 1.03 3065 Unnamed Creek 18 18-May-10 MT BRST U UN U 60 1.0 0.46 3066 Unnamed Creek 18 18-May-10 MT PRDC J IM U 58 1.0 0.51 3067 Unnamed Creek 18 18-May-10 MT BRST J IM U 50 0.4 0.32 3068 Unnamed Creek 18 18-May-10 MT PRDC A MA U 65 3.0 1.09 3069 Unnamed Creek 18 18-May-10 MT PRDC A MA U 66 3.0 1.04 3070 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3071 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3072 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3073 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3074 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3075 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3076 Unnamed Creek 18 18-May-10 MT BRST U UN U - - -




3077 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3078 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3079 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3080 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3081 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3082 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3083 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3084 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3085 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3086 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3087 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3088 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3089 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3090 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3091 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3092 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3093 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3094 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3095 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3096 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3097 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3098 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3099 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3100 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3101 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3102 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3103 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3104 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3105 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3106 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3107 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3108 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3109 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3110 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3111 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3112 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3113 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3114 Unnamed Creek 18 18-May-10 MT BRST U UN U - - -




3115 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3116 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3117 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3118 Unnamed Creek 18 18-May-10 MT BRST U UN U - - - 3119 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3120 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3121 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3122 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3123 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3124 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3125 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3126 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3127 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3128 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3129 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3130 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3131 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3132 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3133 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3134 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3135 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3136 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3137 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3138 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3139 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3140 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3141 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3142 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3143 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3144 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3145 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3146 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3147 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3148 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3149 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3150 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3151 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3152 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - -




3153 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3154 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3155 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3156 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3157 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3158 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3159 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3160 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3161 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3162 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3163 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3164 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3165 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3166 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3167 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3168 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3169 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3170 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3171 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3172 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3173 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3174 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3175 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3176 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3177 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3178 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3179 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3180 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3181 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3182 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3183 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3184 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3185 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3186 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3187 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3188 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3189 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3190 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - -




3647 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3648 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3649 Unnamed Creek 18 18-May-10 MT PRDC U UN U - - - 3650 Unnamed Creek 18 18-May-10 MT FTMN U UN U - - - 3651 Unnamed Creek 18 18-May-10 MT FTMN U UN U - - - 3652 Unnamed Creek 18 18-May-10 MT FTMN U UN U - - - 3653 Unnamed Creek 18 18-May-10 MT FTMN U UN U - - - 3654 Unnamed Creek 18 18-May-10 MT FTMN U UN U - - - 3655 Unnamed Creek 18 18-May-10 MT FTMN U UN U - - - 3656 Unnamed Creek 18 18-May-10 MT FTMN U UN U - - - 3657 Unnamed Creek 18 18-May-10 MT FTMN U UN U - - - 3658 Unnamed Creek 18 20-Sep-10 BPEF FNDC A MA U 50 - - 3659 Unnamed Creek 18 20-Sep-10 BPEF BRST A MA U 62 - - 3660 Unnamed Creek 18 20-Sep-10 BPEF BRST U UN U 47 - - 3661 Unnamed Creek 18 20-Sep-10 BPEF BRST J IM U 23 - - 3662 Unnamed Creek 18 20-Sep-10 BPEF BRST A MA U 65 - - 3663 Unnamed Creek 18 20-Sep-10 BPEF BRST J IM U 24 - - 3664 Unnamed Creek 18 20-Sep-10 BPEF BRST U UN U 38 - - 3665 Unnamed Creek 18 20-Sep-10 BPEF BRST J IM U 24 - - 3666 Unnamed Creek 18 20-Sep-10 BPEF BRST J IM U 24 - - 3667 Unnamed Creek 18 20-Sep-10 BPEF BRST J IM U 21 - - 3668 Unnamed Creek 18 20-Sep-10 BPEF FNDC J IM U 38 - - 3669 Unnamed Creek 18 20-Sep-10 BPEF FNDC J IM U 48 - - 3670 Unnamed Creek 18 20-Sep-10 BPEF FNDC J IM U 39 - - 3671 Unnamed Creek 18 20-Sep-10 MT BRST A MA U 58 - - 3672 Unnamed Creek 18 20-Sep-10 MT BRST A MA U 60 - - 3673 Unnamed Creek 18 20-Sep-10 MT BRST A MA U 55 - - 3674 Unnamed Creek 18 20-Sep-10 MT FNDC J IM U 45 - - 3675 Unnamed Creek 18 20-Sep-10 MT FNDC J IM U 36 - - 3676 Unnamed Creek 18 20-Sep-10 MT FNDC A MA U 55 - - 3677 Unnamed Creek 18 20-Sep-10 MT FNDC U UN U 49 - - 3678 Unnamed Creek 18 20-Sep-10 MT FNDC U UN U 45 - - 3679 Unnamed Creek 18 20-Sep-10 MT FNDC U UN U 50 - - 3680 Unnamed Creek 18 20-Sep-10 MT FNDC U UN U 52 - - 3681 Unnamed Creek 18 20-Sep-10 MT FNDC U UN U 45 - - 3682 Unnamed Creek 18 20-Sep-10 MT BRST A MA U 65 - - 3683 Unnamed Creek 18 20-Sep-10 MT BRST A MA U 60 - - 3684 Unnamed Creek 18 20-Sep-10 MT BRST A MA U 62 - -




3685 Unnamed Creek 18 20-Sep-10 MT BRST A MA U 60 - - 3686 Unnamed Creek 18 20-Sep-10 MT FNDC U UN U 43 - - 3687 Unnamed Creek 18 20-Sep-10 MT BRST A MA U 67 - - 3688 Unnamed Creek 18 20-Sep-10 MT BRST A MA U 59 - - 3689 Sand River 19 18-May-10 MT PRDC A MA U 71 4.0 1.12 3690 Sand River 20 6-Aug-10 BPEF PRDC A MA U 75 - - 3691 Sand River 20 6-Aug-10 BPEF PRDC A MA U 164 - - 3692 Sand River 20 6-Aug-10 BPEF PRDC A MA U 85 - - 3693 Sand River 20 6-Aug-10 BPEF PRDC A MA U 85 - - 3694 Sand River 20 6-Aug-10 BPEF PRDC A MA U 82 - - 3695 Sand River 20 15-Sep-10 MT NRPK J IM U 130 - - 3696 Unnamed Creek 21 16-May-10 MT PRDC J IM U 65 2.0 0.73 3697 Unnamed Creek 21 16-May-10 MT PRDC A MA U 88 7.0 1.03 3698 Unnamed Creek 21 16-May-10 MT PRDC A MA U 85 6.0 0.98 3699 Unnamed Creek 21 16-May-10 MT PRDC J IM U 84 5.0 0.84 3700 Unnamed Creek 21 16-May-10 MT PRDC A MA U 75 4.0 0.95 3701 Unnamed Creek 21 16-May-10 MT PRDC J IM U 55 0.5 0.30 3702 Unnamed Creek 21 16-May-10 MT PRDC A MA U 94 8.0 0.96 3703 Unnamed Creek 21 16-May-10 MT PRDC A MA U 104 12.0 1.07 3704 Unnamed Creek 21 16-May-10 MT PRDC J IM U 58 2.0 1.03 3705 Unnamed Creek 21 16-May-10 MT PRDC J IM U 55 0.5 0.30 3706 Unnamed Creek 21 16-May-10 MT PRDC J IM U 60 0.7 0.32 3707 Unnamed Creek 21 16-May-10 MT PRDC A MA U 98 9.0 0.96 3708 Unnamed Creek 21 16-May-10 MT PRDC A MA U 98 8.0 0.85 3709 Unnamed Creek 21 16-May-10 MT PRDC J IM U 55 0.4 0.24 3710 Unnamed Creek 21 16-May-10 MT PRDC A MA U 76 5.0 1.14 3711 Unnamed Creek 21 16-May-10 MT PRDC J IM U 62 1.0 0.42 3712 Unnamed Creek 21 16-May-10 MT PRDC A MA U 77 4.0 0.88 3713 Unnamed Creek 21 16-May-10 MT PRDC J IM U 56 0.4 0.23 3714 Unnamed Creek 21 16-May-10 MT PRDC J IM U 56 1.0 0.57 3715 Unnamed Creek 21 16-May-10 MT PRDC J IM U 56 1.0 0.57 3716 Unnamed Creek 21 16-May-10 MT PRDC J IM U 54 1.0 0.64 3717 Unnamed Creek 21 16-May-10 MT PRDC J IM U 64 2.0 0.76 3718 Unnamed Creek 21 16-May-10 MT PRDC J IM U 66 0.7 0.24 3719 Unnamed Creek 21 16-May-10 MT PRDC A MA U 88 5.0 0.73 3720 Unnamed Creek 21 16-May-10 MT PRDC A MA U 74 4.0 0.99 3721 Unnamed Creek 21 16-May-10 MT PRDC J IM U 62 2.0 0.84 3722 Unnamed Creek 21 16-May-10 MT PRDC J IM U 56 2.0 1.14




3723 Unnamed Creek 21 16-May-10 MT PRDC A MA U 86 7.0 1.10 3724 Unnamed Creek 21 16-May-10 MT PRDC J IM U 52 0.5 0.36 3725 Unnamed Creek 21 16-May-10 MT PRDC A MA U 77 4.0 0.88 3726 Unnamed Creek 21 16-May-10 MT PRDC J IM U 60 3.0 1.39 3727 Unnamed Creek 21 16-May-10 MT PRDC A MA U 74 4.0 0.99 3728 Unnamed Creek 21 16-May-10 MT PRDC A MA U 80 4.0 0.78 3729 Unnamed Creek 21 16-May-10 MT PRDC A MA U 100 12.0 1.20 3730 Unnamed Creek 21 16-May-10 MT PRDC J IM U 48 0.3 0.27 3731 Unnamed Creek 21 16-May-10 MT PRDC A MA U 94 8.0 0.96 3732 Unnamed Creek 21 16-May-10 MT PRDC J IM U 48 0.3 0.27 3733 Unnamed Creek 21 16-May-10 MT PRDC A MA U 79 2.0 0.41 3734 Unnamed Creek 21 16-May-10 MT PRDC A MA U 71 3.0 0.84 3735 Unnamed Creek 21 16-May-10 MT PRDC A MA U 98 8.0 0.85 3736 Unnamed Creek 21 16-May-10 MT PRDC J IM U 58 2.0 1.03 3737 Unnamed Creek 21 16-May-10 MT PRDC A MA U 75 3.0 0.71 3738 Unnamed Creek 21 16-May-10 MT BRST U UN U 58 0.4 0.21 3739 Unnamed Creek 21 16-May-10 MT PRDC J IM U 55 1.0 0.60 3740 Unnamed Creek 21 16-May-10 MT PRDC J IM U 54 1.0 0.64 3741 Unnamed Creek 21 16-May-10 MT PRDC J IM U 57 0.3 0.16 3742 Unnamed Creek 21 16-May-10 MT PRDC A MA U 75 5.0 1.19 3743 Unnamed Creek 21 16-May-10 MT PRDC J IM U 61 2.0 0.88 3744 Unnamed Creek 21 16-May-10 MT PRDC J IM U 60 2.0 0.93 3745 Unnamed Creek 21 16-May-10 MT PRDC J IM U 59 2.0 0.97 3746 Unnamed Creek 21 16-May-10 MT PRDC J IM U 65 2.0 0.73 3747 Unnamed Creek 21 16-May-10 MT PRDC J IM U 54 0.3 0.19 3748 Unnamed Creek 21 16-May-10 MT PRDC A MA U 85 6.0 0.98 3749 Unnamed Creek 21 16-May-10 MT PRDC J IM U 55 0.4 0.24 3750 Unnamed Creek 21 16-May-10 MT BRST U UN U 58 0.3 0.15 3751 Unnamed Creek 21 16-May-10 MT PRDC J IM U 56 0.5 0.28 3752 Unnamed Creek 21 16-May-10 MT PRDC J IM U 59 1.0 0.49 3753 Unnamed Creek 21 16-May-10 MT PRDC J IM U 72 4.0 1.07 3754 Unnamed Creek 21 16-May-10 MT PRDC A MA U 65 4.0 1.46 3755 Unnamed Creek 21 16-May-10 MT BRST U UN U 75 3.0 0.71 3756 Unnamed Creek 21 16-May-10 MT PRDC J IM U 61 2.0 0.88 3757 Unnamed Creek 21 16-May-10 MT BRST U UN U 63 2.0 0.80 3758 Unnamed Creek 21 16-May-10 MT PRDC J IM U 53 1.0 0.67 3759 Unnamed Creek 21 16-May-10 MT PRDC U UN U - - - 3760 Unnamed Creek 21 16-May-10 MT PRDC U UN U - - -




4065 Unnamed Creek 21 16-May-10 MT PRDC U UN U - - - 4066 Unnamed Creek 21 16-May-10 MT PRDC U UN U - - - 4067 Unnamed Creek 21 16-May-10 MT PRDC U UN U - - - 4068 Unnamed Creek 21 16-May-10 MT PRDC U UN U - - - 4069 Unnamed Creek 21 16-May-10 MT PRDC U UN U - - - 4070 Unnamed Creek 21 16-May-10 MT PRDC U UN U - - - 4071 Unnamed Creek 21 16-May-10 MT PRDC U UN U - - - 4072 Unnamed Creek 21 16-May-10 MT PRDC U UN U - - - 4073 Unnamed Creek 21 16-May-10 MT PRDC U UN U - - - 4074 Unnamed Creek 21 16-May-10 MT BRST U UN U - - - 4075 Unnamed Creek 21 16-May-10 MT BRST U UN U - - - 4076 Unnamed Creek 21 16-May-10 MT BRST U UN U - - - 4077 Unnamed Creek 21 16-May-10 MT BRST U UN U - - - 4078 Unnamed Creek 21 16-Sep-10 BPEF FNDC J IM U 58 - - 4079 Unnamed Creek 21 16-Sep-10 BPEF FNDC J IM U 33 - - 4080 Unnamed Creek 21 16-Sep-10 BPEF BRST U UN U 51 - - 4081 Unnamed Creek 21 16-Sep-10 BPEF FNDC J IM U 31 - - 4082 Unnamed Creek 21 16-Sep-10 BPEF FNDC J IM U 29 - - 4083 Unnamed Creek 21 16-Sep-10 BPEF FNDC J IM U 28 - - 4084 Unnamed Creek 21 16-Sep-10 MT BRST A MA U 56 - - 4085 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 55 - - 4086 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 50 - - 4087 Unnamed Creek 21 16-Sep-10 MT FNDC A MA U 91 - - 4088 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 52 - - 4089 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 51 - - 4090 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 53 - - 4091 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 50 - - 4092 Unnamed Creek 21 16-Sep-10 MT FNDC A MA U 68 - - 4093 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 45 - - 4094 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 48 - - 4095 Unnamed Creek 21 16-Sep-10 MT BRST U UN U 54 - - 4096 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 47 - - 4097 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 45 - - 4098 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 44 - - 4099 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 55 - - 4100 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 56 - - 4101 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 51 - - 4102 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 52 - -




4103 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 50 - - 4104 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 45 - - 4105 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 48 - - 4106 Unnamed Creek 21 16-Sep-10 MT BRST U UN U 50 - - 4107 Unnamed Creek 21 16-Sep-10 MT BRST A MA U 56 - - 4108 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 49 - - 4109 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 53 - - 4110 Unnamed Creek 21 16-Sep-10 MT FNDC J IM U 50 - - 4111 Unnamed Creek 21 16-Sep-10 MT BRST A MA U 57 - - 4112 Sand River 22 16-May-10 MT PRDC J IM U 55 3.0 1.80 4113 Sand River 22 16-May-10 MT PRDC J IM U 53 1.0 0.67 4114 Sand River 22 16-May-10 MT PRDC J IM U 54 2.0 1.27 4115 Sand River 22 16-May-10 MT PRDC J IM U 48 1.0 0.90 4116 Sand River 22 16-May-10 MT PRDC A MA U 87 6.0 0.91 4117 Sand River 22 16-May-10 MT PRDC A MA U 81 5.0 0.94 4118 Sand River 22 16-May-10 MT PRDC J IM U 51 0.5 0.38 4119 Sand River 22 16-May-10 MT PRDC J IM U 69 4.0 1.22 4120 Sand River 22 16-May-10 MT PRDC J IM U 58 0.5 0.26 4121 Sand River 22 16-May-10 MT PRDC J IM U 54 0.4 0.25 4122 Sand River 22 16-May-10 MT PRDC J IM U 49 1.0 0.85 4123 Sand River 22 16-May-10 MT PRDC J IM U 47 1.0 0.96 4124 Sand River 22 16-May-10 MT PRDC J IM U 46 0.4 0.41 4125 Sand River 22 16-May-10 MT PRDC J IM U 49 0.5 0.42 4126 Sand River 22 16-May-10 MT PRDC J IM U 54 0.5 0.32 4127 Sand River 22 16-May-10 MT PRDC J IM U 57 1.0 0.54 4128 Sand River 22 16-May-10 MT PRDC J IM U 48 0.4 0.36 4129 Sand River 22 16-May-10 MT PRDC J IM U 50 1.0 0.80 4130 Sand River 22 16-May-10 MT PRDC J IM U 51 1.0 0.75 4131 Sand River 22 16-May-10 MT PRDC J IM U 62 3.0 1.26 4132 Sand River 22 16-May-10 MT PRDC A MA U 69 3.0 0.91 4133 Sand River 22 16-May-10 MT PRDC A MA U 62 2.0 0.84 4134 Sand River 22 16-May-10 MT PRDC J IM U 55 1.0 0.60 4135 Sand River 22 16-May-10 MT BRST U UN U 65 1.0 0.36 4136 Sand River 22 16-May-10 MT PRDC J IM U 66 2.0 0.70 4137 Sand River 22 16-May-10 MT PRDC A MA U 86 7.0 1.10 4138 Sand River 22 16-May-10 MT PRDC J IM U 52 0.5 0.36 4139 Sand River 22 16-May-10 MT PRDC J IM U 57 1.0 0.54 4140 Sand River 22 16-May-10 MT PRDC J IM U 60 2.0 0.93




4141 Sand River 22 16-May-10 MT PRDC J IM U 63 1.0 0.40 4142 Sand River 22 16-May-10 MT PRDC A MA U 75 3.0 0.71 4143 Sand River 22 16-May-10 MT PRDC J IM U 61 1.0 0.44 4144 Sand River 22 16-May-10 MT PRDC J IM U 60 1.0 0.46 4145 Sand River 22 16-May-10 MT BRST U UN U 62 1.0 0.42 4146 Sand River 22 16-May-10 MT PRDC J IM U 68 3.0 0.95 4147 Sand River 22 16-May-10 MT PRDC J IM U 52 1.0 0.71 4148 Sand River 22 16-May-10 MT PRDC J IM U 51 0.5 0.38 4149 Sand River 22 16-May-10 MT PRDC J IM U 61 3.0 1.32 4150 Sand River 22 16-May-10 MT PRDC J IM U 58 0.5 0.26 4151 Sand River 22 16-May-10 MT PRDC J IM U 62 2.0 0.84 4152 Sand River 22 16-May-10 MT PRDC J IM U 48 0.3 0.27 4153 Sand River 22 16-May-10 MT PRDC J IM U 60 2.0 0.93 4154 Sand River 22 16-May-10 MT PRDC A MA U 79 4.0 0.81 4155 Sand River 22 16-May-10 MT PRDC J IM U 52 0.4 0.28 4156 Sand River 22 16-May-10 MT PRDC A MA U 68 3.0 0.95 4157 Sand River 22 16-May-10 MT PRDC J IM U 59 0.6 0.29 4158 Sand River 22 16-May-10 MT PRDC J IM U 57 0.6 0.32 4159 Sand River 22 16-May-10 MT PRDC J IM U 63 3.0 1.20 4160 Sand River 22 16-May-10 MT PRDC J IM U 60 2.0 0.93 4161 Sand River 22 16-May-10 MT PRDC J IM U 60 2.0 0.93 4162 Sand River 22 16-May-10 MT PRDC J IM U 54 1.0 0.64 4163 Sand River 22 16-May-10 MT PRDC J IM U 54 0.7 0.44 4164 Sand River 22 16-May-10 MT PRDC J IM U 58 1.0 0.51 4165 Sand River 22 16-May-10 MT PRDC J IM U 52 0.7 0.50 4166 Sand River 22 16-May-10 MT PRDC J IM U 52 0.5 0.36 4167 Sand River 22 16-May-10 MT PRDC J IM U 56 2.0 1.14 4168 Sand River 22 16-May-10 MT PRDC J IM U 68 3.0 0.95 4169 Sand River 22 16-May-10 MT PRDC J IM U 60 0.7 0.32 4170 Sand River 22 16-May-10 MT WHSC J IM U 68 2.0 0.64 4171 Sand River 22 16-May-10 MT PRDC U UN U - - - 4172 Sand River 22 16-May-10 MT PRDC U UN U - - - 4173 Sand River 22 16-May-10 MT PRDC U UN U - - - 4174 Sand River 22 16-May-10 MT PRDC U UN U - - - 4175 Sand River 22 16-May-10 MT PRDC U UN U - - - 4176 Sand River 22 16-May-10 MT PRDC U UN U - - - 4177 Sand River 22 16-May-10 MT PRDC U UN U - - - 4178 Sand River 22 16-May-10 MT PRDC U UN U - - -




4179 Sand River 22 16-May-10 MT PRDC U UN U - - - 4180 Sand River 22 16-May-10 MT PRDC U UN U - - - 4181 Sand River 22 16-May-10 MT PRDC U UN U - - - 4182 Sand River 22 16-May-10 MT PRDC U UN U - - - 4183 Sand River 22 16-May-10 MT PRDC U UN U - - - 4184 Sand River 22 16-May-10 MT PRDC U UN U - - - 4185 Sand River 22 16-May-10 MT PRDC U UN U - - - 4186 Sand River 22 16-May-10 MT PRDC U UN U - - - 4187 Sand River 22 16-May-10 MT PRDC U UN U - - - 4188 Sand River 22 16-May-10 MT PRDC U UN U - - - 4189 Sand River 22 16-May-10 MT PRDC U UN U - - - 4190 Sand River 22 16-May-10 MT PRDC U UN U - - - 4191 Sand River 22 16-May-10 MT PRDC U UN U - - - 4192 Sand River 22 16-May-10 MT PRDC U UN U - - - 4193 Sand River 22 16-May-10 MT PRDC U UN U - - - 4194 Sand River 22 16-May-10 MT PRDC U UN U - - - 4195 Sand River 22 16-May-10 MT PRDC U UN U - - - 4196 Sand River 22 16-May-10 MT PRDC U UN U - - - 4197 Sand River 22 16-May-10 MT PRDC U UN U - - - 4198 Sand River 22 16-May-10 MT PRDC U UN U - - - 4199 Sand River 22 16-May-10 MT PRDC U UN U - - - 4200 Sand River 22 16-May-10 MT PRDC U UN U - - - 4201 Sand River 22 16-May-10 MT PRDC U UN U - - - 4202 Sand River 22 16-May-10 MT PRDC U UN U - - - 4203 Sand River 22 16-May-10 MT PRDC U UN U - - - 4204 Sand River 22 16-May-10 MT PRDC U UN U - - - 4205 Sand River 22 16-May-10 MT PRDC U UN U - - - 4206 Sand River 22 16-May-10 MT PRDC U UN U - - - 4207 Sand River 22 16-May-10 MT PRDC U UN U - - - 4208 Sand River 22 16-May-10 MT PRDC U UN U - - - 4209 Sand River 22 16-May-10 MT PRDC U UN U - - - 4210 Sand River 22 16-May-10 MT PRDC U UN U - - - 4211 Sand River 22 16-May-10 MT PRDC U UN U - - - 4212 Sand River 22 16-May-10 MT PRDC U UN U - - - 4213 Sand River 22 16-May-10 MT PRDC U UN U - - - 4214 Sand River 22 16-May-10 MT PRDC U UN U - - - 4215 Sand River 22 16-May-10 MT PRDC U UN U - - - 4216 Sand River 22 16-May-10 MT PRDC U UN U - - -




4293 Sand River 22 16-May-10 MT BRST U UN U - - - 4294 Sand River 22 15-Sep-10 BPEF SPSC A MA U 112 - - 4295 Sand River 22 15-Sep-10 BPEF FNDC A MA U 74 - - 4296 Sand River 22 15-Sep-10 BPEF FNDC A MA U 87 - - 4297 Sand River 22 15-Sep-10 BPEF FNDC A MA U 85 - - 4298 Sand River 22 15-Sep-10 BPEF FNDC A MA U 69 - - 4299 Sand River 22 15-Sep-10 BPEF FNDC J IM U 30 - - 4300 Sand River 22 15-Sep-10 BPEF FNDC J IM U 30 - - 4301 Sand River 22 15-Sep-10 BPEF FNDC J IM U 30 - - 4302 Sand River 22 15-Sep-10 BPEF FNDC J IM U 32 - - 4303 Sand River 22 16-Sep-10 MT FNDC A MA U 62 - - 4304 Sand River 22 16-Sep-10 MT FNDC A MA U 90 - - 4305 Sand River 22 16-Sep-10 MT FNDC A MA U 64 - - 4306 Sand River 22 16-Sep-10 MT FNDC J IM U 52 - - 4307 Sand River 22 16-Sep-10 MT FNDC U UN U 66 - - 4308 Sand River 22 16-Sep-10 MT FNDC U UN U 62 - - 4309 Sand River 22 16-Sep-10 MT FNDC J IM U 56 - - 4310 Sand River 22 16-Sep-10 MT FNDC A MA U 96 - - 4311 Sand River 22 16-Sep-10 MT FNDC J IM U 48 - - 4312 Sand River 22 16-Sep-10 MT FNDC A MA U 88 - - 4313 Sand River 22 16-Sep-10 MT FNDC A MA U 68 - - 4314 Sand River 22 16-Sep-10 MT FNDC J IM U 48 - - 4315 Sand River 22 16-Sep-10 MT FNDC A MA U 64 - - 4316 Sand River 22 16-Sep-10 MT FNDC A MA U 69 - - 4317 Sand River 22 16-Sep-10 MT FNDC J IM U 60 - - 4318 Sand River 22 16-Sep-10 MT FNDC J IM U 56 - - 4319 Sand River 22 16-Sep-10 MT FNDC J IM U 45 - - 4320 Sand River 22 16-Sep-10 MT FNDC A MA U 70 - - 4321 Sand River 22 16-Sep-10 MT FNDC U UN U 59 - - 4322 Sand River 22 16-Sep-10 MT FNDC J IM U 55 - - 4323 Unnamed Creek 23 16-May-10 MT PRDC A MA U 87 8.0 1.21 4324 Unnamed Creek 23 16-May-10 MT BRST U UN U 61 1.0 0.44 4325 Unnamed Creek 23 16-May-10 MT BRST U UN U 50 0.4 0.32 4326 Unnamed Creek 23 16-May-10 MT BRST U UN U 54 0.4 0.25 4327 Unnamed Creek 23 16-May-10 MT BRST U UN U 43 0.2 0.25 4328 Unnamed Creek 23 16-May-10 MT BRST U UN U 50 1.0 0.80 4329 Unnamed Creek 23 16-May-10 MT BRST U UN U 65 2.0 0.73 4330 Unnamed Creek 23 16-May-10 MT BRST U UN U 48 1.0 0.90




4331 Unnamed Creek 23 16-May-10 MT BRST U UN U 48 1.0 0.90 4332 Unnamed Creek 23 16-May-10 MT BRST U UN U 50 1.0 0.80 4333 Unnamed Creek 23 16-May-10 MT BRST U UN U 48 0.3 0.27 4334 Unnamed Creek 23 16-May-10 MT BRST U UN U 59 1.0 0.49 4335 Unnamed Creek 23 16-May-10 MT BRST U UN U 66 3.0 1.04 4336 Unnamed Creek 23 16-May-10 MT BRST U UN U 60 0.5 0.23 4337 Unnamed Creek 23 16-May-10 MT PRDC J IM U 60 0.5 0.23 4338 Unnamed Creek 23 16-May-10 MT BRST U UN U 58 0.4 0.21 4339 Unnamed Creek 23 16-May-10 MT PRDC J IM U 53 0.4 0.27 4340 Unnamed Creek 23 16-May-10 MT WHSC J IM U 77 5.0 1.10 4341 Unnamed Creek 23 16-May-10 MT BRST U UN U 55 0.3 0.18 4342 Unnamed Creek 23 16-May-10 MT BRST U UN U 58 1.0 0.51 4343 Unnamed Creek 23 16-May-10 MT PRDC J IM U 55 1.0 0.60 4344 Unnamed Creek 23 16-May-10 MT BRST U UN U 63 2.0 0.80 4345 Unnamed Creek 23 16-May-10 MT PRDC J IM U 59 2.0 0.97 4346 Unnamed Creek 23 16-May-10 MT BRST U UN U 65 2.0 0.73 4347 Unnamed Creek 23 16-May-10 MT PRDC J IM U 46 0.8 0.82 4348 Unnamed Creek 23 16-May-10 MT BRST U UN U 60 1.0 0.46 4349 Unnamed Creek 23 16-May-10 MT BRST U UN U 63 1.0 0.40 4350 Unnamed Creek 23 16-May-10 MT PRDC J IM U 50 0.4 0.32 4351 Unnamed Creek 23 15-Sep-10 BPEF BRST J IM U 44 - - 4352 Unnamed Creek 23 16-Sep-10 MT BRST J IM U 59 - - 4353 Unnamed Creek 23 16-Sep-10 MT FNDC J IM U 48 - - 4354 Unnamed Creek 24 19-Sep-10 BPEF BRST A MA U 58 - - 4355 Unnamed Creek 24 19-Sep-10 BPEF BRST A MA U 65 - - 4356 Unnamed Creek 24 19-Sep-10 BPEF BRST A MA U 65 - - 4357 Unnamed Creek 24 19-Sep-10 BPEF BRST U UN U 52 - - 4358 Unnamed Creek 24 19-Sep-10 BPEF BRST U UN U 50 - - 4359 Unnamed Creek 24 1-Jun-11 MT FNDC U UN U 74 - - 4360 Unnamed Creek 24 1-Jun-11 MT BRST U UN U 63 - - 4361 Unnamed Creek 24 1-Jun-11 MT BRST U UN U 56 - - 4362 Unnamed Creek 24 1-Jun-11 MT BRST U UN U 65 - - 4363 Unnamed Creek 24 1-Jun-11 MT BRST U UN U 85 - - 4364 Unnamed Creek 24 1-Jun-11 MT FNDC U UN U 75 - - 4365 Unnamed Creek 24 1-Jun-11 MT FNDC U UN U 73 - - 4366 Unnamed Creek 24 1-Jun-11 MT FNDC U UN U 79 - - 4367 Unnamed Creek 24 1-Jun-11 MT FNDC U UN U 78 - - 4368 Unnamed Creek 24 1-Jun-11 MT BRST U UN U 58 - -




4369 Unnamed Creek 24 1-Jun-11 MT BRST U UN U 48 - - 4370 Unnamed Lake 25 16-Sep-10 BEF BRST J IM U 35 - - 4371 Unnamed Lake 25 16-Sep-10 BEF BRST A MA U 59 - - 4372 Unnamed Lake 25 16-Sep-10 BEF BRST J IM U 34 - - 4373 Unnamed Lake 25 16-Sep-10 BEF BRST J IM U 36 - - 4374 Unnamed Lake 25 16-Sep-10 BEF BRST J IM U 32 - - 4375 Unnamed Lake 25 16-Sep-10 BEF BRST J IM U 26 - - 4376 Unnamed Lake 25 16-Sep-10 BEF BRST J IM U 31 - - 4377 Unnamed Lake 25 16-Sep-10 BEF PRDC J IM U 27 - - 4378 Unnamed Lake 25 16-Sep-10 MT BRST A MA U 70 - - 4379 Unnamed Lake 25 16-Sep-10 MT FTMN J IM U 39 - - 4380 Unnamed Lake 25 16-Sep-10 MT BRST A MA U 51 - - 4381 Unnamed Lake 25 16-Sep-10 MT BRST A MA U 52 - - 4382 Unnamed Lake 25 16-Sep-10 MT BRST U UN U 45 - - 4383 Unnamed Lake 25 16-Sep-10 MT FTMN J IM U 42 - - 4384 Unnamed Lake 25 16-Sep-10 MT FTMN J IM U 43 - - 4385 Unnamed Lake 25 16-Sep-10 MT BRST U UN U 46 - - 4386 Unnamed Lake 25 16-Sep-10 MT BRST U UN U 45 - - 4387 Unnamed Lake 25 16-Sep-10 MT BRST U UN U 46 - - 4388 Unnamed Lake 25 16-Sep-10 MT BRST U UN U 50 - - 4389 Unnamed Lake 25 16-Sep-10 MT BRST U UN U 45 - - 4390 Unnamed Lake 25 16-Sep-10 MT FTMN J IM U 32 - - 4391 Unnamed Lake 25 16-Sep-10 MT FNDC J IM U 36 - - 4392 Unnamed Lake 25 16-Sep-10 MT BRST U UN U 45 - - 4393 Unnamed Lake 25 16-Sep-10 MT BRST A MA U 55 - - 4394 Unnamed Lake 25 16-Sep-10 MT FTMN U UN U 42 - - 4395 Unnamed Lake 25 16-Sep-10 MT FTMN U UN U 40 - - 4396 Unnamed Lake 25 16-Sep-10 MT BRST U UN U 41 - - 4397 Unnamed Lake 25 16-Sep-10 MT BRST J IM U 36 - - 4398 Unnamed Lake 25 16-Sep-10 MT BRST J IM U 38 - - 4399 Unnamed Lake 25 16-Sep-10 MT BRST J IM U 38 - - 4400 Unnamed Lake 25 16-Sep-10 MT BRST U UN U 46 - - 4401 Unnamed Lake 25 16-Sep-10 MT BRST A MA U 65 - - 4402 Unnamed Lake 25 16-Sep-10 MT BRST U UN U 45 - - 4403 Unnamed Lake 25 16-Sep-10 MT BRST J IM U 35 - - 4404 Unnamed Lake 25 16-Sep-10 MT BRST J IM U 42 - - 4405 Unnamed Lake 25 16-Sep-10 MT BRST A MA U 60 - - 4406 Unnamed Lake 25 16-Sep-10 MT BRST U UN U 41 - -




4407 Unnamed Lake 25 16-Sep-10 MT BRST A MA U 50 - - 4408 Unnamed Lake 25 16-Sep-10 MT BRST U UN U 41 - - 4409 Unnamed Lake 25 16-Sep-10 MT FTMN U UN U 40 - - 4410 Unnamed Lake 25 16-Sep-10 MT BRST U UN U 42 - - 4411 Unnamed Lake 25 16-Sep-10 MT BRST U UN U 42 - - 4412 Unnamed Lake 25 16-Sep-10 MT FNDC J IM U 36 - - 4413 Unnamed Lake 25 16-Sep-10 MT BRST U UN U 51 - - 4414 Unnamed Lake 25 16-Sep-10 MT BRST U UN U 45 - - 4415 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U 55 - - 4416 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U 55 - - 4417 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U 55 - - 4418 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 70 - - 4419 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 70 - - 4420 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 68 - - 4421 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 65 - - 4422 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 70 - - 4423 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 50 - - 4424 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 53 - - 4425 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 67 - - 4426 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 68 - - 4427 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U 50 - - 4428 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 57 - - 4429 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 70 - - 4430 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 60 - - 4431 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 65 - - 4432 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 58 - - 4433 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 60 - - 4434 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 55 - - 4435 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 63 - - 4436 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 70 - - 4437 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 65 - - 4438 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 72 - - 4439 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 52 - - 4440 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 71 - - 4441 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 66 - - 4442 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 63 - - 4443 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 48 - - 4444 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 70 - -




4445 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 72 - - 4446 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 50 - - 4447 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 57 - - 4448 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 63 - - 4449 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 52 - - 4450 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 52 - - 4451 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 45 - - 4452 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 53 - - 4453 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 74 - - 4454 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 70 - - 4455 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 75 - - 4456 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 50 - - 4457 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 78 - - 4458 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 52 - - 4459 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 70 - - 4460 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 65 - - 4461 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 47 - - 4462 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 65 - - 4463 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 71 - - 4464 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 50 - - 4465 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 65 - - 4466 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 72 - - 4467 Unnamed Lake 25 2-Jun-11 MT BRST U UN U 69 - - 4468 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U 44 - - 4469 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U 55 - - 4470 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U 55 - - 4471 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U 54 - - 4472 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U 59 - - 4473 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U 50 - - 4474 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U 58 - - 4475 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U 49 - - 4476 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U 50 - - 4477 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U 57 - - 4478 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U 58 - - 4479 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U 55 - - 4480 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U 55 - - 4481 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U 55 - - 4482 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - -




4483 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4484 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4485 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4486 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4487 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4488 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4489 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4490 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4491 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4492 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4493 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4494 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4495 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4496 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4497 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4498 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4499 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4500 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4501 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4502 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4503 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4504 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4505 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4506 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4507 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4508 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4509 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4510 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4511 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4512 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4513 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4514 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4515 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4516 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4517 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4518 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4519 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4520 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - -




4559 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4560 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4561 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4562 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4563 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4564 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4565 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4566 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4567 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4568 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4569 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4570 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4571 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4572 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4573 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4574 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4575 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4576 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4577 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4578 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4579 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4580 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4581 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4582 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4583 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4584 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4585 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4586 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4587 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4588 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4589 Unnamed Lake 25 2-Jun-11 MT BRST U UN U - - - 4590 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4591 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4592 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4593 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4594 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4595 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4596 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - -




4597 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4598 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4599 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4600 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4601 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4602 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4603 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4604 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4605 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4606 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4607 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4608 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4609 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4610 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4611 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4612 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4613 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4614 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4615 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4616 Unnamed Lake 25 2-Jun-11 MT FTMN U UN U - - - 4617 Unnamed Lake 26 16-Sep-10 BEF BRST J IM U 42 - - 4618 Unnamed Lake 26 16-Sep-10 BEF FNDC J IM U 35 - - 4619 Unnamed Lake 26 16-Sep-10 BEF BRST A MA U 57 - - 4620 Unnamed Lake 26 16-Sep-10 BEF BRST A MA U 72 - - 4621 Unnamed Lake 26 16-Sep-10 BEF BRST J IM U 32 - - 4622 Unnamed Lake 26 16-Sep-10 BEF BRST J IM U 31 - - 4623 Unnamed Lake 26 16-Sep-10 BEF BRST J IM U 34 - - 4624 Unnamed Lake 26 16-Sep-10 BEF BRST A MA U 61 - - 4625 Unnamed Lake 26 16-Sep-10 BEF BRST A MA U 68 - - 4626 Unnamed Lake 26 16-Sep-10 BEF FNDC J IM U 32 - - 4627 Unnamed Lake 26 16-Sep-10 BEF BRST A MA U 68 - - 4628 Unnamed Lake 26 16-Sep-10 BEF BRST J IM U 34 - - 4629 Unnamed Lake 26 16-Sep-10 BEF BRST J IM U 32 - - 4630 Unnamed Lake 26 16-Sep-10 BEF BRST A MA U 58 - - 4631 Unnamed Lake 26 16-Sep-10 BEF BRST A MA U 62 - - 4632 Unnamed Lake 26 16-Sep-10 BEF BRST U UN U 45 - - 4633 Unnamed Lake 26 16-Sep-10 BEF BRST J IM U 32 - - 4634 Unnamed Lake 26 16-Sep-10 BEF FNDC J IM U 33 - -




4635 Unnamed Lake 26 16-Sep-10 BEF BRST J IM U 35 - - 4636 Unnamed Lake 26 16-Sep-10 BEF FNDC J IM U 41 - - 4637 Unnamed Lake 26 16-Sep-10 BEF BRST J IM U 38 - - 4638 Unnamed Lake 26 16-Sep-10 BEF FNDC J IM U 33 - - 4639 Unnamed Lake 26 16-Sep-10 BEF FNDC J IM U 34 - - 4640 Unnamed Lake 26 16-Sep-10 BEF FNDC J IM U 35 - - 4641 Unnamed Lake 26 16-Sep-10 BEF BRST A MA U 58 - - 4642 Unnamed Lake 26 16-Sep-10 BEF BRST A MA U 54 - - 4643 Unnamed Lake 26 16-Sep-10 BEF BRST J IM U 40 - - 4644 Unnamed Lake 26 16-Sep-10 BEF FNDC J IM U 38 - - 4645 Unnamed Lake 26 16-Sep-10 BEF BRST J IM U 25 - - 4646 Unnamed Lake 26 16-Sep-10 BEF BRST J IM U 42 - - 4647 Unnamed Lake 26 16-Sep-10 BEF BRST J IM U 46 - - 4648 Unnamed Lake 26 16-Sep-10 BEF BRST J IM U 40 - - 4649 Unnamed Lake 26 16-Sep-10 BEF BRST J IM U 25 - - 4650 Unnamed Lake 26 16-Sep-10 BEF BRST J IM U 40 - - 4651 Unnamed Lake 26 16-Sep-10 BEF BRST J IM U 26 - - 4652 Unnamed Lake 26 16-Sep-10 BEF FNDC J IM U 32 - - 4653 Unnamed Lake 26 16-Sep-10 BEF FNDC J IM U 25 - - 4654 Unnamed Lake 26 16-Sep-10 BEF BRST J IM U 25 - - 4655 Unnamed Lake 26 16-Sep-10 BEF FNDC J IM U 25 - - 4656 Unnamed Lake 26 16-Sep-10 BEF FNDC J IM U 33 - - 4657 Unnamed Lake 26 16-Sep-10 BEF BRST A MA U 52 - - 4658 Unnamed Lake 26 16-Sep-10 BEF FNDC J IM U 27 - - 4659 Unnamed Lake 26 16-Sep-10 BEF FNDC J IM U 30 - - 4660 Unnamed Lake 26 16-Sep-10 BEF FNDC J IM U 37 - - 4661 Unnamed Lake 26 16-Sep-10 BEF FNDC J IM U 31 - - 4662 Unnamed Lake 26 16-Sep-10 BEF BRST J IM U 36 - - 4663 Unnamed Lake 26 16-Sep-10 BEF BRST J IM U 45 - - 4664 Unnamed Lake 26 16-Sep-10 BEF FNDC J IM U 30 - - 4665 Unnamed Lake 26 16-Sep-10 BEF FNDC J IM U 31 - - 4666 Unnamed Lake 26 16-Sep-10 BEF FNDC J IM U 35 - - 4667 Unnamed Lake 26 16-Sep-10 BEF FNDC J IM U 30 - - 4668 Unnamed Lake 26 16-Sep-10 MT BRST A MA U 57 - - 4669 Unnamed Lake 26 16-Sep-10 MT BRST A MA U 51 - - 4670 Unnamed Lake 26 16-Sep-10 MT BRST A MA U 56 - - 4671 Unnamed Lake 26 16-Sep-10 MT FNDC A MA U 53 - - 4672 Unnamed Lake 26 16-Sep-10 MT FNDC A MA U 56 - -




4673 Unnamed Lake 26 16-Sep-10 MT BRST A MA U 51 - - 4674 Unnamed Lake 26 16-Sep-10 MT BRST A MA U 53 - - 4675 Unnamed Lake 26 16-Sep-10 MT BRST A MA U 71 - - 4676 Unnamed Lake 26 16-Sep-10 MT BRST U UN U 45 - - 4677 Unnamed Lake 26 16-Sep-10 MT BRST A MA U 56 - - 4678 Unnamed Lake 26 16-Sep-10 MT BRST A MA U 51 - - 4679 Unnamed Lake 26 16-Sep-10 MT BRST A MA U 53 - - 4680 Unnamed Lake 26 16-Sep-10 MT BRST U UN U 48 - - 4681 Unnamed Lake 26 16-Sep-10 MT BRST A MA U 68 - - 4682 Unnamed Lake 26 16-Sep-10 MT BRST A MA U 54 - - 4683 Unnamed Lake 26 16-Sep-10 MT BRST J IM U 39 - - 4684 Unnamed Lake 26 16-Sep-10 MT BRST J IM U 38 - - 4685 Unnamed Lake 26 16-Sep-10 MT FNDC A MA U 41 - - 4686 Unnamed Lake 26 16-Sep-10 MT BRST A MA U 56 - - 4687 Unnamed Lake 26 16-Sep-10 MT BRST A MA U 51 - - 4688 Unnamed Lake 26 16-Sep-10 MT FNDC A MA U 51 - - 4689 Unnamed Lake 26 16-Sep-10 MT FNDC J IM U 35 - - 4690 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 55 - - 4691 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 52 - - 4692 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 65 - - 4693 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 68 - - 4694 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 55 - - 4695 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 60 - - 4696 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 64 - - 4697 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 55 - - 4698 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 67 - - 4699 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 51 - - 4700 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U 78 - - 4701 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U 65 - - 4702 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U 54 - - 4703 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 70 - - 4704 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 65 - - 4705 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 45 - - 4706 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U 57 - - 4707 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 50 - - 4708 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 55 - - 4709 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 55 - - 4710 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 60 - -




4711 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 45 - - 4712 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 66 - - 4713 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 62 - - 4714 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 60 - - 4715 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 54 - - 4716 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 53 - - 4717 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 52 - - 4718 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 50 - - 4719 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 49 - - 4720 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 70 - - 4721 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 53 - - 4722 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U 59 - - 4723 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 48 - - 4724 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 50 - - 4725 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 45 - - 4726 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 50 - - 4727 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 50 - - 4728 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 51 - - 4729 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 60 - - 4730 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U 60 - - 4731 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 70 - - 4732 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 70 - - 4733 Unnamed Lake 26 2-Jun-11 MT BRST U UN U 52 - - 4734 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 4735 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 4736 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 4737 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 4738 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 4739 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 4740 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 4741 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 4742 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 4743 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 4744 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 4745 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 4746 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 4747 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 4748 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - -




5015 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5016 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5017 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5018 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5019 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5020 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5021 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5022 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5023 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5024 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5025 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5026 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5027 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5028 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5029 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5030 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5031 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5032 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5033 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5034 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5035 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5036 Unnamed Lake 26 2-Jun-11 MT BRST U UN U - - - 5037 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5038 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5039 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5040 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5041 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5042 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5043 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5044 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5045 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5046 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5047 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5048 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5049 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5050 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5051 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5052 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - -




5053 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5054 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5055 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5056 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5057 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5058 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5059 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5060 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5061 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5062 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5063 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5064 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5065 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5066 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5067 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5068 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5069 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5070 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5071 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5072 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5073 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5074 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5075 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5076 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5077 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5078 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5079 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5080 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5081 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5082 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5083 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5084 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5085 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5086 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5087 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5088 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5089 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5090 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - -




5205 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5206 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5207 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5208 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5209 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5210 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5211 Unnamed Lake 26 2-Jun-11 MT FNDC U UN U - - - 5212 Unnamed Creek 27 19-Sep-10 BPEF BRST U UN U 68 - - 5213 Unnamed Creek 27 19-Sep-10 BPEF FNDC U UN U 45 - - 5214 Unnamed Creek 27 19-Sep-10 BPEF FNDC U UN U 45 - - 5215 Unnamed Creek 27 19-Sep-10 BPEF BRST U UN U 31 - - 5216 Unnamed Creek 27 19-Sep-10 BPEF FNDC U UN U 42 - - 5217 Unnamed Creek 27 19-Sep-10 BPEF FNDC J IM U 39 - - 5218 Unnamed Creek 27 19-Sep-10 BPEF BRST J IM U 35 - - 5219 Unnamed Creek 27 19-Sep-10 BPEF FNDC U UN U 49 - - 5220 Unnamed Creek 27 19-Sep-10 BPEF BRST U UN U 35 - - 5221 Unnamed Creek 27 19-Sep-10 BPEF FNDC J IM U 43 - - 5222 Unnamed Creek 27 19-Sep-10 BPEF BRST J IM U 25 - - 5223 Unnamed Creek 27 19-Sep-10 MT FNDC U UN U 46 - - 5224 Unnamed Creek 27 19-Sep-10 MT BRST U UN U 50 - - 5225 Unnamed Creek 27 19-Sep-10 MT FNDC U UN U 45 - - 5226 Unnamed Creek 27 19-Sep-10 MT FNDC U UN U 48 - - 5227 Unnamed Creek 27 19-Sep-10 MT FNDC A MA U 52 - - 5228 Unnamed Creek 27 19-Sep-10 MT FNDC U UN U 55 - - 5229 Unnamed Creek 27 19-Sep-10 MT FNDC U UN U 53 - - 5230 Unnamed Creek 27 19-Sep-10 MT FNDC U UN U 55 - - 5231 Unnamed Creek 27 19-Sep-10 MT FNDC U UN U 60 - - 5232 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 60 - - 5233 Unnamed Creek 27 1-Jun-11 MT BRST U UN U 37 - - 5234 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 50 - - 5235 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 45 - - 5236 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 44 - - 5237 Unnamed Creek 27 1-Jun-11 MT BRST U UN U 65 - - 5238 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 73 - - 5239 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 67 - - 5240 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 63 - - 5241 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 60 - - 5242 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 59 - -




5243 Unnamed Creek 27 1-Jun-11 MT BRST U UN U 43 - - 5244 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 50 - - 5245 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 55 - - 5246 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 66 - - 5247 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 65 - - 5248 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 56 - - 5249 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 45 - - 5250 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 60 - - 5251 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 60 - - 5252 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 71 - - 5253 Unnamed Creek 27 1-Jun-11 MT BRST U UN U 65 - - 5254 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 59 - - 5255 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 47 - - 5256 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 46 - - 5257 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 66 - - 5258 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 57 - - 5259 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 55 - - 5260 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 57 - - 5261 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 58 - - 5262 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 57 - - 5263 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 64 - - 5264 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 60 - - 5265 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 63 - - 5266 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 62 - - 5267 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 73 - - 5268 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 50 - - 5269 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 65 - - 5270 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 52 - - 5271 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 60 - - 5272 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 60 - - 5273 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 44 - - 5274 Unnamed Creek 27 1-Jun-11 MT BRST U UN U 49 - - 5275 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 55 - - 5276 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 44 - - 5277 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 62 - - 5278 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 55 - - 5279 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 60 - - 5280 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 55 - -




5281 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 60 - - 5282 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 56 - - 5283 Unnamed Creek 27 1-Jun-11 MT FNDC U UN U 50 - - 5284 Unnamed Creek 28 21-Sep-10 MT BRST A MA U 58 - - 5285 Unnamed Creek 28 21-Sep-10 MT BRST U UN U 48 - - 5286 Unnamed Creek 28 1-Jun-11 MT BRST U UN U 50 - - 5287 Unnamed Creek 28 1-Jun-11 MT BRST U UN U 76 - - 5288 Unnamed Creek 28 1-Jun-11 MT BRST U UN U 44 - - 5289 Unnamed Creek 28 1-Jun-11 MT BRST U UN U 71 - - 5290 Unnamed Creek 28 1-Jun-11 MT BRST U UN U 45 - - 5291 Unnamed Creek 28 1-Jun-11 MT BRST U UN U 46 - - 5292 Unnamed Creek 28 1-Jun-11 MT BRST U UN U 67 - - 5293 Unnamed Creek 28 1-Jun-11 MT BRST U UN U 43 - - 5294 Unnamed Creek 28 1-Jun-11 MT BRST U UN U 53 - - 5295 Unnamed Creek 28 1-Jun-11 MT BRST U UN U 45 - - 5296 Unnamed Creek 28 1-Jun-11 MT BRST U UN U 43 - - 5297 Unnamed Creek 28 1-Jun-11 MT BRST U UN U 44 - - 5298 Unnamed Creek 28 1-Jun-11 MT BRST U UN U 50 - - 5299 Unnamed Creek 29 21-Sep-10 BPEF WHSC J IM U 68 - - 5300 Unnamed Creek 29 21-Sep-10 BPEF BRST A MA U 43 - - 5301 Unnamed Creek 29 22-Sep-10 MT WHSC U UN U 81 - - 5302 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 61 - - 5303 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 63 - - 5304 Unnamed Creek 29 22-Sep-10 MT BRST J IM U 41 - - 5305 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 42 - - 5306 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 55 - - 5307 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 56 - - 5308 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 45 - - 5309 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 52 - - 5310 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 54 - - 5311 Unnamed Creek 29 22-Sep-10 MT WHSC J IM U 84 - - 5312 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 63 - - 5313 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 54 - - 5314 Unnamed Creek 29 22-Sep-10 MT WHSC J IM U 83 - - 5315 Unnamed Creek 29 22-Sep-10 MT WHSC J IM U 72 - - 5316 Unnamed Creek 29 22-Sep-10 MT WHSC J IM U 74 - - 5317 Unnamed Creek 29 22-Sep-10 MT WHSC U UN U 68 - - 5318 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 62 - -




5319 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 61 - - 5320 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 58 - - 5321 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 49 - - 5322 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 50 - - 5323 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 62 - - 5324 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 69 - - 5325 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 72 - - 5326 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 64 - - 5327 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 61 - - 5328 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 64 - - 5329 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 65 - - 5330 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 58 - - 5331 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 48 - - 5332 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 53 - - 5333 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 45 - - 5334 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 47 - - 5335 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 69 - - 5336 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 52 - - 5337 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 63 - - 5338 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 55 - - 5339 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 47 - - 5340 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 45 - - 5341 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 50 - - 5342 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 58 - - 5343 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 63 - - 5344 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 61 - - 5345 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 46 - - 5346 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 49 - - 5347 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 65 - - 5348 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 57 - - 5349 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 70 - - 5350 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 62 - - 5351 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 52 - - 5352 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 54 - - 5353 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 60 - - 5354 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 72 - - 5355 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 45 - - 5356 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 65 - -




5357 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 61 - - 5358 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 49 - - 5359 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 45 - - 5360 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 40 - - 5361 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 68 - - 5362 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 62 - - 5363 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 64 - - 5364 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 68 - - 5365 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 70 - - 5366 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 55 - - 5367 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 48 - - 5368 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 47 - - 5369 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 63 - - 5370 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 55 - - 5371 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 45 - - 5372 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 52 - - 5373 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 47 - - 5374 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 72 - - 5375 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 55 - - 5376 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 54 - - 5377 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 55 - - 5378 Unnamed Creek 29 22-Sep-10 MT BRST A MA U 61 - - 5379 Unnamed Creek 29 22-Sep-10 MT BRST J IM U 35 - - 5380 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 42 - - 5381 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 45 - - 5382 Unnamed Creek 29 22-Sep-10 MT BRST U UN U 56 - - 5383 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 50 - - 5384 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 45 - - 5385 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 46 - - 5386 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 51 - - 5387 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 50 - - 5388 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 41 - - 5389 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 44 - - 5390 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 67 - - 5391 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 47 - - 5392 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 45 - - 5393 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 50 - - 5394 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 45 - -




5395 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 64 - - 5396 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 54 - - 5397 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 44 - - 5398 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 45 - - 5399 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 45 - - 5400 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 50 - - 5401 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 50 - - 5402 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 54 - - 5403 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 50 - - 5404 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 49 - - 5405 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 65 - - 5406 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 56 - - 5407 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 45 - - 5408 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 52 - - 5409 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 53 - - 5410 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 46 - - 5411 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 50 - - 5412 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 65 - - 5413 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 66 - - 5414 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 43 - - 5415 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 45 - - 5416 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 67 - - 5417 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 49 - - 5418 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 79 - - 5419 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 67 - - 5420 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 45 - - 5421 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 65 - - 5422 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 55 - - 5423 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 47 - - 5424 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 67 - - 5425 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 48 - - 5426 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 48 - - 5427 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 45 - - 5428 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 68 - - 5429 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 50 - - 5430 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 49 - - 5431 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 51 - - 5432 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 49 - -




5433 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 45 - - 5434 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 65 - - 5435 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 49 - - 5436 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 67 - - 5437 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 45 - - 5438 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 60 - - 5439 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 49 - - 5440 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 55 - - 5441 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 53 - - 5442 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 44 - - 5443 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 52 - - 5444 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 65 - - 5445 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 55 - - 5446 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 45 - - 5447 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 65 - - 5448 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 46 - - 5449 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 46 - - 5450 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 40 - - 5451 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 65 - - 5452 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 50 - - 5453 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 53 - - 5454 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 46 - - 5455 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 70 - - 5456 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 45 - - 5457 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 45 - - 5458 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 44 - - 5459 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 47 - - 5460 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 46 - - 5461 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 42 - - 5462 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 48 - - 5463 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 45 - - 5464 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 43 - - 5465 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 50 - - 5466 Unnamed Creek 29 1-Jun-11 MT WHSC U UN U 44 - - 5467 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 45 - - 5468 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 52 - - 5469 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 45 - - 5470 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 55 - -




5471 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 50 - - 5472 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 50 - - 5473 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 65 - - 5474 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 56 - - 5475 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 39 - - 5476 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 47 - - 5477 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 61 - - 5478 Unnamed Creek 29 1-Jun-11 MT BRST U UN U 51 - - 5479 Monday Creek 30 22-Sep-10 MT LKCH A MA U 92 - - 5480 Monday Creek 30 22-Sep-10 MT SPSC A MA U 97 - - 5481 Monday Creek 30 22-Sep-10 MT BRST A MA U 64 - - 5482 Monday Creek 30 22-Sep-10 MT WHSC J IM U 56 - - 5483 Monday Creek 30 1-Jun-11 MT BRST U UN U 48 - - 5484 Monday Creek 30 1-Jun-11 MT BRST U UN U 62 - - 5485 Monday Creek 30 1-Jun-11 MT BRST U UN U 49 - - 5486 Monday Creek 30 1-Jun-11 MT BRST U UN U 46 - - 5487 Monday Creek 30 1-Jun-11 MT BRST U UN U 47 - - 5488 Monday Creek 30 1-Jun-11 MT BRST U UN U 48 - -

Notes: 1 Gear: BEF = boat electrofishing, BPEF = backpack electrofishing, GN = gillnet, MT = minnow trap 2 Species: refer to Table H5-1 for species names and codes 3 Stage: J = juvenile, A = adult, IM = immature, U = unidentified 4 Maturity: IM = immature, MA = mature, U = unknown 5 Sex: M = male, F = female, U = unknown 6 K Factor = (Weight⋅105) / (Length3)



Table H5-3: Number and Catch-Per-Unit-Effort, by Species, for Fish Captured at Fish Inventory Sites within the Devon Pike ALSA, 2010-2011

Site Water Body Seas.1 Meth.2 Effort BRST FNDC FTMN LKCH LKWH LNSC NRPK PRDC SPSC WHSC YLPR TOTAL 1 Unnamed

Creek SP MT 22.00 - - - - - - - - - - - 0 FA BPEF 610 s - - - - - - - - - - - 0 FA MT 69.00 - - - - - - - - - - - 0

5 Unnamed Creek

SP MT 16.50 11 (0.67) - - - - - - 60 (3.64) - - - 71 (4.30) FA BPEF 413 s - - - - - - - - - - - 0 FA MT 12.50 8 (0.64) 188 (15.04) - - - - - - - 2 (0.16) - 198 (15.84)

6 Unnamed Creek

SP MT 47.50 - - - - - - - - - 1 (0.02) - 1 (0.02) FA BPEF 385 s - - - - - - 1 (0.26) - - 1 (0.26) - 2 (0.52) FA MT 70.50 - - - - - - - - - - - 0

7 Hay Lake SP GN 6.43 - - - - - - 42 (6.53) - - - - 42 (6.53) SP MT 17.05 - - - - - - - - - - - 0 SM BEF 550 s - - - - - - 1 (0.18) - - - - 1 (0.18) SM GN 4.00 - - - - - - 16 (4.00) - - 1 (0.25) - 17 (4.25) SM MT 138.00 - - - - - - - - - - - 0 FA BEF 947 s - - - - - - 4 (0.42) - - - - 4 (0.42) FA GN 1.98 - - - - - - 5 (2.52) - - - - 5 (2.52) FA MT 71.00 - - - - - - - - - - - 0

8 Unnamed Creek

SP MT 12.05 5 (0.41) - - - - - - - - 4 (0.33) - 9 (0.75) FA BPEF 393 s - - - - - - - - - - - 0 FA MT 64.50 1 (0.02) - - - - - - - - - - 1 (0.02)

9 Kirby Lake SP MT 89.00 - - - - - - - - - - 29 (0.33) 29 (0.33) SM BEF 1300 s - - - - - - - - - - 5 (0.38) 5 (0.38)

9 Kirby Lake SM GN 4.33 - - - - 7 (1.62) - - - - 6 (1.38) 119 (27.46) 132 (30.48) SM MT 73.40 - - - - - - - - - - 13 (0.18) 13 (0.18) FA BEF 900 s - - - - - - - - - 5 (0.56) 13 (1.44) 18 (2.00) FA GN 7.75 - - - - 14 (1.81) - 8 (1.03) - - - - 22 (2.84) FA MT 71.00 - - - - - - - - - - - 0

11 Unnamed Creek

SP MT 70.50 1 (0.01) - - - - - - - - - - 0 FA BPEF 332 s - - - - - - - - - - - 0 FA MT 10.33 - - - - - - - - - - - 0

12 Unnamed Lake

SP GN 7.92 - - - - - 17 (2.15) 5 (0.63) - - - - 22 (2.78) SP MT 55.00 - - - - - - - - - - - 0 SM BEF 733 s - - - - - - 5 (0.68) - - - - 5 (0.68) SM GN 10.00 - - - - - - 1 (0.10) - - 3 (0.30) - 4 (0.40) SM MT 128.00 - - - - - - 1 (0.01) - - - - 1 (0.01) FA GN 9.68 - - - - - - - - - 12 (1.24) - 12 (1.24) FA MT 61.50 - - - - - - - - - - - 0




Creek SP MT 85.20 207 (2.43) - - - - - - - - - - 207 (2.43) FA BPEF 440 s 1 (0.23) - - - - - - - - 1 (0.23) - 2 (0.45) FA MT 67.75 13 (0.19) 7 (0.10) - - - - - - - 4 (0.06) - 24 (0.35)

14 Unnamed Creek

SP MT 93.00 - - - - - - - - - - - 0 FA BPEF 443 s - - - - - - - - - - - 0 FA MT 70.50 - - - - - - - - - - - 0

16 Unnamed Creek

SP MT 50.50 20 (0.40) 317 (6.28) 39 (0.77) - - - - 72 (1.43) - - - 448 (8.87) FA BPEF 166 s 2 (1.2) 23 (13.86) - - - - - 3 (1.81) - - - 28 (16.87) FA MT 48.00 5 (0.10) 162 (3.37) - - - - - - - - - 167 (3.48)

17 Unnamed Lake

SP GN 8.08 - - - - - - - - - - - 0 SP MT 48.00 2 (0.04) 424 (8.83) - - - - - - - - - 426 (8.88) SM BEF 650 s - - - - - - - - - - - 0 SM GN 3.98 - - - - - - - - - - - 0 SM MT 20.00 44 (2.20) 327 (16.35) - - - - - - - - - 371 (18.55) FA BEF 8211 s 17 (0.21) 39 (0.47) - - - - - - - - - 56 (0.68) FA MT 72.00 86 (1.19) 581 (8.07) - - - - - - - - - 667 (9.26)

18 Unnamed Creek

SP MT 47.25 76 (1.61) - 10 (0.21) - - - - 560 (11.85) - - - 646 (13.67) FA BPEF 467 s 9 (1.93) 4 (0.86) - - - - - - - - - 13 (2.78) FA MT 24.50 9 (0.37) 9 (0.37) - - - - - - - - - 18 (0.73)

19 Sand River SP MT 51.00 - - - - - - - 1 (0.02) - - - 1 (0.02) FA BPEF 543 s - - - - - - - - - - - 0 FA MT 1.33 - - - - - - - - - - - 0

20 Sand River SP MT 50.10 - - - - - - - - - - - 0 SM BPEF 1822 s - - - - - - - 5 (0.27) - - - 5 (0.27) SM MT 55.50 - - - - - - - - - - - 0 FA BPEF 382 s - - - - - - - - - - - 0 FA MT 44.60 - - - - - - 1 (0.02) - - - - 1 (0.02)

21 Unnamed Creek

SP MT 60.00 8 (0.13) - - - - - - 374 (6.23) - - - 382 (6.37) FA BPEF 432 s 1 (0.23) 5 (1.16) - - - - - - - - - 6 (1.39) FA MT 54.00 5 (0.09) 23 (0.43) - - - - - - - - - 28 (0.52)

22 Sand River SP MT 48.90 3 (0.06) - - - - - - 178 (3.64) - 1 (0.02) - 182 (3.72) FA BPEF 924 s - 8 (0.87) - - - - - - 1 (0.11) - - 9 (0.97) FA MT 57.00 - 20 (0.35) - - - - - - - - - 20 (0.35)

23 Unnamed Creek

SP MT 78.75 20 (0.25) - - - - - - 7 (0.09) - 1 (0.01) - 28 (0.36) FA BPEF 444 s 1 (0.23) - - - - - - - - - - 1 (0.23) FA MT 65.25 1 (0.02) 1 (0.02) - - - - - - - - - 2 (0.03)

24 Unnamed Creek

SP MT 5.00 6 (1.20) 5 (1.00) - - - - - - - - - 11 (2.20) FA BPEF 403 s 5 (1.24) - - - - - - - - - - 5 (1.24) FA MT 4.50 - - - - - - - - - - - 0




Lake SP MT 16.00 157 (9.81) - 45 (2.81) - - - - - - - - 202 (12.63) FA BEF 689 s 7 (1.02) - - - - - - 1 (0.15) - - - 8 (1.16) FA GN 4.35 - - - - - - - - - - - 0 FA MT 17.25 28 (1.62) 2 (0.12) 7 (0.41) - - - - - - - - 37 (2.14)

26 Unnamed Lake

SP GN 1.50 - - - - - - - - - - - 0 SP MT 8.00 341 (42.63) 181 (22.63) - - - - - - - - - 522 (65.25) FA BEF 563 s 31 (5.51) 20 (3.55) - - - - - - - - - 51 (9.06) FA MT 19.50 17 (0.87) 5 (0.26) - - - - - - - - - 22 (1.13)

27 Unnamed Creek

SP MT 3.00 5 (1.67) 47 (15.67) - - - - - - - - - 52 (17.33) FA BPEF 339 s 5 (1.47) 6 (1.77) - - - - - - - - - 11 (3.24) FA MT 14.00 1 (0.07) 8 (0.57) - - - - - - - - - 9 (0.64)

28 Unnamed Creek

SP MT 132.00 13 (0.10) - - - - - - - - - - 13 (0.10) FA BPEF 376 s - - - - - - - - - - - 0 FA MT 4.00 2 (0.50) - - - - - - - - - - 2 (0.50)

29 Unnamed Creek

SP MT 75.75 95 (1.25) - - - - - - - - 1 (0.01) - 96 (1.27) FA BPEF 363 s 1 (0.28) - - - - - - - - 1 (0.28) - 2 (0.55) FA MT 64.75 76 (1.17) - - - - - - - - 6 (0.09) - 82 (1.27)

30 Monday Creek SP MT 144.75 6 (0.04) - - - - - - - - - - 6 (0.04) FA BPEF 479 s - - - - - - - - - - - 0 FA MT 59.1 1 (0.02) - - 1 (0.02) - - - - 1 (0.02) 1 (0.02) - 4 (0.07)

31 Unnamed Creek

FA BPEF 442 s - - - - - - - - - - - 0

Notes: 1 Season: SP = spring, SM = summer, FA = fall 2 Method: BEF = boat electrofishing, BPEF = backpack electrofishing, GN = gillnet, MT = minnow trap CPUE is provided in brackets BEF, BPEF - CPUE units are fish per 100 seconds of electrofishing MT, GN - CPUE units are fish per net-hour



Table H5-4: Mean Length, Weight, and Condition of Fish Captured Within the Devon Pike ALSA, 2010-2011

Species Number Length (mm) Weight (g) K-Factor

n mean SD n mean SD n mean SDBRST 1353 609 54.1 10.5 122 1.0 0.6 122 0.5 0.2 FNDC 2412 679 56.4 15.4 129 2.1 1.3 129 1.1 0.3 FTMN 101 36 50.2 6.9 11 1.1 1.0 11 0.7 0.4 LKCH 1 1 92.0 - - - - - - - LKWH 21 21 320.2 131.2 - - - - - - LNSC 17 17 442.1 48.9 - - - - - - NRPK 90 90 460.9 129.0 2 23.1 20.2 2 0.7 0.2 PRDC 1261 230 54.8 21.1 161 2.4 2.2 161 0.7 0.3 SPSC 2 2 104.5 10.6 - - - - - - WHSC 51 50 208.5 167.9 8 3.8 3.7 8 1.0 0.2 YLPR 179 179 116.1 33.3 26 7.3 9.4 26 1.2 0.3

Appendix H6

Benthic Invertebrate Raw Data



Table H6-1: Benthic Invertebrate Data, Devon Pike EIA, 2010

TAXON Stage Site A3 Site A5

Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max BRYOZOA Bryozoa indet. colony 0 0 0 0 0 0 - - - - - 0 0 0 0 0 0 - - - - - NEMATODA Nematoda indet. A 43 0 0 0 43 17 - - - - - 130 87 0 130 0 70 - - - - - CNIDARIA Hydrozoa Hydra sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 ANNELIDA Oligochaeta Oligochaeta indet. J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Enchytraeidae Enchytraeidae indet. J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Enchytraeidae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Henlea sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Lumbriculidae Lumbriculidae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Lumbriculus variegatus A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Naididae Naididae indet. J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Chaetogaster diaphanus A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Naididae indet. Group 2 Arcteonais lomondi A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Pristina leidyi A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Pristina sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Stylaria lacustris A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Naidadae indet. Group 3 Dero nivea A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Dero sp. J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Dero sp. A 43 0 0 0 0 9 1.72 19 9 0 43 0 0 0 0 0 0 0.00 0 0 0 0 Naididae indet. Group 4 Slavina appendiculata A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Vejdovskyella comata J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Vejdovskyella comata A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Vejdovskyella sp. J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Naididae indet. Group 5 Nais communis A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Nais pardalis A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Nais simplex A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Nais variabilis J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Nais variabilis A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Specaria josinae A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0




Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Tubificoid Naididae Tubificoid Naididae indet. J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Tubificoid Naididae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Tubificoid Naididae indet. Group 2 J 0 0 43 43 0 17 3.45 24 11 0 43 0 0 0 0 0 0 0.00 0 0 0 0 Tubificoid Naididae indet. Group 2 A 0 43 0 0 0 9 1.72 19 9 0 43 43 43 174 43 0 61 10.14 66 29 0 174 Tubificoid Naididae indet. Group 3 Aulodrilus pigueti A 0 43 87 43 43 43 8.62 31 14 0 87 0 0 0 0 0 0 0.00 0 0 0 0 Tubificoid Naididae indet. Group 5 J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Aulodrilus limnobius A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Limnodrilus udekemeanus J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Limnodrilus udekemeanus A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Limnodrilus sp. J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Limnodrilus sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0

Total Oligochaeta 43 87 130 87 43 78 15.52 36 16 43 130 43 43 174 43 0 61 10.14 66 29 0 174 Hirudinea Erpobdellidae Erpobdella sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Nephelopsis sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Glossiphoniidae Helobdella stagnalis A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Helobdellasp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0

Total Hirudinea 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 MOLLUSCA Bivalvia Sphaeriidae Sphaeriidae indet. J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 87 0 0 17 2.90 39 17 0 87 Pisidium sp. A 87 0 174 0 0 52 10.34 78 35 0 174 43 43 43 43 43 43 7.25 0 0 43 43 Sphaerium sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0

Total Bivalvia 87 0 174 0 0 52 10.34 78 35 0 174 43 43 130 43 43 61 10.14 39 17 43 130 Gastropoda Lymnaeidae Lymnaeidae indet. J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Planorbidae Planorbidae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Ancylidae Ferissia sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Valvatidae Valvata sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Valvata sincera sincera A 0 0 43 0 0 9 1.72 19 9 0 43 0 0 0 0 0 0 0.00 0 0 0 0

Total Gastropoda 0 0 43 0 0 9 1.72 19 9 0 43 0 0 0 0 0 0 0.00 0 0 0 0 TARDIGRADA Tardigrada indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0




Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max ARTHROPODA ARACHNIDA Acari Hydrachnidia Hydrachnidia indet. J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hydrachnidia indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hygrobatidae Hygrobatidae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Lebertiidae Lebertia sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Pionidae Forelia sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Piona sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Sperchontidae Sperchonopsis sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Unionicolidae Unionicola sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Oribatida Oribatida indet. J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Oribatida indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hydrozetidae Hydrozetes sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0

Total Acari 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 CRUSTACEA Copepoda Calanoida Calanoida indet. cpp 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Diaptomidae indet. A 43 130 87 130 87 96 18.97 36 16 43 130 43 0 0 0 0 9 1.45 19 9 0 43 Cyclopoida Cyclopoida indet. cpp 0 0 0 0 0 0 0.00 0 0 0 0 0 0 43 0 0 9 1.45 19 9 0 43 Eucyclops sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Macrocyclops sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 43 0 9 1.45 19 9 0 43 Harpacticoida Harpacticoida indet. cpp 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Canthocamptidae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0

Total Copepoda 43 130 87 130 87 96 18.97 36 16 43 130 43 0 43 43 0 26 4.35 24 11 0 43 Ostracoda Podocopida indet. J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Podocopida indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Candona sp. A 0 0 87 43 87 43 8.62 43 19 0 87 0 130 43 0 130 61 10.14 66 29 0 130 Cypria sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0

Total Ostracoda 0 0 87 43 87 43 8.62 43 19 0 87 0 130 43 0 130 61 10.14 66 29 0 130




Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Cladocera Chydoridae Chydoridae indet. J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Chydoridae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Chydorus sphaericus A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Daphnidae Daphnidae indet. A 43 87 43 87 87 70 13.79 24 11 43 87 0 0 43 0 0 9 1.45 19 9 0 43 Daphnia sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Macrothricidae Ilyocryptus spinifer A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Sididae Sididae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Sida crystallina A 0 0 0 0 0 0 0.00 0 0 0 0 0 43 0 0 0 9 1.45 19 9 0 43

Total Cladocera 43 87 43 87 87 70 13.79 24 11 43 87 0 43 43 0 0 17 2.90 24 11 0 43 Tanaidacea Leptochelia dubia A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Isopoda Isopoda indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Amphipoda Gammaridae Gammarus sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hyalellidae Hyalella sp. J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hyalella sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hyalella azteca A 0 43 0 0 0 9 1.72 19 9 0 43 0 0 0 0 0 0 0.00 0 0 0 0

Total Amphipoda 0 43 0 0 0 9 1.72 19 9 0 43 0 0 0 0 0 0 0.00 0 0 0 0 TOTAL NON-INSECT

(excluding Bryozoa and Nematoda) 217 348 565 348 304 357 70.69 128 57 217 565 130 261 435 130 174 226 37.68 128 57 130 435

INSECTA Insecta indet. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Insecta indet. P 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Collembola Collembola indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Entomobryidae Entomobryidae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Isotomidae Isotomidae indet. A 0 0 0 0 43 9 1.72 19 9 0 43 0 0 0 0 0 0 0.00 0 0 0 0 Ephemeroptera Ephemeroptera indet. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Baetidae Baetidae indet. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Baetis sp. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Caenidae




Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Caenis sp. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Ephemerellidae Ephemerellidae indet. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Leptophlebiidae Paraleptophlebia sp. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Paraleptophlebia debilis N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0

Total Ephemeroptera 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Odonata Anisoptera Corduliidae Cordulia sp. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Epitheca sp. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Libellulidae Libellulidae indet. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hemiptera Corixidae Corixidae indet. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Plecoptera Plecoptera indet. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Nemouridae Nemouridae indet. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0

Total Plecoptera 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Trichoptera Trichoptera indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Brachycentridae Brachycentridae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Brachycentrus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Glossosomatidae Glossosoma sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hydropsychidae Hydropsychidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hydropsyche sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hydroptilidae Hydroptilidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Oxyethira sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Lepidostomatidae Lepidostomatidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Leptoceridae Leptoceridae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Mystacides sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Oecetis sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Limnephilidae Limnephilini indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0




Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Nemotaulius sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Phryganeidae Phryganea sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0

Total Trichoptera 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Lepidoptera Lepidoptera indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Coleoptera Coleoptera indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Dytiscidae Hydroporus sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Haliplidae Haliplus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Elmidae Elmidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Optioservus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0

Total Coleoptera 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Diptera Diptera indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Diptera indet. P 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Ceratopogonidae Ceratopogonidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Atrichopogon sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Bezzia/Palpomyia sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Culicoides sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Dasyhelea sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Probezzia sp. L 0 43 0 0 0 9 1.72 19 9 0 43 0 0 0 0 0 0 0.00 0 0 0 0

Total Ceratopogonidae 0 43 0 0 0 9 1.72 19 9 0 43 0 0 0 0 0 0 0.00 0 0 0 0 Chaoboridae Chaoborus sp. L 0 43 0 0 0 9 1.72 19 9 0 43 43 261 435 174 0 183 30.43 175 78 0 435 Chironomidae Chironomidae indet. L 0 87 0 0 43 26 5.00 39 17 0 87 0 0 0 0 0 0 0.00 0 0 0 0 Chironominae Chironomini Chironomini indet. L 0 43 87 0 0 26 5.17 39 17 0 87 0 0 0 0 0 0 0.00 0 0 0 0 Chironomus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 304 174 174 217 174 28.99 111 50 0 304 Cladopelma sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Cryptochironomus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Dicrotendipes sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 43 0 0 9 1.45 19 9 0 43 Endochironomus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Microtendipes sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Paralauterborniella sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Phaenopsectra sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Polypedilum (pentapedilum) sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0




Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Polypedilum (polypedilum) sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Robackia sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Tanytarsini Tanytarsini indet. L 0 304 0 0 0 61 12.07 136 61 0 304 0 0 0 0 43 9 1.45 19 9 0 43 Cladotanytarsus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Micropsectra sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Paratanytarsus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Stempellinella sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Tanytarsus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0

Total Chironominae 0 348 87 0 0 87 17.24 151 67 0 348 0 304 217 174 261 191 31.88 117 53 0 304 Orthocladiinae Orthocladiinae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Corynoneura sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Cricotopus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Eukiefferiella sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Heterotanytarsus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Heterotrissocladius sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Orthocladius sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Psectrocladius sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Synorthocladius sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Thienemanniella sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0

Total Orthocladiinae 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Tanypodinae Tanypodinae indet. L 0 43 0 0 0 9 1.72 19 9 0 43 0 0 0 0 0 0 0.00 0 0 0 0 Coelotanypodini Clinotanypus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Pentaneurini Ablabesmyia sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Thienemannimyia sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Procladiini Procladius sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0

Total Tanypodinae 0 43 0 0 0 9 1.72 19 9 0 43 0 0 0 0 0 0 0.00 0 0 0 0 Total Chironomidae 0 478 87 0 43 122 24.14 203 91 0 478 0 304 217 174 261 191 31.88 117 53 0 304

Empididae Empididae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hemerodromia sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Metachela/Chelifera sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Simuliidae Simuliidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Tabanidae Tabanidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Chrysops sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Silvius sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0




Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Tipulidae Tipulidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Dicranota sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hexatoma sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0

Total Diptera 0 565 87 0 43 139 27.59 241 108 0 565 43 565 652 348 261 374 62.32 243 109 43 652 TOTAL INSECTA 0 565 87 0 87 148 29.31 237 106 0 565 43 565 652 348 261 374 62.32 243 109 43 652

TOTAL ABUNDANCE (excluding Bryozoa and Nematoda) 217 913 652 348 391 504 278 124 217 913 174 826 1087 478 435 600 358 160 174 1087



Table H6-1: Continued (Site A7 and Site B1)

TAXON Stage Site A7 Site B1








Total Ostracoda 87 261 261 174 0 157 0.43 113 51 0 261 0 0 0 0 0 0 0.00 0 0 0 0






Total Amphipoda 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 TOTAL NON-INSECTA (excluding

Bryozoa and Nematoda) 1043 15000 8348 7652 3130 7035 19.39 5401 2415 1043 15000 87 174 43 43 130 96 47.83 57 25 43 174

INSECTA Insecta indet. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Insecta indet. P 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Collembola Collembola indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Entomobryidae Entomobryidae indet. A 0 0 0 87 0 17 0.05 39 17 0 87 0 0 0 0 0 0 0.00 0 0 0 0 Isotomidae Isotomidae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Ephemeroptera Ephemeroptera indet. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Baetidae Baetidae indet. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Baetis sp. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0




Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Caenidae Caenis sp. N 0 0 130 87 0 43 0.12 61 27 0 130 0 0 0 0 0 0 0.00 0 0 0 0 Ephemerellidae Ephemerellidae indet. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Leptophlebiidae Paraleptophlebia sp. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Paraleptophlebia debilis N 0 130 130 0 0 52 0.14 71 32 0 130 0 0 0 0 0 0 0.00 0 0 0 0


Total Plecoptera 0 0 0 0 0 0 0.00 0 0 0 0 0 43 0 0 0 9 4.35 19 9 0 43 Trichoptera Trichoptera indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Brachycentridae Brachycentridae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Brachycentrus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Glossosomatidae Glossosoma sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hydropsychidae Hydropsychidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hydropsyche sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hydroptilidae Hydroptilidae indet. L 87 0 0 0 0 17 0.05 39 17 0 87 0 0 0 0 0 0 0.00 0 0 0 0 Oxyethira sp. L 0 0 130 0 0 26 0.07 58 26 0 130 0 0 0 0 0 0 0.00 0 0 0 0 Lepidostomatidae Lepidostomatidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Leptoceridae Leptoceridae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Mystacides sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Oecetis sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0




Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Limnephilidae Limnephilini indet. L 0 130 0 0 0 26 0.07 58 26 0 130 0 0 0 0 0 0 0.00 0 0 0 0 Nemotaulius sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Phryganeidae Phryganea sp. L 0 0 130 0 0 26 0.07 58 26 0 130 0 0 0 0 0 0 0.00 0 0 0 0



Total Ceratopogonidae 2522 783 3913 783 522 1704 4.70 1470 657 522 3913 0 0 0 0 0 0 0.00 0 0 0 0 Chaoboridae Chaoborus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Chironomidae Chironomidae indet. L 2957 1696 261 0 0 983 2.71 1309 586 0 2957 0 43 0 0 0 9 4.35 19 9 0 43 Chironominae Chironomini Chironomini indet. L 3913 10957 12130 8696 12000 9539 26.29 3433 1535 3913 12130 0 0 0 0 0 0 0.00 0 0 0 0 Chironomus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Cladopelma sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Cryptochironomus sp. L 783 0 0 0 0 157 0.43 350 157 0 783 0 0 0 0 0 0 0.00 0 0 0 0 Dicrotendipes sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Endochironomus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Microtendipes sp. L 87 261 130 0 0 96 0.26 108 48 0 261 0 0 0 0 0 0 0.00 0 0 0 0 Paralauterborniella sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0




Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Phaenopsectra sp. L 435 0 522 522 0 296 0.81 272 122 0 522 0 0 0 0 0 0 0.00 0 0 0 0 Polypedilum (pentapedilum) sp. L 0 0 0 174 0 35 0.10 78 35 0 174 0 0 0 0 0 0 0.00 0 0 0 0 Polypedilum (polypedilum) sp. L 870 2609 2609 1652 522 1652 4.55 964 431 522 2609 0 0 0 0 43 9 4.35 19 9 0 43 Robackia sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 217 87 61 30.43 95 43 0 217 Tanytarsini Tanytarsini indet. L 15217 7174 9261 5652 10435 9548 26.31 3668 1640 5652 15217 0 0 0 0 0 0 0.00 0 0 0 0 Cladotanytarsus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Micropsectra sp. L 2609 1435 652 696 522 1183 3.26 874 391 522 2609 0 0 0 0 0 0 0.00 0 0 0 0 Paratanytarsus sp. L 0 783 652 0 174 322 0.89 371 166 0 783 0 0 0 0 0 0 0.00 0 0 0 0 Stempellinella sp. L 0 0 130 174 0 61 0.17 85 38 0 174 0 0 0 0 0 0 0.00 0 0 0 0 Tanytarsus sp. L 435 130 261 261 174 252 0.69 117 52 130 435 0 0 0 0 0 0 0.00 0 0 0 0




Empididae Empididae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hemerodromia sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Metachela/Chelifera sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 43 0 0 0 9 4.35 19 9 0 43 Simuliidae Simuliidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Tabanidae Tabanidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0




Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Chrysops sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Silvius sp. L 0 130 0 0 0 26 0.07 58 26 0 130 0 0 0 0 0 0 0.00 0 0 0 0 Tipulidae Tipulidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Dicranota sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hexatoma sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0





Table H6-1: Continued (Site B4 and Site B11)

TAXON Stage Site B4 Site B11







Total Hirudinea 75 0 0 0 0 15 0.07 33 15 0 75 87 0 0 0 43 26 0.37 39 17 0 87 MOLLUSCA Bivalvia Sphaeriidae Sphaeriidae indet. J 447 130 174 217 87 211 1.03 141 63 87 447 1304 783 1435 913 2348 1357 19.14 616 275 783 2348 Pisidium sp. A 745 130 174 0 43 219 1.07 302 135 0 745 522 435 696 609 1261 704 9.94 326 146 435 1261 Sphaerium sp. A 224 783 609 304 0 384 1.88 312 139 0 783 0 0 0 0 0 0.00 0 0 0 0

Total Bivalvia 1416 1043 957 522 130 814 3.98 497 222 130 1416 1826 1217 2130 1522 3609 2061 29.08 930 416 1217 3609 Gastropoda Lymnaeidae Lymnaeidae indet. J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Planorbidae Planorbidae indet. A 224 913 348 174 174 366 1.79 314 140 174 913 0 0 0 0 0 0 0.00 0 0 0 0 Ancylidae Ferissia sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Valvatidae Valvata sp. A 0 0 0 0 0 0 0.00 0 0 0 0 87 43 87 174 43 87 1.23 53 24 43 174 Valvata sincera sincera A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0





Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max ARTHROPODA ARACHNIDA Acari Hydrachnidia Hydrachnidia indet. J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hydrachnidia indet. A 75 130 87 304 43 128 0.63 103 46 43 304 0 0 0 0 0 0 0.00 0 0 0 0 Hygrobatidae Hygrobatidae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Lebertiidae Lebertia sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Pionidae Forelia sp. A 75 0 87 0 0 32 0.16 44 20 0 87 0 0 0 0 0 0.00 0 0 0 0 Piona sp. A 0 0 0 0 0 0 0.00 0 0 0 0 43 43 43 0 0 26 0.37 24 11 0 43 Sperchontidae Sperchonopsis sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Unionicolidae Unionicola sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 43 0 0 9 0.12 19 9 0 43 Oribatida Oribatida indet. J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Oribatida indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hydrozetidae Hydrozetes sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0

Total Acari 149 130 174 304 43 160 0.78 94 42 43 304 43 43 87 0 0 35 0.49 36 16 0 87 CRUSTACEA Copepoda Calanoida Calanoida indet. cpp 0 0 0 0 0 0 0.00 0 0 0 0 43 43 261 130 261 148 2.09 109 49 43 261 Diaptomidae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Cyclopoida Cyclopoida indet. cpp 0 1174 0 43 43 252 1.23 516 231 0 1174 130 87 43 174 174 122 1.72 57 25 43 174 Eucyclops sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Macrocyclops sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Harpacticoida Harpacticoida indet. cpp 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 43 0 9 0.12 19 9 0 43 Canthocamptidae indet. A 298 522 0 87 0 181 0.89 226 101 0 522 0 0 0 0 0 0 0.00 0 0 0 0

Total Copepoda 298 1696 0 130 43 434 2.12 715 320 0 1696 174 130 304 348 435 278 3.93 125 56 130 435 Ostracoda Podocopida indet. J 0 0 0 0 0 0 0.00 0 0 0 0 43 0 130 0 0 35 0.49 57 25 0 130 Podocopida indet. A 0 0 0 0 0 0 0.00 0 0 0 0 87 0 174 43 261 113 1.60 105 47 0 261 Candona sp. A 75 261 87 0 0 84 0.41 107 48 0 261 0 0 0 0 0 0.00 0 0 0 0 Cypria sp. A 298 522 174 43 217 251 1.23 177 79 43 522 0 0 0 0 0 0.00 0 0 0 0

Total Ostracoda 373 783 261 43 217 335 1.64 277 124 43 783 130 0 304 43 261 148 2.09 133 59 0 304




Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Cladocera Chydoridae Chydoridae indet. J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 43 87 0 26 0.37 39 17 0 87 Chydoridae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Chydorus sphaericus A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Daphnidae Daphnidae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Daphnia sp. A 0 0 0 0 0 0 0.00 0 0 0 0 217 217 217 478 652 357 5.03 200 90 217 652 Macrothricidae Ilyocryptus spinifer A 75 652 0 174 0 180 0.88 273 122 0 652 0 0 0 0 0 0.00 0 0 0 0 Sididae Sididae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Sida crystallina A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0

Total Cladocera 75 652 0 174 0 180 0.88 273 122 0 652 217 217 261 565 652 383 5.40 209 94 217 652 Tanaidacea Leptochelia dubia A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 43 9 0.12 19 9 0 43 Isopoda Isopoda indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Amphipoda Gammaridae Gammarus sp. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hyalellidae Hyalella sp. J 0 0 0 0 0 0 0.00 0 0 0 0 0 0 87 0 43 26 0.37 39 17 0 87 Hyalella sp. A 0 0 0 0 0 0 0.00 0 0 0 0 696 1261 565 1217 1174 983 13.87 326 146 565 1261 Hyalella azteca A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0



INSECTA Insecta indet. N 0 0 0 0 0 0 0.00 0 0 0 0 43 0 0 0 0 9 0.12 19 9 0 43 Insecta indet. P 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Collembola Collembola indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Entomobryidae Entomobryidae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Isotomidae Isotomidae indet. A 0 0 87 0 43 26 0.13 39 17 0 87 43 0 0 0 0 9 0.12 19 9 0 43 Ephemeroptera Ephemeroptera indet. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Baetidae Baetidae indet. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Baetis sp. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 43 0 0 9 0.12 19 9 0 43 Caenidae




Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Caenis sp. N 149 391 261 0 696 299 1.46 264 118 0 696 0 43 0 43 43 26 0.37 24 11 0 43 Ephemerellidae Ephemerellidae indet. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Leptophlebiidae Paraleptophlebia sp. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Paraleptophlebia debilis N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0










Empididae Empididae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hemerodromia sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Metachela/Chelifera sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Simuliidae Simuliidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Tabanidae Tabanidae indet. L 0 0 0 0 43 9 0.04 19 9 0 43 0 0 0 0 0 0 0.00 0 0 0 0




Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Chrysops sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Silvius sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Tipulidae Tipulidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Dicranota sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Hexatoma sp. L 0 0 87 0 0 17 0.08 39 17 0 87 0 0 0 0 0 0 0.00 0 0 0 0





Table H6-1: Continued (Site B14 and Site B17)









Total Ostracoda 783 522 261 0 835 480 2.50 353 158 0 835 0 24 0 0 0 5 0.05 11 5 0 24








INSECTA Insecta indet. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Insecta indet. P 0 0 0 0 0 0 0.00 0 0 0 0 35 0 0 0 0 7 0.07 16 7 0 35 Collembola Collembola indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 24 12 7 0.07 11 5 0 24 Entomobryidae Entomobryidae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Isotomidae Isotomidae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 0 0 71 0 106 35 0.35 50 22 0 106 Ephemeroptera Ephemeroptera indet. N 0 0 130 0 0 26 0.14 58 26 0 130 106 0 0 0 0 21 0.21 47 21 0 106 Baetidae Baetidae indet. N 0 0 0 0 0 0 0.00 0 0 0 0 247 0 0 24 0 54 0.54 108 48 0 247 Baetis sp. N 0 0 0 0 0 0 0.00 0 0 0 0 212 235 0 0 24 94 0.93 119 53 0 235




Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Caenidae Caenis sp. N 87 348 1174 0 730 468 2.44 486 217 0 1174 0 0 0 0 12 2 0.02 5 2 0 12 Ephemerellidae Ephemerellidae indet. N 0 0 0 0 0 0 0.00 0 0 0 0 71 0 0 0 0 14 0.14 32 14 0 71 Leptophlebiidae Paraleptophlebia sp. N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 24 12 7 0.07 11 5 0 24 Paraleptophlebia debilis N 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0










Empididae Empididae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 318 306 0 94 24 148 1.47 153 69 0 318 Hemerodromia sp. L 0 0 0 0 0 0 0.00 0 0 0 0 424 447 706 729 294 520 5.16 190 85 294 729 Metachela/Chelifera sp. L 0 0 0 0 0 0 0.00 0 0 0 0 35 0 71 94 0 40 0.40 42 19 0 94 Simuliidae Simuliidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 35 0 0 0 0 7 0.07 16 7 0 35




Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Tabanidae Tabanidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Chrysops sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 71 0 0 14 0.14 32 14 0 71 Silvius sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 0 0 0.00 0 0 0 0 Tipulidae Tipulidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 71 0 12 24 35 28 0.28 27 12 0 71 Dicranota sp. L 0 0 0 0 0 0 0.00 0 0 0 0 106 0 0 0 0 21 0.21 47 21 0 106 Hexatoma sp. L 0 0 0 0 0 0 0.00 0 0 0 0 0 0 0 0 24 5 0.05 11 5 0 24





Table H6-1: Continued (Site C1)

TAXON Stage Site C1

Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max BRYOZOA Bryozoa indet. colony 0 0 0 0 0 0 - - - - -NEMATODA Nematoda indet. A 0 0 52 87 87 45 - - - - -CNIDARIA Hydrozoa Hydra sp. A 0 0 0 0 0 0 0.00 0 0 0 0ANNELIDA Oligochaeta Oligochaeta indet. J 0 0 0 0 0 0 0.00 0 0 0 0 Enchytraeidae Enchytraeidae indet. J 0 0 0 0 0 0 0.00 0 0 0 0 Enchytraeidae indet. A 0 0 104 0 0 21 0.17 47 21 0 104 Henlea sp. A 0 0 0 0 0 0 0.00 0 0 0 0 Lumbriculidae Lumbriculidae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 Lumbriculus variegatus A 0 0 0 0 0 0 0.00 0 0 0 0 Naididae Naididae indet. J 0 0 0 0 0 0 0.00 0 0 0 0 Chaetogaster diaphanus A 0 0 0 0 0 0 0.00 0 0 0 0 Naididae indet. Group 2 Arcteonais lomondi A 0 0 0 0 0 0 0.00 0 0 0 0 Pristina leidyi A 0 0 0 0 0 0 0.00 0 0 0 0 Pristina sp. A 0 0 0 0 0 0 0.00 0 0 0 0 Stylaria lacustris A 0 0 0 0 0 0 0.00 0 0 0 0 Naidadae indet. Group 3 Dero nivea A 0 0 0 0 0 0 0.00 0 0 0 0 Dero sp. J 0 0 0 0 0 0 0.00 0 0 0 0 Dero sp. A 0 0 0 0 0 0 0.00 0 0 0 0 Naididae indet. Group 4 Slavina appendiculata A 0 0 0 0 0 0 0.00 0 0 0 0 Vejdovskyella comata J 0 0 0 0 0 0 0.00 0 0 0 0 Vejdovskyella comata A 0 0 0 0 0 0 0.00 0 0 0 0 Vejdovskyella sp. J 0 0 0 0 0 0 0.00 0 0 0 0 Naididae indet. Group 5 Nais communis A 0 0 0 0 0 0 0.00 0 0 0 0 Nais pardalis A 0 0 0 0 0 0 0.00 0 0 0 0 Nais simplex A 0 0 0 0 0 0 0.00 0 0 0 0 Nais variabilis J 0 0 0 0 0 0 0.00 0 0 0 0 Nais variabilis A 0 0 0 0 0 0 0.00 0 0 0 0 Specaria josinae A 0 0 0 1783 696 496 3.96 780 349 0 1783



TAXON Stage Site C1

Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Tubificoid Naididae Tubificoid Naididae indet. J 0 0 0 0 0 0 0.00 0 0 0 0 Tubificoid Naididae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 Tubificoid Naididae indet. Group 2 J 0 0 0 0 0 0 0.00 0 0 0 0 Tubificoid Naididae indet. Group 2 A 0 0 0 0 87 17 0.14 39 17 0 87 Tubificoid Naididae indet. Group 3 Aulodrilus pigueti A 0 0 0 0 0 0 0.00 0 0 0 0 Tubificoid Naididae indet. Group 5 J 0 0 0 0 0 0 0.00 0 0 0 0 Aulodrilus limnobius A 0 0 0 0 0 0 0.00 0 0 0 0 Limnodrilus udekemeanus J 0 0 0 0 0 0 0.00 0 0 0 0 Limnodrilus udekemeanus A 0 0 0 0 0 0 0.00 0 0 0 0 Limnodrilus sp. J 87 609 522 87 1391 539 4.30 534 239 87 1391 Limnodrilus sp. A 652 913 2713 870 2348 1499 11.96 955 427 652 2713

Total Oligochaeta 739 1522 3339 2739 4522 2572 20.53 1490 666 739 4522Hirudinea Erpobdellidae Erpobdella sp. A 0 0 0 0 0 0 0.00 0 0 0 0 Nephelopsis sp. A 0 0 0 0 0 0 0.00 0 0 0 0 Glossiphoniidae Helobdella stagnalis A 0 0 0 0 0 0 0.00 0 0 0 0 Helobdellasp. A 0 0 0 0 0 0 0.00 0 0 0 0

Total Hirudinea 0 0 0 0 0 0 0.00 0 0 0 0MOLLUSCA Bivalvia Sphaeriidae Sphaeriidae indet. J 0 130 0 304 261 139 1.11 142 64 0 304 Pisidium sp. A 87 0 52 0 87 45 0.36 44 20 0 87 Sphaerium sp. A 0 0 0 0 0 0 0.00 0 0 0 0

Total Bivalvia 87 130 52 304 348 184 1.47 133 60 52 348Gastropoda Lymnaeidae Lymnaeidae indet. J 0 0 0 0 0 0 0.00 0 0 0 0 Planorbidae Planorbidae indet. A 43 0 0 0 174 43 0.35 75 34 0 174 Ancylidae Ferissia sp. A 0 0 0 0 0 0 0.00 0 0 0 0 Valvatidae Valvata sp. A 0 0 0 0 0 0 0.00 0 0 0 0 Valvata sincera sincera A 0 0 0 0 0 0 0.00 0 0 0 0

Total Gastropoda 43 0 0 0 174 43 0.35 75 34 0 174TARDIGRADA Tardigrada indet. A 0 0 0 0 0 0 0.00 0 0 0 0



TAXON Stage Site C1

Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max ARTHROPODA ARACHNIDA Acari Hydrachnidia Hydrachnidia indet. J 0 0 0 0 0 0 0.00 0 0 0 0Hydrachnidia indet. A 174 217 313 6261 174 1428 11.39 2702 1209 174 6261 Hygrobatidae Hygrobatidae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 Lebertiidae Lebertia sp. A 0 0 0 0 0 0 0.00 0 0 0 0 Pionidae Forelia sp. A 43 0 0 43 0 17 0.14 24 11 0 43 Piona sp. A 0 0 0 0 0 0 0.00 0 0 0 0 Sperchontidae Sperchonopsis sp. A 0 0 0 0 0 0 0.00 0 0 0 0 Unionicolidae Unionicola sp. A 0 0 0 0 0 0 0.00 0 0 0 0Oribatida Oribatida indet. J 0 0 0 0 0 0 0.00 0 0 0 0Oribatida indet. A 0 0 0 0 0 0 0.00 0 0 0 0 Hydrozetidae Hydrozetes sp. A 0 0 0 0 0 0 0.00 0 0 0 0

Total Acari 217 217 313 6304 174 1445 11.53 2717 1215 174 6304CRUSTACEA Copepoda Calanoida Calanoida indet. cpp 0 0 0 0 0 0 0.00 0 0 0 0 Diaptomidae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 Cyclopoida Cyclopoida indet. cpp 0 0 0 43 261 61 0.49 113 51 0 261 Eucyclops sp. A 0 0 0 0 0 0 0.00 0 0 0 0 Macrocyclops sp. A 0 0 0 0 0 0 0.00 0 0 0 0 Harpacticoida Harpacticoida indet. cpp 0 0 0 0 0 0 0.00 0 0 0 0 Canthocamptidae indet. A 0 0 0 0 0 0 0.00 0 0 0 0

Total Copepoda 0 0 0 43 261 61 0.49 113 51 0 261Ostracoda Podocopida indet. J 0 0 0 0 0 0 0.00 0 0 0 0 Podocopida indet. A 0 0 0 0 0 0 0.00 0 0 0 0 Candona sp. A 0 0 0 0 0 0 0.00 0 0 0 0 Cypria sp. A 0 0 0 0 0 0 0.00 0 0 0 0

Total Ostracoda 0 0 0 0 0 0 0.00 0 0 0 0



TAXON Stage Site C1

Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Cladocera Chydoridae Chydoridae indet. J 0 0 0 0 0 0 0.00 0 0 0 0 Chydoridae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 Chydorus sphaericus A 0 0 0 0 0 0 0.00 0 0 0 0 Daphnidae Daphnidae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 Daphnia sp. A 0 0 0 0 0 0 0.00 0 0 0 0 Macrothricidae Ilyocryptus spinifer A 43 87 0 0 0 26 0.21 39 17 0 87 Sididae Sididae indet. A 0 0 0 0 0 0 0.00 0 0 0 0 Sida crystallina A 0 0 0 0 0 0 0.00 0 0 0 0

Total Cladocera 43 87 0 0 0 26 0.21 39 17 0 87Tanaidacea Leptochelia dubia A 0 0 0 0 0 0 0.00 0 0 0 0Isopoda Isopoda indet. A 0 0 0 0 0 0 0.00 0 0 0 0Amphipoda Gammaridae Gammarus sp. A 0 0 0 0 0 0 0.00 0 0 0 0 Hyalellidae Hyalella sp. J 0 0 0 0 0 0 0.00 0 0 0 0 Hyalella sp. A 0 0 0 0 0 0 0.00 0 0 0 0 Hyalella azteca A 0 0 0 0 0 0 0.00 0 0 0 0

Total Amphipoda 0 0 0 0 0 0 0.00 0 0 0 0TOTAL NON-INSECTA (excluding

Bryozoa and Nematoda) 1130 1957 3704 9391 5478 4332 34.57 3286 1470 1130 9391

INSECTA Insecta indet. N 0 0 0 0 0 0 0.00 0 0 0 0Insecta indet. P 0 0 0 0 0 0 0.00 0 0 0 0Collembola Collembola indet. A 0 0 0 0 0 0 0.00 0 0 0 0 Entomobryidae Entomobryidae indet. A 0 0 0 0 87 17 0.14 39 17 0 87 Isotomidae Isotomidae indet. A 43 0 0 0 0 9 0.07 19 9 0 43Ephemeroptera Ephemeroptera indet. N 0 0 0 0 0 0 0.00 0 0 0 0 Baetidae Baetidae indet. N 0 0 0 0 0 0 0.00 0 0 0 0 Baetis sp. N 0 0 0 0 0 0 0.00 0 0 0 0 Caenidae



TAXON Stage Site C1

Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Caenis sp. N 0 0 0 0 0 0 0.00 0 0 0 0 Ephemerellidae Ephemerellidae indet. N 0 0 0 0 0 0 0.00 0 0 0 0 Leptophlebiidae Paraleptophlebia sp. N 0 0 0 0 0 0 0.00 0 0 0 0 Paraleptophlebia debilis N 0 0 0 0 0 0 0.00 0 0 0 0

Total Ephemeroptera 0 0 0 0 0 0 0.00 0 0 0 0Odonata Anisoptera Corduliidae Cordulia sp. N 0 0 0 0 0 0 0.00 0 0 0 0 Epitheca sp. N 0 0 0 0 0 0 0.00 0 0 0 0 Libellulidae Libellulidae indet. N 0 0 0 0 0 0 0.00 0 0 0 0Hemiptera Corixidae Corixidae indet. N 0 0 0 0 0 0 0.00 0 0 0 0Plecoptera Plecoptera indet. N 0 0 0 0 0 0 0.00 0 0 0 0 Nemouridae Nemouridae indet. N 0 0 0 0 0 0 0.00 0 0 0 0

Total Plecoptera 0 0 0 0 0 0 0.00 0 0 0 0Trichoptera Trichoptera indet. L 0 0 0 0 0 0 0.00 0 0 0 0 Brachycentridae Brachycentridae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 Brachycentrus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Glossosomatidae Glossosoma sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Hydropsychidae Hydropsychidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 Hydropsyche sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Hydroptilidae Hydroptilidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 Oxyethira sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Lepidostomatidae Lepidostomatidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 Leptoceridae Leptoceridae indet. L 43 0 0 0 0 9 0.07 19 9 0 43 Mystacides sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Oecetis sp. L 0 0 0 0 0 0 0.00 0 0 0 0



TAXON Stage Site C1

Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Limnephilidae Limnephilini indet. L 0 0 0 0 0 0 0.00 0 0 0 0 Nemotaulius sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Phryganeidae Phryganea sp. L 0 0 0 0 0 0 0.00 0 0 0 0

Total Trichoptera 43 0 0 0 0 9 0.07 19 9 0 43Lepidoptera Lepidoptera indet. L 0 0 0 0 0 0 0.00 0 0 0 0Coleoptera Coleoptera indet. L 0 0 0 0 0 0 0.00 0 0 0 0 Dytiscidae Hydroporus sp. A 0 0 52 0 0 10 0.08 23 10 0 52 Haliplidae Haliplus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Elmidae Elmidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 Optioservus sp. L 0 0 0 0 0 0 0.00 0 0 0 0

Total Coleoptera 0 0 52 0 0 10 0.08 23 10 0 52Diptera Diptera indet. L 0 0 52 43 0 19 0.15 26 12 0 52Diptera indet. P 0 0 0 0 0 0 0.00 0 0 0 0 Ceratopogonidae Ceratopogonidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 Atrichopogon sp. L 0 0 0 43 0 9 0.07 19 9 0 43 Bezzia/Palpomyia sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Culicoides sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Dasyhelea sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Probezzia sp. L 130 130 52 1043 261 323 2.58 409 183 52 1043

Total Ceratopogonidae 130 130 52 1087 261 332 2.65 429 192 52 1087 Chaoboridae Chaoborus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Chironomidae Chironomidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 Chironominae Chironomini Chironomini indet. L 261 43 95 2217 6783 1880 15.00 2887 1291 43 6783 Chironomus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Cladopelma sp. L 0 0 52 0 0 10 0.08 23 10 0 52 Cryptochironomus sp. L 0 87 313 478 870 350 2.79 346 155 0 870 Dicrotendipes sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Endochironomus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Microtendipes sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Paralauterborniella sp. L 0 0 0 0 87 17 0.14 39 17 0 87



TAXON Stage Site C1

Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Phaenopsectra sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Polypedilum (pentapedilum) sp. L 43 0 52 0 0 19 0.15 26 12 0 52 Polypedilum (polypedilum) sp. L 1783 435 8661 565 12261 4741 37.84 5400 2415 435 12261 Robackia sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Tanytarsini Tanytarsini indet. L 0 43 52 217 261 115 0.92 116 52 0 261 Cladotanytarsus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Micropsectra sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Paratanytarsus sp. L 261 43 313 130 174 184 1.47 106 48 43 313 Stempellinella sp. L 0 0 0 696 0 139 1.11 311 139 0 696 Tanytarsus sp. L 0 0 0 0 174 35 0.28 78 35 0 174

Total Chironominae 2348 652 9538 4304 20609 7490 59.78 8057 3603 652 20609 Orthocladiinae Orthocladiinae indet. L 0 0 0 43 0 9 0.07 19 9 0 43 Corynoneura sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Cricotopus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Eukiefferiella sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Heterotanytarsus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Heterotrissocladius sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Orthocladius sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Psectrocladius sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Synorthocladius sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Thienemanniella sp. L 0 0 0 0 0 0 0.00 0 0 0 0

Total Orthocladiinae 0 0 0 43 0 9 0.07 19 9 0 43 Tanypodinae Tanypodinae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 Coelotanypodini Clinotanypus sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Pentaneurini Ablabesmyia sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Thienemannimyia sp. L 0 0 0 0 87 17 0.14 39 17 0 87 Procladiini Procladius sp. L 87 0 261 261 261 174 1.39 123 55 0 261

Total Tanypodinae 87 0 261 261 348 191 1.53 143 64 0 348Total Chironomidae 2435 652 9799 4609 20957 7690 61.37 8171 3654 652 20957

Empididae Empididae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 Hemerodromia sp. L 0 0 0 43 0 9 0.07 19 9 0 43 Metachela/Chelifera sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Simuliidae Simuliidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 Tabanidae Tabanidae indet. L 43 43 209 217 0 103 0.82 102 46 0 217



TAXON Stage Site C1

Rep 1 Rep 2 Rep 3 Rep 4 Rep 5 Mean RA (%) STD SE Min Max Chrysops sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Silvius sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Tipulidae Tipulidae indet. L 0 0 0 0 0 0 0.00 0 0 0 0 Dicranota sp. L 0 0 0 0 0 0 0.00 0 0 0 0 Hexatoma sp. L 0 0 0 0 0 0 0.00 0 0 0 0

Total Diptera 2609 826 10112 6000 21217 8153 65.07 8118 3630 826 21217TOTAL INSECTA 2696 826 10165 6000 21304 8198 65.43 8141 3641 826 21304

TOTAL ABUNDANCE (excluding Bryozoa and Nematoda) 3826 2783 13869 15391 26783 12530 9797 4381 2783 26783

Appendix H7

Fish Habitat Requirements



Table H7-1: Habitat Requirements for Fish Species Documented within Devon Pike ALSA

Fish Species Spawning Rearing (juvenile) Holding (Adult) Overwintering

SALMONIDAE (trout family) – cover is recognized as one of the essential components of trout steams

Arctic grayling (Riverine) (Thymallus arcticus)

• Spring (when water is between 7 and 10°C).

• Small boulder and gravel with a little silt or sand.

• No nest or Redd is prepared.

• Spawn during spring break up.

• Eggs are broadcast over clean, gravel or rock substrate, settling in between the rocks to incubate.

• Newly emergent fry are weak swimmers. They take up side-channels or stream margins moving into deeper and faster water as they grow.

• Juveniles remain in natal streams for up to 15 months.

• Temperature tolerance ranges between 2 and 24.5°C.

• Preferred cover type is boulders.

• Juveniles mainly eat zooplankton with a gradual shift to immature insects, mainly mayflies, caddis flies and midges, with increased size.

• Cold, clear water with abundant pools and riffles.

• Temperature ranges between 1 and 20°C.

• Mean water depths of 28.4 cm.

• Utilize pools and are often found downstream of the riffle areas but seldom in the riffles except during spawning or migration.

• Overhanging vegetation, high quality of pools and diverse pool types (debris pools, lateral-scour pools, class 4 pools) support a relatively high abundance of grayling.

• Deep pools present- water depths greater than 1.2 m in large streams or spring-fed reaches of small streams that do not freeze solid in winter.

• Velocities less than 0.15 m/s.

• Maintaining DO levels of more than 1.0 mg/L during winter.

lake whitefish (Coregonus clupeaformis) LKWH

• Occurs September to January; firm substrate (i.e., rocks or compact sand); at depths of less than 7.6 m in lakes. Spawn at night.

• Shallow, riffle areas of rivers or shallow lake beaches with rock, gravel or sand substrate.

• Eggs remain on the spawning grounds until they hatch in April or May.

• Preferred spawning depth in rivers - 0.1 to 1.0 m; Preferred spawning depth in large lakes - 3.0 to 30.0 m; Preferred spawning depth in small lakes - 1.0 to 5.0 m.

• Rear in large groups; along steep shorelines.

• Young whitefish leave the shallow inshore waters by early summer to migrate to deeper water.

• Food habits during first year of life changes from planktonic to benthic; Cladocerans remain the primary food organism consumed.

• TSS affects juvenile feeding, best at less than 10 mg/L.

• Restricted to cool well-oxygenated regions of lakes; in Alberta they occasionally occur in rivers.

• Generally they are bottom feeders consuming bottom-living invertebrates and small fish. But in some regions, they will mainly be planktonic feeders.

• Males mature and die earlier than females.

• Preferred cover type is darkness.

• Deep pools and lakes; minimum DO levels of >4.25 mg/L.




ESOCIDAE (pike family)

northern pike (Esox lucius) NRPK

• Occurs in early spring, during or shortly after the ice clears; shallow marshes connected to rivers and lakes or flooded vegetation in shallow bays and rivers; water velocity <0.1 m/s; water depth 0.2 to 0.4 m.

• Temperature between 8 and 12°C.

• Fish tend to migrate up tributaries to shallow marshes and wetlands or shallow shoreline inundation.

• Eggs are broadcast and adhere to vegetation, only a few eggs (5 to 60) are released at a time, they are released at different locations and not al at the same time.

• Prefer dense submergent and emergent vegetation (>30% cover) in the calm bays of sloughs, marshes and lakes and in the back eddies or mouths of (low gradient) tributary streams; water depth <4 m.

• Stay in the macrophyte areas, don not venture into the macrophyte-open water interface.

• Prefer shallow, weedy, clear waters primarily in lakes and marshes; common in streams with slow to moderate current with ample aquatic vegetation and fine substrate; diet consists of fish, crustacean, minnows, insects and young muskrats and ducks.

• Rarely venture below the thermocline, they prefer the interface between vegetation and open water.

• Piscivore.

• Larger individuals frequent lower vegetation densities and small individuals frequent higher vegetation densities.

• High turbidity reduces the ability for adults to feed.

• Typically deep water; dissolved oxygen >3 to 4 mg/L.

• Juveniles are able to handle lower DO than adults.

GADIDAE (cod family)

burbot (Lota lota) BURB

• Spawn during the winter and early spring (Jan to April) beneath the ice or open water.

• Boulders, cobble, or gravel with small amount of silt, sand and detritus; shallow bays or on shoals of lakes and rivers; no current; clear water; 0.3 to 3 m deep.

• Burbot are mass spawners – a group of 10 to 12 male and female gather over gravelly, near-shore shoals or shallow, sandy area. Spawning occurs only at night.

• Preferred spawning temperature is between 0.6 and 1.7°C.

• Eggs are semi-buoyant when laid and become demersal within a few days sinking to the substrate in the interstitial spaces- preferred substrate is interstices of sand, gravel, and cobble free of silt and debris.

• Juveniles occur along rocky shores and weedy areas of tributary streams.

• Found in littoral regions of lakes and in shallow regions of streams and rivers where they forage for benthic invertebrates.

• Preferred cover types are rocks, cobble, vegetation and logs.

• Juveniles eat primarily crayfish and aquatic insects and secondarily fish.

• Optimum temperature for growth is between 15.6 and 18.3°C.

• Cold parts of lakes and in large and small streams; diet consists of fish and aquatic insect larvae as well as whitefish eggs; adults are night feeders and voracious predators.

• Preferred cover type is darker waters at depth.

• Deep water of lakes and large rivers.

• Sensitive to DO levels with acute lethal DO limit >2 mg/L.




CATOSTOMIDAE (sucker family)

longnose sucker (Catostomus catostomus) LNSC

• Spawn from late May to early July; Enter spawning stream as soon as temperature exceeds 5°C.

• Occurs in shallow, moderately flowing water over a coarse gravel to cobble substrate.

• The spawning act is repeated numerous times broadcasting small numbers of tiny sticky eggs with each trial.

• Shallows of streams or areas of lakes; gravel substrate; water depth 0.15 to 0.28 m.

• Spawn before white sucker.

• Move upstream between noon and midnight with the greatest number moving in the evening hours.

• A female moves from quiet water near shore into group of males near stream centre. Two to 4 males crowd around one female, clasping or beating against her with their anal fins and thrashing about. The spawning act last 3 to 5s and my occur 6 to 40 timer per hour.

• Male develops large red lateral line during spawning.

• Fry remain within gravel for 1 to 2 weeks then disperse to bottoms of deeper, cooler lakes and clear rivers.

• Fry feed on zooplankton and diatoms.

• Often in association with vegetation and sandy substrates.

• Adult fish feed primarily on bottom invertebrates such as immature insects, freshwater shrimp, small clams and crustaceans; Plants, algae and detritus.

• Presumably occurs in deeper sections of large lakes and rivers.

white sucker (Catostomus commersoni) WHSC

• Spawn in spring (early May to early June).

• Adults migrate from lakes into gravelly streams when steam temperature first reaches 10°C.

• Shallow water; occasionally in rapids.

• Preferred spawning velocity is 30 to 60 cm/s; they select moderate stream velocities for spawning.

• Fertilized eggs adhere to gravel in riffles or drift downstream where they adhere to the substrate in areas with water of slow velocities.

• Fry emerge 9 to 11 days after hatching and drift downstream at night.

• Fry (12 mm) feed on surface plankton and other invertebrates near the surface.

• At 16 to 18 mm, when the mouth moves from terminal to ventral, there is a shift to bottom feeding.

• Adults are bottom feeders; prefer warm, shallow lakes and tributary rivers of large lakes.

• Optimum white sucker habitat is assumed to have a pool to riffle ration of 1:1.

• pH ranges from 5 to 9.

• Pools and riffles of creeks and rivers, warm shallow lakes and embayments of larger lakes usually at depths of 6 to 9 m.

• Presumably occurs in lakes and large rivers.




GASTEROSTEIDAE (stickleback family)

brook stickleback (Culea inconstans) BRST

• Spring-early summer (April to July).

• Male builds an oval shaped nest with vegetation held together with its own kidney secretions.

• Builds nests in shallow water, on the stems of grass, reeds, or on substrate bottom.

• Males aerates and defends eggs until they hatch 21 days later.

• Males turn jet black before nest building and others turn black after the nest is complete.

• Presumably similar to adult stage. • Small, boggy headwater streams, shallow lake margins, ponds, and clear pools and backwaters of creeks and small rivers; usually associated with aquatic vegetation; occasionally brackish water; preferred water temperature 21.3°C.

• Eats insect larvae, crustaceans, eggs and larvae of other fish, snails, oligochaetes and algae.

• High tolerance to low oxygen concentration.

COTTIDAE (sculpin family)

slimy scuplin (Cottus cognatus) SLSC

• Spawn in May.

• Male build nests under a rock or ledge or sometimes under a submerged tree root, the courted female enters the nest and deposits adhesive eggs in a mass to the ceiling of the nest. The male guards the nest and aerates eggs and guards the next even after the young have began to feed.

• Eggs hatch in about 28 days.

• Presumably similar to adult stage. • Found in lakes and cool rocky stream.

• Eat crustaceans, aquatic insects, small fishes and occasional detritus.

• Rocky habitat, hide in interstitial spaces.

• Gravelly, rocky riffles of cold streams and rocky substrates in deep (37 to 108 m), cooler waters of lakes; preferred water temperature range 9 to 14°C.

• Adequate flow, boulder habitat, presumably in pools/lakes and areas with flow.




CYPRINIDAE (minnow family)

emerald shiner (Notropis atherinoides) EMSH

• Spawns in late spring to early summer (Jun/August).

• Broadcast spawners and female carries up to 3000 eggs per spawning season.

• Eggs hatch in 24 to 36 hrs.

• Aggregate in large schools in inshore waters sometimes near docks, piers and river mouths.

• Pools and runs of medium to large rivers with sand or gravel substrates and open waters of lakes; preferred water temperature range 9 to 23°C.

• Pelagic feeder, follows rise of plankton to surface at dusk and sinking of plankton at dawn; move into surface water at night and drop down to deeper water during the day.

• Schooling species.

• Along shallow shorelines in autumn, open water during rest of the year.

• Also eats algae, fish eggs and small juveniles, worms and invertebrates.

• Move into deeper water for overwintering.

flathead chub (Platygobio gracilis) FLCH

• Likely occurs in the summer; July/August.

• May be fractional spawners. Not enough research.

• Little or no sexual dimorphism.

• Semi-buoyant eggs afloat until hatching occurs. Newly-hatched fry are weak swimmers, so strong currents are required to keep fry suspended so that they do not settle to the bottom and become buried.

• Presumably similar to adult stage. • Found in large rivers with high seasonal silt load.

• Frequent backwaters or river margins; Turbid, flowing waters of main stem rivers; Riffle and runs.

• Feeds on a wide variety of organisms, probably by sight and by the gustatory (taste buds) on the barbells; Barbells help.

• Feed on terrestrial and aquatic insects and occasionally fish.

• Prefer gravel, sand and clay/silt substrate.

• The importance of terrestrial insects to the diets of flathead chubs is consistent with the fact that the species occurs in turbid waters where low light penetration results in low primary production and hence, a low abundance of aquatic invertebrates.

• Flathead chub use of refugia in high or low flows or during winter is unknown.

• Presumably in deeper water with adequate flow.

• DO is greater than 2.0 mg/L.




lake chub (Couesius plumbeus) LKCH SUMMER

• June to mid-August.

• Migrate from lakes to tributary streams in early spring and spawn when temperatures 14 to 19°C.

• No nests, non-adhesive eggs are deposited among cobble and boulder.

• Presumably similar to adult stage.

• Feed on plankton.

• Cool water in both lakes and streams, wide range of depths from 15 cm shoals in streams to rocky habitats along lakeshores.

• Food preference variable but typically insects, zooplankton, and algae; some large LKCH will eat fish.

• Sight-feeding predator.

• Instream cover consists of coarse substrate, vegetation, woody debris, submergent and emergent vegetation.

• Prefers runs, flats and pools in rivers, in lakes prefer <2 m depth.

• DO is greater than 1.0 mg/L.

• Presumably in deeper water.

Appendix H8

Typical Watercourse Crossing Schematics

Typical Clear Span Bridge Crossing

Pike 1 Project

May 22, 2012

FigureH8-1

PROVIDED BY:

DevonFINAL MAPPING BY:

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Typical Clear Span Pipeline Crossing

Pike 1 Project

May 22, 2012

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Watercourse CrossingDirectional Drill Stages

Pike 1 Project

May 22, 2012

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PROVIDED BY:


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STAGE 1: PILOT HOLE DIRECTIONAL DRILLING

STAGE 2: REAMING AND PULLING BACK

PROFILE(Not to Scale)

ENTRYPOINT

HORIZONTALDRILLING RIG

DRILLPIPE

GENERAL DIRECTION OFPROGRESS PILOT HOLE DRILLING

PILOTHOLE

WATERCOURSE

DESIGNEDDRILL PATH

EXIT POINT


WATERCOURSE

WATERCOURSE

DRILLING FLUIDRETURNS

REAMERGENERAL DIRECTION OFPROGRESS PREREAMING


DRILLING FLUIDRETURNS STRUNG PIPE

(WELDED, TESTEDAND PRECOATED)

SWIVELGENERAL DIRECTION OFPULLING BACK

Notes:1. Utilize the directional drill technique on watercourse listed in the Project Description Construction Agreement A-6123.2. Obtain geotechnical data prior to initiating drilling. Drilling may not be feasible in some materials such as unconsolidated gravels.3. Set up drilling equipment outside the riparian zone of the watercoruse; do not clear or grade within the riparian zone, except along the workside, if temporary vehicle crossing is utilized.4. Assign full time inspectors to observe for an inadvertent mud release into or adjacent to the watercourse.5. Ensure that only bentonite based drilling mud is used. Do not allow the use of any additives in the drilling mud without the approval of Natural Resources Service.6. Install suitable drilling mud tanks or sumps to prevent contamination of watercourse.7. Install berms downslope from the drill entry and anticipated exit points to contain any release of drilling mud. Have vacuum trucks onsite to recover excess mud when pulling back.8. Dispose of drilling mud in accordance with ERCB guidelines. Source: Devon GS-7310-EPP Forest Lands 26

Watercourse CrossingDirectional Drill

Pike 1 Project

May 22, 2012

FigureH8-4

PROVIDED BY:


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General Notes:1. The pipeline shall be installed so that the entire pipe is outside the shaded zone.2. Crossing Type Selection: A) Single SAG Bend crossing shall be used where minimum cover can be provided on narrow streams. B) Double SAG Bend crossing shall be installed where width prohibits the use of a single SAG to provide minimum cover during the lifetime of the pipeline.

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