List of Tables List of Figures - vbwd.org...Water quality sampling was conducted on Kramer Pond in...

16
2015 Valley Branch Watershed District Watershed Management Plan Kramer Pond Watershed Management Plan Barr Engineering Company Page 5.34-i P:\Mpls\23 MN\82\2382174\WorkFiles\2015 VBWD Plan\Final\Section 5.34 - Kramer Pond.doc 5.34 Kramer Pond Watershed Management Plan ...................................................... 5.34-1 5.34.1 General Information ............................................................................. 5.34-1 5.34.2 Water Quality Management Plan .......................................................... 5.34-2 5.34.2.1 Water Chemistry .................................................................... 5.34-3 5.34.2.2 Biological Data ...................................................................... 5.34-3 5.34.3 Water Quantity Management Plan ........................................................ 5.34-4 5.34.4 Groundwater ........................................................................................ 5.34-5 5.34.5 References............................................................................................ 5.34-5 List of Tables Table 5.34-1 Summary of Kramer Pond summer average water quality ..................................... 5.34-3 List of Figures Figure 5.34-1 Kramer Pond Watershed Subwatersheds and Flow Routing ................ 5.34-7 Figure 5.34-2 Kramer Pond Watershed Current (2010) and Future (2030) Land Use 5.34-8 Figure 5.34-3 Kramer Pond Water Quality Data Summary .......................................... 5.34-9 Figure 5.34-4 Kramer Pond Water Level Data ........................................................... 5.34-10 List of Appendices Appendix A-5.34 Additional Macrophyte Information

Transcript of List of Tables List of Figures - vbwd.org...Water quality sampling was conducted on Kramer Pond in...

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5.34 Kramer Pond Watershed Management Plan ...................................................... 5.34-1 5.34.1 General Information ............................................................................. 5.34-1 5.34.2 Water Quality Management Plan .......................................................... 5.34-2

5.34.2.1 Water Chemistry .................................................................... 5.34-3 5.34.2.2 Biological Data ...................................................................... 5.34-3

5.34.3 Water Quantity Management Plan ........................................................ 5.34-4 5.34.4 Groundwater ........................................................................................ 5.34-5 5.34.5 References ............................................................................................ 5.34-5

List of Tables

Table 5.34-1 Summary of Kramer Pond summer average water quality ..................................... 5.34-3

List of Figures

Figure 5.34-1 Kramer Pond Watershed – Subwatersheds and Flow Routing ................ 5.34-7

Figure 5.34-2 Kramer Pond Watershed – Current (2010) and Future (2030) Land Use 5.34-8

Figure 5.34-3 Kramer Pond Water Quality Data Summary.......................................... 5.34-9

Figure 5.34-4 Kramer Pond Water Level Data ........................................................... 5.34-10

List of Appendices

Appendix A-5.34 Additional Macrophyte Information

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5.34 Kramer Pond Watershed Management Plan

5.34.1 General Information

Kramer Pond and its entire tributary

watershed lie within the City of Lake

Elmo (see Figure 5.34-1). Kramer

Pond is a 9-acre wetland located north

of the I-94 frontage road, between

Keats Avenue North (CSAH 19) and

Lake Elmo Avenue North (CSAH 17),

near the south border of the City of

Lake Elmo.

One development is located adjacent

to Kramer Pond on the northeast side.

The remainder of the watershed is

currently occupied by agricultural land

use and undeveloped space, although

some developments are near

construction on the western edge of

the watershed. Future (2030)

estimated land use calls single family

residential development north of

Kramer Pond, multi-option

development along I-94, and

commercial development near the

intersection of I-94 and Keats Avenue

(CSAH 19). Figure 5.34-2 shows the

current (2010) and future (2030)

estimated land use within the Kramer

Pond watershed.

There is no public access to Kramer

Pond. Around 1969, the landowner

constructed a berm across the wetland

for tractor access to the fields north of

the pond. The berm causes the

northeastern lobe of the wetland (in

subwatershed KRM-3) to be drier than

the western portion of the wetland (in

subwatershed KRM-1, see Figure

5.34-1).

Kramer Pond Watershed Information

Tributary Area (acres) 427

MDNR-Designated Basins within Watershed

82-0117W (Kramer Pond)

Downstream Watershed Landlocked (Rose Lake if overflows)

Kramer Pond Information

MDNR Designation 82-0117W

Surface Area (acres)

North lobe: 8.5 at El. 909.8

South lobe: 3.4 at El. 909.8

NE Wetland: 10.4 at El 910

Mean Depth (feet) Not determined

Maximum Depth (feet) Not determined

Volume Below Discharge Elevation (acre-feet)

Not determined

Discharge Elevation 916

Outlet Type Landlocked

MDNR Ordinary High Water Level (OHW)

Not determined

100-Year Flood Level1 914.0

VBWD “Allowable Fill”

(cubic yards/lineal foot of shoreline)

(See Section 4.7.)

1.0

VBWD Water Quality Priority Category Low 1 Elevation in NAVD88 vertical datum

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5.34.2 Water Quality Management Plan

The VBWD classified and will manage Kramer Pond as a Low Priority waterbody (see Section 4.1 –

Water Quality) due to the lack of public access and is classification as a wetland by the Minnesota

Pollution Control Agency (MPCA). This is consistent with its classification in the 2005 VBWD Plan.

In the VBWD 1995 Plan, Kramer Pond was classified as a Level V (wetland) waterbody.

The water quality of Kramer Pond is generally poor. The VBWD has a non-degradation water quality

policy which sets “action triggers” for all of its major waterbodies. Section 4.1 – Water Quality

discusses the action triggers in more detail. Action triggers for VBWD lakes consider the following

water quality parameters (summer average) relative to MPCA water quality standards and prior water

quality data (i.e., trend analysis):

Secchi disc depth

Total phosphorus

Chlorophyll a

Specific water quality implementation tasks for Kramer Pond include the following.

1. The VBWD will cooperate with other entities to monitor the water quality of Kramer Pond at

the interval(s) specified in Section 4.1 – Water Quality for Low Priority waterbodies. As for

all Low Priority waterbodies, the VBWD will perform additional monitoring or other actions

on a case-by-case (see Table 4.1-6).

The VBWD will evaluate the average summertime water quality (total phosphorus,

chlorophyll a, and Secchi disc transparency) and compare it to water quality standards (if

applicable) and applicable action triggers (described in Section 4.1.7.5).

2. The VBWD will cooperate with other entities in support of macrophyte management efforts.

VBWD efforts may include:

point-intercept surveys of aquatic vegetation

preparation of lake vegetation management plans (LVMP)

completion of Invasive Aquatic Plant Management (IAPM) Permit applications

design of herbicide treatment programs

participation in meetings with MDNR staff

other technical analysis

3. The VBWD will continue to implement its Rules and Regulations (2013, as amended) in the

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Kramer Pond watershed. The VBWD Rules address water quality performance standards for

development and redevelopment projects, as well as required vegetated buffers around

VBWD lakes, streams, and wetlands. The VBWD Rules and Regulations are included in this

Plan as Appendix A-4.5.

5.34.2.1 Water Chemistry

Water quality sampling was conducted on Kramer Pond in 2003, 2008, 2009, 2010, 2012, and 2013.

Water quality samples are typically analyzed for total phosphorus and chlorophyll a, while Secchi

disc transparency is measured in the field at the time of sampling (see Appendix A-4.1 – Water

Quality Background Information).

The most recent 10-year average summer water quality data is presented in Table 5.34-1 and

illustrated in Figure 5.34-3.

Table 5.34-1 Summary of Kramer Pond summer average water quality

Parameter Units

10-year

Average

(2004-2013)

Trend in

Average

MPCA

Standard1

Total Phosphorus ug/L 685 NA NA

Chlorophyll a ug/L 193 NA NA

Secchi Disc Depth m 0.41 NA NA

1 MPCA eutrophication water quality standards are not applicable to wetlands

While water quality in Kramer Pond fluctuates annually, water quality has been consistently poor

since monitoring began in 2003. Summer average Secchi disc transparency was less than (i.e. worse

than) 0.7 meters in all years measured. The worst water quality occurred in 2012, when Secchi disc

transparency was less than 0.2 meters, summer average chlorophyll a was over 300 ug/L (the highest

observed) and summer average total phosphorus was approximately 800 ug/L (the second highest

observed value). Chlorophyll a declined sharply in 2013, decreasing from over 300 ug/L to less than

10 ug/L (see Figure 5.34-3).

The most recent 10-years of data identify no statistically significant trends in total phosphorus,

chlorophyll a, or Secchi disc transparency.

5.34.2.2 Biological Data

Various types of biological data have been compiled and evaluated for Kramer Pond, in addition to

physical and chemical parameters. Macrophyte (large aquatic plants), phytoplankton (non-rooted

floating plants – algae), zooplankton (microscopic aquatic animals), and fisheries data provide

insight into the ecological quality of a waterbody. Section 4.2 (Water Quality Background

Information) provides more information about the importance of fisheries and other biological data.

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The Kramer Pond fishery is not managed by the MDNR and there are no stocking or surveying

programs in place. Kramer Pond does not have a fisheries-use classification, and no fish consumption

advisories have been issued for the pond. The MDNR’s Lakefinder website includes the most current

data on Kramer Pond and is available at: http://www.dnr.state.mn.us/lakefind/lake.html?id=82011700

The VBWD conducted macrophyte (large aquatic plant) surveys on June 9, 2003, August 18, 2003,

June 4, 2009, and June 5, 2012. Appendix A-5.34 includes the 2003, 2009, and 2012 macrophyte

survey information. The VBWD collects macrophyte data to identify the conditions of plant growth

throughout the lake. Macrophytes are the primary producers in the aquatic food chain, converting the

basic chemical nutrients in water and soil into plant matter through photosynthesis, which becomes

food for all other aquatic life. While macrophytes can negatively impact the recreational use of a

water body, they are critical to the ecosystem as fish and wildlife habitat.

In 2003 and 2009, the pond’s moderately diverse plant community consisted of five to eight

individual species. In both 2003 surveys, plant growth was limited to depths less than two or three

feet due to shading by the algal community. Plant species observed in Kramer pond are consistent

with the pond’s poor water transparency and include three turbidity tolerant native species, water

celery (Vallisneria americana), Canada waterweed (Elodea canadensis), and coontail

(Ceratophyllum demersum) (Borman et al., 1997). In 2012 the water level in Kramer Pond was high

and no macrophyte species were observed during the survey.

All plant species observed in Kramer Pond are common to Minnesota ponds and lakes and provide

good habitat for the fish and aquatic animals living within the pond. No non-native, exotic species

were noted in the two surveys.

There are no phytoplankton (microscopic plants), or zooplankton (microscopic animals) data for

Kramer Pond.

5.34.3 Water Quantity Management Plan

Kramer Pond is a landlocked basin and is often split into two water bodies. The two parts of the pond

in subwatershed KRM-1 (see Figure 5.34-1) are at an elevation of about 910, according to

Washington County’s 2000 two-foot interval topographic map. The two ponds become one larger

pond at higher elevations, approximately Elevation 911.2. At Elevation 910.15, water will flow into

the large wetland area northeast of the two ponds in subwatershed KRM-3 (see Figure 5.34-1). When

this combined water body reaches Elevation 911.64, water will flow northeast from Kramer Pond to a

1.2-acre pond located in subwatershed KRM-6 (see Figure 5.34-1). The ultimate overflow from the

combined ponding area is the low point in Lake Elmo Avenue North, at Elevation 916, based on

Washington County’s 2000 topography. If Kramer Pond were to overflow, the water would flow to

Rose Lake.

The 100-year flood elevation for Kramer Pond has been managed by the VBWD at different levels

throughout the history of the VBWD. In the 1987 VBWD water management plan, the 100-year flood

level of Kramer Pond was shown as Elevation 911 (NGVD29 datum). This elevation was based on

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the belief that there are culverts under Lake Elmo Avenue North (CSAH 17) at the low point in the

road. However, during VBWD’s review of The Forest development adjacent to Kramer Pond, it was

determined that there are no culverts under Lake Elmo Avenue North (CSAH 17). Therefore, the

overflow point became the low point in Lake Elmo Avenue North, and the 100-year flood elevation

was computed to be Elevation 916. At this elevation, a home adjacent to the 1.2-acre pond northeast

of Kramer Pond would be flooded. The 1995 VBWD water management plan listed the 100-year

flood level of Kramer Pond at Elevation 915.8.

In 2003, Washington County contracted with the VBWD to establish a “Base Flood Elevation” that

could be used for new Federal Emergency Management Agency (FEMA) Flood Insurance Rate Maps

(FIRMs). Through this detailed study, the VBWD determined that the 1% probability flood level

(i.e., the 100-year flood level) for Kramer Pond is Elevation 914.0 (NAVD88), which the VBWD has

adopted as the 100-year flood elevation for Kramer Pond. The 100-year flood level for Kramer Pond

included on FEMA’s Washington County Flood Insurance Rate Map (FIRM) is also set at Elevation

914 (NAVD88 datum). At this elevation, there still appears to be one home within Kramer Pond’s

100-year floodplain.

In 2013, the National Oceanographic and Atmospheric Administration (NOAA) published Atlas 14,

Volume 8 (see Section 4.7.6). Atlas 14 contains updated precipitation data for Minnesota and

supersedes data sources used to establish the VBWD and FEMA 100-year flood elevations within the

Kramer Pond subwatershed. Over the next several years, the VBWD will update its hydrologic -

hydraulic modeling of major subwatersheds, including Kramer Pond. Updated modeling will

incorporate the most recent precipitation data (see Section 4.7.7) which may increase 100-year flood

levels relative to the existing levels.

VBWD has no plans to control Kramer Pond water levels. The VBWD has monitored water levels on

Kramer Pond since 2008 (see Figure 5.34-4). The VBWD will continue to monitor water levels on

Kramer Pond as staff or volunteer time and access allow.

5.34.4 Groundwater

Water that seeps from Kramer Pond could contribute to the groundwater feeding Valley Creek. More

information regarding groundwater regional ground water flow is described in Section 3.7.

Groundwater management strategies of the VBWD are described in Section 4.2. Information

regarding groundwater contributions to Valley Creek is described in the Valley Creek subwatershed

management plan (see Section 5.20).

5.34.5 References

Barr Engineering Company. September 1995. Water Management Plan, Valley Branch Watershed

District.

Barr Engineering Company. December 2005. Valley Branch Watershed District Watershed

Management Plan.

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Borman, S., R. Korth, and J. Temte. 1997. Through the Looking Glass … A Field Guide to Aquatic

Plants. Wisconsin Lakes Partnership (Cooperative Extension of the University of Wisconsin—

Extension and the Wisconsin Department of Natural Resources). Stevens Point, WI.

National Oceanographic and Atmospheric Administration (NOAA). 2013. Atlas 14 Precipitation-

Frequency Atlas of the United States – Volume 8.

Valley Branch Watershed District. April 1987. Watershed Management Plan.

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FL = 932NL = 921AF = 601OHW = 924.4

GooseLake

KramerPond

§̈¦94

Woodbury

§̈¦94

Lake Elmo

10th St N

Keats

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NW

oodb

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r

Lake

Elm

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NCo

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Grov

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FL = 914NL = 906AF = 70

EPL-1

EPL-4

ELM-1

ROS-2

ROS-1456710

456719

456717

82-113 W

82-117 W

82-88 W

82-434 W

82-432 W

RAP-11

GOS-1

GOS-2

KRM-1

KRM-6

ROS-14

KRM-11

EPL-2

RAP-19

RAP-18

ROS-8

ROS-6

GOS-3

RAP-13

ROS-12

RAP-15

FAL-12

KRM-3

GOS-5

ROS-7

ROS-13ROS-11

ROS-3

ROS-9 ROS-10

GOS-6

KRM-4

ROS-15

GOS-7

FAL-19

RAP-20

KRM-8

EPL-3

HRS-12 HRS-11

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KRM-10

RAP-16

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23

3534

1

36

27 26 25

Barr Footer: Date: 12/1/2005 5:16:18 PM File: I:\Client\Vbwd\District\Project\WtrshdPlan\Watershed_maps\34-KramerPond_Watershed.mxd User: lkp

Figure 5.34-1KRAMER POND WATERSHEDValley Branch Watershed District

1,000 0 1,000 2,000500

Scale in Feet

ILEGEND

Project 1007Catch BasinManhole CoverOpen ChannelPipeMN-DOT Pipe

Overflow Path from Semi-Landlocked Watershed

Subwatershed Contributing RunoffOverflow Path from Landlocked Watershed(Non-Contributing Subwatershed)

Major Watershed DivideSubwatershed Divide

Lakes, Ponds, Wetlands,Approximate Normal Water Surface Level

VBWD Legal Boundary

KRM-1 Subwatershed Designation82-117W DNR Protected Waters Designation

Municipal Boundary

FL-100 100 Year Flood LevelNL Normal LevelAF Acre Feet of Storage at 100 Year Flood Level

DNR Established Ordinary High Water ElevationOHW

Lakes, Ponds Wetlands, Approximate 100 Year Flood Surface Level

Kramer Pond Watershed

Landlocked: Basin does not overflow using VBWD simplified method for calculating its 100-year flood level or using a more detailed analysis, such as the 1% probability flood level.

Semi-Landlocked: Basin does not overflow in the 100-year 24-hour rainfall total or the 100-year 10-day snowmelt event, but does overflow when calulating its 100-year flood level based on the VBWD simplified method or the 1% probablility flood level.

Section Lines

&-

!.

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§̈¦94§̈¦94

456719

456710

456717

456719

©̈17B

1,500 0 1,500 3,000Feet

Figure 5.34-2KRAMER POND WATERSHED

CURRENT (2010) AND FUTURE (2030) LANDUSE2015-2025 Watershed Management Plan

Valley Branch Watershed District

Barr Footer: ArcGIS 10.2.2, 2015-01-05 16:45 File: I:\Client\VBWD\District\Work_Orders\2015_Watershed_Mgmt_Plan\Maps\Reports\Draft_2015_Plan\Section05\Fig0534_02_KramerPond LandUse.mxd User: mjw

ICurrent (2010) Land Use

FarmsteadSeasonal/VacationSingle Family DetachedManufactured Housing ParkSingle Family AttachedMultifamilyRetail and Other Commercial

OfficeMixed Use ResidentialMixed Use IndustrialMixed Use Commercial and OtherIndustrial and UtilityExtractiveInstitutionalPark, Recreational or Preserve

Golf CourseMajor HighwayRailwayAirportAgriculturalUndevelopedWater

Kramer Pond SubwatershedMajor Subwatershed BoundaryVBWD Legal Boundary

Source: Metropolitan Council 2010

§̈¦94§̈¦94

456719

456710

456717

456719

©̈17B

1 inch = 1,500 feet

Future (2030) Land UseAgriculturalRural or Large-Lot ResidentialSingle Family ResidentialMultifamily ResidentialCommercial

IndustrialInstitutionalMixed UseMulti-Optional DevelopmentPark and RecreationOpen Space or Restrictive Use

Rights-of-Way (i.e., Roads)Railway (inc. LRT)AirportVacant or UnknownOpen Water

Kramer Pond SubwatershedMajor Subwatershed BoundaryVBWD Legal Boundary

Current (2010) Land Use Future (2030) Land Use

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0

200

400

600

800

1000

1200

2000 2002 2004 2006 2008 2010 2012 2014

Jun

e-S

ep

t. A

vera

ge T

ota

l Ph

osp

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rus

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Kramer Pond June-Sept. Average Total Phosphorus

0

50

100

150

200

250

300

350

2000 2002 2004 2006 2008 2010 2012 2014

Jun

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ug/

L)

Kramer Pond June-Sept. Average Chlorophyll a

0.0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

2000 2002 2004 2006 2008 2010 2012 2014

Jun

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ep

t. A

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ecc

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isk

Tran

spar

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m)

Kramer Pond June-Sept. Secchi Disk Transparency

Figure 5.34-3

Kramer Pond Water Quality 2015 - 2025 Watershed Management Plan

Valley Branch Watershed District

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906

908

910

912

914

916

918

1/1

/2008

1/1

/2009

1/1

/2010

1/1

/2011

1/1

/2012

1/1

/2013

1/1

/2014

1/1

/2015

Ele

vati

on

(ft

, M

SL

)

Date

Water Level 100-Year Flood Level Discharge Elevation

Figure 5.34-4

KRAMER POND WATER LEVELS 2015 - 2025 Watershed Management Plan

Valley Branch Watershed District

Observed elevations in NGVD29 datum 100-year flood level in NAVD88 datum Pond is landlocked

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Appendix A-5.34 Additional Macrophyte Information

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N

KRAMER POND

MACROPHYTE SURVEY

JUNE 9, 2003

NOT TO SCALE

WaterQuality

MonitoringLocation

Wetland (grasses, sedges)

Scirpus spp.

Elodea canadensis 1

Potamogeton spp. 1

Vallisneria americana 1

Filamentous algae

in this area

Potamogeton spp. 2-3

Berm

Scirpus spp.

Sagittaria spp.

Submerged Aquatic Plants:

Common Name Scientific Name

Floating Leaf:

Emergent:

No Aquatic Vegetation Found:

No Macrophytes Found in Water > 2-3 FeetMacrophyte Densities Estimated as Follows: 1 = Light; 2 = Moderate; 3 = Heavy

Potamogeton spp. (narrowleaf)

Vallisneria americana

Elodea canadensis

Scirpus spp.

Sagittaria spp.

Narrowleaf pondweed

Water celery

Elodea

Bulrush

Arrowhead

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KRAMER POND

MACROPHYTE SURVEY

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MonitoringLocation

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Elodea canadensis 1-2

Potamogeton spp. 1

Vallisneria americana 1

Ceratophyllum demersum 1

Najas spp. 1

Filamentous algae

in this area

Potamogeton spp. 2-3

Berm

Scirpus spp.

Sagittaria spp.

Typha spp.

Scirpus spp.

Sagittaria spp.

Sagittaria spp.

Sagittaria spp.

Sagittaria spp.

Submerged Aquatic Plants:

Common Name Scientific Name

Floating Leaf:

Emergent:

No Aquatic Vegetation Found:

No Macrophytes Found in Water > 2-3 FeetMacrophyte Densities Estimated as Follows: 1 = Light; 2 = Moderate; 3 = Heavy

Potamogeton spp. (narrowleaf)

Vallisneria americana

Elodea canadensis

Najas spp.

Ceratophyllum demersum

Scirpus spp.

Sagittaria spp.

Typha spp.

Narrowleaf pondweed

Water celery

Elodea

Bushy pondweed and naiad

Coontail

Bulrush

Arrowhead

Cattail

Wetland (grasses, sedges, bulrush)

Page 15: List of Tables List of Figures - vbwd.org...Water quality sampling was conducted on Kramer Pond in 2003, 2008, 2009, 2010, 2012, and 2013. Water quality samples are typically analyzed

Najas sp. - 1

Nitella sp. - 1Scirpus acutus

Sagittaria sp.

Scirpus acutus

Scirpus acutus

Scirpus atrovirens

Scirpus atrovirens

Eleocharis palustris

Ceratophyllum demersum - 1Elodea canadensis - 1

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Imagery Source: 2008 AE

KRAMER POND MACROPHYTESURVEY RESULTS

June 4, 2009Valley Branch Watershed District

FIELD NOTES:- No macrophytes found in water > 1-2 feet.- Macrophyte densities estimated as follows: 1=light; 2=moderate; 3=heavy

LegendEmergent PlantsFloating Leaf PlantsSubmerged Aquatic PlantsNo Aquatic VegetationCommon Name Scientific Name

coontail Ceratophyllum demersumstonewort Nitella sp.bushy pondweed Najas sp.Canada waterweed Elodea canadensis

Common Name Scientific Name

arrowhead Sagittaria sp.green bulrush Scirpus atrovirenshardstem bulrush Scirpus acutuscreeping spikerush Eleocharis palustris

Submerged Aquatic Plants

Floating Leaf Plants

Emergent Plants

None Found

Water QualityMonitoring Location

Page 16: List of Tables List of Figures - vbwd.org...Water quality sampling was conducted on Kramer Pond in 2003, 2008, 2009, 2010, 2012, and 2013. Water quality samples are typically analyzed

!?Water QualityMonitoring Location

3.5’ deep silt / clay

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Imagery Source: 2009 AE

KRAMER POND MACROPHYTESURVEY RESULTS

June 5, 2012Valley Branch Watershed DistrictFIELD NOTES:

- No macrophytes found in water > 1-2 feet.- Macrophyte densities estimated as follows: 1=light; 2=moderate; 3=heavy- High water level

Emergent Plants

Floating Leaf Plants

Submerged Aquatic Plants

No Aquatic Vegetation

!? Water Quality Monitoring Location

Submerged Aquatic Plants

Floating Leaf Plants

None Found

Emergent Plants

None Found

None Found