APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer...

56
APPENDIX A Air Quality Data

Transcript of APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer...

Page 1: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

APPENDIX A Air Quality Data

Page 2: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1
Page 3: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

APPENDIX A-1 URBEMIS2007 Output – Operational Worker

Trips

Prepared by Impact Sciences, Inc. August 2008

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INTENTIONALLY LEFT BLANK

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2008

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2:04

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Pag

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% o

f Trip

s -

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Pag

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Page 11: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

APPENDIX A-2 URBEMIS2007 Output – Operational Emissions

under Current Zoning

Prepared by Impact Sciences, Inc. August 2008

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INTENTIONALLY LEFT BLANK

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2008

4:5

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PM

Pag

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Urb

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Page 16: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

8/9/

2008

4:5

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Page 17: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

8/9/

2008

4:5

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Page 18: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

8/9/

2008

4:5

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Page 19: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

8/9/

2008

4:5

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Page 20: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

8/9/

2008

4:5

9:01

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Pag

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Page 21: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

8/9/

2008

4:5

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Page 22: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

8/9/

2008

4:5

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Page 23: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

8/9/

2008

4:5

3:24

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Page 24: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

8/9/

2008

4:5

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Page 25: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

8/9/

2008

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Page 26: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

8/9/

2008

4:5

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ter

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itiga

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lysi

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ear:

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9 T

empe

ratu

re (

F):

50

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son:

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ter

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fac:

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: E

mfa

c200

7 V

2.3

Nov

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lude

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pass

by tr

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stm

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or in

tern

al tr

ips

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gs:

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a S

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e C

hang

es to

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aults

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8/9/

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8/9/

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APPENDIX A-3 Health Risk Screening Assessment

Prepared by Environ Corporation

March 2008

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INTENTIONALLY LEFT BLANK

Page 31: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

Marketplace Tower, 6001 Shellmound Street, Suite 700, Emeryville, CA 94608 Tel: 510. 655.7400 Fax: 510.655.9517

www.environcorp.com

March 25, 2008

Ms. Emily Keller Senior Scientist, Wetlands and Wildlife Biologist PBS&J 1200 Second Street Sacramento, CA 95814

RE: Health Risk Screening Analysis - Proposed Sacramento Natural Gas Storage Project, Florin Gas Field Facility

Dear Ms. Keller:

At the request of PBS&J, ENVIRON International Corporation (ENVIRON) performed an ambient air quality health risk screening analysis (HRSA) of the toxic air contaminant (TAC) emissions from a glycol dehydration unit associated with the Sacramento Natural Gas Storage Project at the Florin Gas Field (the “Project”) in Sacramento, California (the “Site”). Our analysis indicates that the proposed operations of the Project are not expected to have a significant human health risk impact as defined under Sacramento Metropolitan Air Quality Management District (SMAQMD) California Environmental Quality Act (CEQA) Guidelines.

Process

ENVIRON performed this HRSA using information obtained from PBS&J. This HRSA reflects the fact that we utilized conservative methodologies for:

1) the estimation of TAC emissions, 2) the calculation of screening-level airborne TAC concentrations at offsite receptors, and 3) the estimation of cancer risks and non-cancer hazards at these receptors.

Potential incremental health effects resulting from exposure to projected emissions of TAC associated with the Project were evaluated for hypothetical offsite workers and offsite residential receptors nearby the Site boundary. Two sensitive offsite receptors representing Still Water’s Academy and Elder Creek Elementary were also considered. ENVIRON evaluated potential exposures to TAC emission at these locations using conservative (i.e., health protective) exposure parameters consistent with the California Environmental Protection Agency (Cal/EPA) Office of Environmental Health Hazard Assessment (OEHHA) risk screening guidance.1

Using an established emission estimation model developed by the Gas Research Institute (GRI) for use in regulatory permitting projects (GRI-GLYCalc 4.0), ENVIRON estimated

1 California Environmental Protection Agency (Cal/EPA). 2003. The Air Toxics Hot Spots Program

Guidance Manual for Preparation of Health Risk Assessments. Office of Environmental Health Hazard Assessment. August.

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Ms. Emily Keller - 2 - March 25, 2008 TAC emissions for the glycol dehydration unit. Parameters used for GRI-GLYCalc and emission estimates are shown in Table 1. GRI-GLYCalc estimates emissions of the BTEX compounds (i.e., benzene, toluene, ethyl benzene and xylenes) and n-hexane, all of which are considered TACs under OEHHA guidance.2

Consistent with SMAQMD-approved practices, TAC concentrations for estimated emissions at receptor locations were conservatively estimated using the United States Environmental Protection Agency (USEPA) air dispersion model SCREEN3, which represents worst-case scenario meteorological conditions. Parameters used in SCREEN3 modeling are shown in Table 2 and estimated one-hour maximum and annual average concentrations for BTEX and n-hexane are presented in Table 3. One-hour maximum concentrations estimated using SCREEN3 were converted to annual average concentrations using a conservative conversion factor of 0.1, per OEHHA guidance.3

Quantitative estimates of cancer risks and non-cancer health effects associated with potential offsite residential, offsite worker and offsite child exposure at nearby schools to TACs from the Project were then calculated based on the screening air dispersion modeling results. Exposure assumptions used in this analysis are presented in Table 4 and toxicity values are presented in Table 5. GRI-GLYCalc only estimates BTEX emissions as a composite, therefore all BTEX was assumed to be benzene as it has the highest toxicity of all BTEX compounds. This is a conservative assumption as BTEX emissions represent a mixture of compounds that have a composite toxicity lower than benzene.

As part of this HRSA, the estimated human health risks were compared to the thresholds for significance for TACs in the SMAQMD CEQA Guidelines for a maximally exposed individual (MEI). These results are shown in Table 6. The SMAQMD CEQA Guidelines thresholds correspond to the TAC concentration that would not pose an unacceptable health risk to offsite populations. According to the SMAQMD CEQA Guidelines, the threshold for significance for TACs is a cancer risk greater than ten in one million (1 x 10-5) and a non-cancer hazard index (HI) of greater than one for the MEI.4

Findings

The results of our analysis indicate that the estimated incremental cancer risks and non-cancer HIs for the offsite workers and offsite residents in the vicinity of Project and the offsite children at nearby schools are below the SMAQMD CEQA thresholds (i.e. an estimated cancer risk of less than ten in one million and an HI less than one), as summarized in Table 6. Thus, based on the results of this HRSA, the Project should not have a significant adverse impact on human health according to SMAQMD CEQA Guidelines.

2 Ibid. 3 Ibid. 4 Sacramento Metropolitan Air Quality Management District (SMAQMD). 2004. Guide to Air Quality

Assessment in Sacramento County. July.

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Ms. Emily Keller - 3 - March 25, 2008 To provide perspective for the results of a HRSA, OEHHA indicates that the estimated cancer risks can be “compared to the overall risk of cancer in the general U.S. population” or “to the risk posed by all harmful chemicals in a particular medium, such as air. The cancer risk from breathing current levels of pollutants in California’s ambient air over a 70-year lifetime is estimated to be 760 in one million.”5 Furthermore, the California Department of Health Services (DHS) reports that two in five Californians will be diagnosed with cancer during their lifetime, corresponding to a background cancer risk of 400,000 in one million.6

The many conservative assumptions that have been used in this screening assessment regarding the identification of truck traffic routes and associated emissions, estimation of ambient air concentrations, and exposure assumptions likely lead to an overestimate of potential risks, the magnitude of which could likely be substantial. The USEPA explains the effect of using conservative parameters in regulatory risk assessments as follows: 7

“These values are upper-bound estimates of excess cancer risk potentially arising from lifetime exposure to the chemical in question. A number of assumptions have been made in the derivation of these values, many of which are likely to overestimate exposure and toxicity. The actual incidence of cancer is likely to be lower than these estimates and may be zero.”

Closing

Thank you for the opportunity to complete this assignment. If you have any questions about our analysis or need further information, please feel free to contact Liz Miesner at 415.796.1938 or [email protected] or Michael Keinath at 510.420.2539 or [email protected].

Sincerely,

Michael Keinath, P.E. Elizabeth A. Miesner, M.S. Manager Principal

5 Office of Environmental Health Hazard Assessment (OEHHA) 2001. A Guide to Health Risk Assessment.

California Environmental Protection Agency. 6 California Department of Health Services (DHS), California Cancer Registry. 2006. Available at

http://www.dhs.ca.gov/cdic. 7 USEPA. 1989. Risk Assessment Guidance for Superfund: Volume 1- Human Health Evaluation Manual

(Part A). Interim Final. Washington, D.C. December.

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Ms. Emily Keller - 4 - March 25, 2008 Attachments:

Table 1: GRI-Glycalc 4.0 Inputs and Outputs

Table 2: SCREEN3 Modeling Parameters

Table 3: Summary of Receptor Concentrations

Table 4: OEHHA-Recommended Exposure Parameters for Evaluating Cancer Risk for Resident, Worker, and Child Receptors

Table 5: Inhalation Carcinogenic and Non-Carcinogenic Toxicity Values for Benzene and n-Hexane

Table 6: Summary of Carcinogenic Risks and Non-Cancer Hazard Indices

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Inputs Units ValueAnnual Hours of Operation hours 3075.0Wet gas temperature degrees F 97.00Wet gas pressure psig 250.00Wet Gas Water Content Saturated Composition of the wet gas1

Methane volume % 99.97% n-Hexane volume % 0.03%

BTEX volume % <0.01%Dry Gas Flow Rate2 MMSCF / day 225-314Dry Gas Water Content lbs H2O / MMSCF 7.0Lean Glycol Type: TEG Lean Glycol Water Content: weight % H2O 1.0%Lean Glycol Recirculation Ratio: gallons/lb H2O 3.0Glycol Pump Type Electric/Pneumatic Flash Tank Control3 Vented to atmosphere Flash Tank Temperature: degrees F 200.0Flash Tank Pressure: psig 75.0

Output

Annual BTEX Emissions(at Average Dry Gas Flow Rate)

lbs/yr 976

Maximum Hourly BTEX Emissions(at Maximum Dry Gas Flow Rate)

lbs/hr 0.44

Annual n-Hexane Emissions(at Average Dry Gas Flow Rate) lbs/yr 9,614

Sacramento, CA

Table 1GRI-Glycalc 4.0 Inputs and Outputs

SNGS Florin Facility

Notes: 1. Client data specified BTEX concentrations <1 ppm. To be conservative, ENVIRON assumed a concentration of 1 ppm of BTEX. 2. The average flow rate is 225 MMSCF/day; the maximum flow rate is 314 MMSCF/day. 3. Assumed to be conservative.

Abbreviations: BTEX - benzene, toluene, ethyl benzene, xylenes F - Fahrenheit hr - hour lb(s) - pound(s) MMSCF - million standard cubic feet ppm - parts per million TEG - triethylene glycol yr - year % - percent

Source: Inputs provided by client.

E N V I R O N

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Parameter Units ValueBTEX Emission Rate (1-hr maximum) 1 g/s 0.056BTEX Emission Rate (annual) 2 g/s 0.014n-Hexane Emission Rate (annual) 2 g/s 0.14Stack Height m 6.1Stack Diameter m 0.356Exit Velocity m/s 4.91Exit Temperature K 644

Air Temperature K 293

Table 2SCREEN3 Modeling Parameters

Sacramento, CASNGS Florin Facility

Notes: 1. 1-hour maximum emission rate = hourly emissions (lbs/hr)*453.59 g/lb / (3600 s/hr) 2. Annual emission rate = annual emissions (lbs/yr)*453.59 g/lb / (8760 hr/yr * 3600 s/hr)

Abbreviations: BTEX - benzene, toluene, ethyl benzene, xylenes g - gram hr - hour K - Kelvin lb - pound m - meter s - second yr - year

E N V I R O N

Page 37: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

BT

EX

1-H

our

Max

imum

C

once

ntra

tion1

BT

EX

Ann

ual A

vera

ge

Con

cent

ratio

n2n-

Hex

ane

Ann

ual A

vera

ge

Con

cent

ratio

n2

ug/m

3ug

/m3

ug/m

3

PMI

92 m

eter

s fro

m so

urce

180.

444.

4

ME

IW

Nea

rest

off

site

wor

ker i

dent

ified

at 1

50 m

eter

s nor

th o

r eas

t of s

ourc

e17

0.42

4.1

ME

IR

Nea

rest

resi

denc

e id

entif

ied

800

met

ers w

est o

f sou

rce

7.7

0.19

1.9

Still

Wat

er's

Aca

dem

y80

08 4

3rd

Ave

. (90

0 m

eter

s wes

t of s

ourc

e)6.

80.

171.

7

Eld

er C

reek

Ele

men

tary

7934

Lem

on H

ill A

ve. (

900

met

ers w

est o

f sou

rce)

6.8

0.17

1.7

Sacr

amen

to, C

A

Loc

atio

nR

ecep

tor

Tab

le 3

Sum

mar

y of

Rec

epto

r C

once

ntra

tions

SNG

S Fl

orin

Fac

ility

Not

es:

1. E

stim

ated

dire

ctly

usi

ng S

CR

EEN

3 w

ith th

e m

axim

um h

ourly

em

issi

on ra

te o

f BTE

X u

nder

the

max

imum

dry

gas

flow

rate

of 3

14 M

MSC

F/da

y. 2

. Est

imat

ed u

sing

SC

REE

N3

to e

stim

ate

a 1-

hour

max

imum

con

cent

ratio

n fo

r the

em

issi

ons o

f BTE

X a

nd n

-hex

ane

unde

r the

ave

rage

dry

gas

flow

rate

of 2

25 M

MSC

F/da

y an

d th

en sc

alin

g th

e 1-

hour

max

imum

co

ncen

tratio

n to

an

annu

al c

once

ntra

tion

usin

g th

e fa

ctor

0.1

, as r

ecom

men

ded

by O

EHH

A g

uida

nce.

Abb

revi

atio

ns:

BTE

X -

benz

ene,

tolu

ene,

eth

yl b

enze

ne, x

ylen

es M

EIR

- M

axim

ally

Exp

osed

Indi

vidu

al R

esid

ent

MEI

W -

Max

imal

ly E

xpos

ed In

divi

dual

Wor

ker

MM

SCF

- mill

ion

stan

dard

cub

ic fe

et O

EHH

A -

Off

ice

of E

nviro

nmen

tal H

ealth

Haz

ard

Ass

essm

ent

PM

I - P

oint

of M

axim

um Im

pact

ug/

m3 -

mic

rogr

am p

er c

ubic

met

er

Sour

ce:

Cal

iforn

ia E

nviro

nmen

tal P

rote

ctio

n A

genc

y (C

al/E

PA).

2003

. "A

ir To

xics

Hot

Spo

ts P

rogr

am R

isk

Ass

essm

ent G

uide

lines

, the

Air

Toxi

cs H

ot S

pots

Pro

gram

Gui

danc

e M

anua

l for

Pre

para

tions

of H

ealth

Ris

k A

sses

smen

ts,"

Off

ice

of E

nviro

nmen

tal H

ealth

Haz

ard

Ass

essm

ent,

Aug

ust.

E N

V I

R O

N

Page 38: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

Exp

osur

e Pa

ram

eter

Uni

tsR

esid

ent

Wor

ker

Chi

ld

Dai

ly B

reat

hing

Rat

e 1[L

/kg-

day]

302

149

581

Expo

sure

Tim

e[h

ours

/day

]24

88

Expo

sure

Fre

quen

cy[d

ays/

year

]35

024

518

0Ex

posu

re D

urat

ion

[yea

rs]

7040

9C

onve

rsio

n Fa

ctor

(CF)

[m3 /L

]0.

001

0.00

10.

001

Ave

ragi

ng T

ime

[day

s]25

550

2555

025

550

Inta

ke F

acto

r, In

hala

tion

(IF i

nh)2

[m3 /k

g-da

y]0.

290.

057

0.01

2

Tab

le 4

OE

HH

A-R

ecom

men

ded

Exp

osur

e Pa

ram

eter

s for

Eva

luat

ing

Can

cer

Ris

k fo

r R

esid

ent,

Wor

ker,

and

Chi

ld R

ecep

tors

Sacr

amen

to, C

ASN

GS

Flor

in F

acili

ty

Not

es:

1. R

esid

ent u

ses 8

0th

perc

entil

e br

eath

ing

rate

use

d pe

r AR

B G

uida

nce.

Wor

ker a

nd c

hild

use

hig

h en

d va

lues

per

OEH

HA

. 2

. Res

iden

t and

wor

ker:

IFin

h =

(Bre

athi

ng R

ate*

Expo

sure

Fre

quen

cy*E

xpos

ure

Dur

atio

n*C

F)/(A

vera

ging

tim

e)

C

hild

: IF

inh

= (B

reat

hing

Rat

e*[E

xpos

ure

Tim

e/24

hou

rs]*

Expo

sure

Fre

quen

cy*E

xpos

ure

Dur

atio

n*C

F)/(A

vera

ging

tim

e)

Abb

revi

atio

ns:

CF

- con

vers

ion

fact

or I

Finh

- in

hala

tion

inta

ke fa

ctor

kg

- kilo

gram

l -

liter

m -

met

er O

EHH

A =

Off

ice

of E

nviro

nmen

tal H

ealth

Haz

ard

Ass

essm

ent

Sour

ce:

Cal

iforn

ia A

ir R

esou

rces

Boa

rd (A

RB

). 20

03.

"Air

Res

ourc

es B

oard

Rec

omm

ende

d In

terim

Ris

k M

anag

emen

t Pol

icy

for I

nhal

atio

n-B

ased

Res

iden

tial C

ance

r Ris

k."

Oct

ober

9.

Cal

iforn

ia E

nviro

nmen

tal P

rote

ctio

n A

genc

y (C

al/E

PA).

2003

. "A

ir To

xics

Hot

Spo

ts P

rogr

am R

isk

Ass

essm

ent G

uide

lines

, the

Air

Toxi

cs H

ot S

pots

Pro

gram

Gui

danc

e M

anua

l for

Pre

para

tions

of H

ealth

Ris

k A

sses

smen

ts,"

Off

ice

of E

nviro

nmen

tal H

ealth

Haz

ard

Ass

essm

ent,

Aug

ust .

E N

V I

R O

N

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Che

mic

al

CPF

(mg/

kg-d

ay)-1

Sour

ce C

hron

ic R

EL

(u

g/m

3 ) R

efer

ence

A

cute

RE

L

(ug/

m3 )

Sour

ce

Ben

zene

10.

10 C

al/E

PA 2

007

60

Cal

/EPA

200

5

1300

Cal

/EPA

200

3n-

Hex

ane

7000

Cal

/EPA

200

5

Not

es:

CPF

= C

ance

r pot

ency

fact

orPM

= P

artic

ulat

e m

atte

r(m

g/kg

-day

)-1 =

per

mill

igra

m p

er k

ilogr

am-d

ayR

EL =

Ref

eren

ce e

xpos

ure

leve

lug

/m3 =

mic

rogr

am p

er c

ubic

met

er

Ref

eren

ces:

Cal

iforn

ia E

nviro

nmen

tal P

rote

ctio

n A

genc

y (C

al/E

PA).

2005

b. A

ll C

hron

ic R

efer

ence

Exp

osur

eLe

vels

Ado

pted

by

Off

ice

of E

nviro

nmen

tal H

ealth

Haz

ard

Ass

essm

ent (

OEH

HA

) . F

ebru

ary.

Cal

iforn

ia E

nviro

nmen

tal P

rote

ctio

n A

genc

y (C

al/E

PA).

2007

a. C

alifo

rnia

Can

cer P

oten

cy V

alue

s.O

ffic

e of

Env

ironm

enta

l Hea

lth H

azar

d A

sses

smen

t. A

pril

9.

NA

NA

Tab

le 5

Sacr

amen

to, C

A

Inha

latio

n C

arci

noge

nic

and

Non

-Car

cino

geni

c T

oxic

ity V

alue

s for

Ben

zene

and

n-H

exan

eSN

GS

Flor

in F

acili

ty

Not

es:

1.

BTE

X a

ssum

ed to

be

100%

ben

zene

as i

t has

the

high

est t

oxic

ity o

f BTE

X c

ompo

unds

.

Abb

revi

atio

n: B

TEX

- be

nzen

e, to

luen

e, e

thyl

ben

zene

, xyl

enes

CPF

- C

ance

r Pot

ency

Fac

tor

NA

- no

t app

licab

le R

EL -

Ref

eren

ce e

xpos

ure

leve

l (

mg/

kg-d

ay)-

1 - m

illig

ram

per

kilo

gram

-day

ug/

m3 -

mic

rogr

am p

er c

ubic

met

er

Sour

ce:

Cal

iforn

ia E

nviro

nmen

tal P

rote

ctio

n A

genc

y (C

al/E

PA).

2003

. Air

Toxi

cs H

ot S

pots

Pro

gram

Ris

k A

sses

smen

t G

uide

lines

, the

Air

Toxi

cs H

ot S

pots

Pro

gram

Gui

danc

e M

anua

l for

Pre

para

tions

of H

ealth

Ris

k A

sses

smen

ts,"

O

EHH

A, A

ugus

t.

Cal

iforn

ia E

nviro

nmen

tal P

rote

ctio

n A

genc

y (C

al/E

PA).

2005

. All

Chr

onic

Ref

eren

ce E

xpos

ure

Leve

ls A

dopt

ed b

y O

ffic

e of

Env

ironm

enta

l Hea

lth H

azar

d A

sses

smen

t (O

EHH

A).

Janu

ary.

Cal

iforn

ia E

nviro

nmen

tal P

rote

ctio

n A

genc

y (C

al/E

PA).

2007

. Cal

iforn

ia C

ance

r Pot

ency

Val

ues.

Off

ice

of

Envi

ronm

enta

l Hea

lth H

azar

d A

sses

smen

t. A

pril

9.

E N

V I

R O

N

Page 40: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

Can

cer

Ris

kC

hron

ic H

I 1A

cute

HI

(in a

mill

ion)

PMI 2

92 m

eter

s fro

m so

urce

130.

008

0.01

4

ME

IW 3

Nea

rest

off

site

wor

ker i

dent

ified

at 1

50 m

eter

s nor

th o

r eas

t of s

ourc

e2

0.00

170.

013

ME

IRN

eare

st re

side

nce

iden

tifie

d 80

0 m

eter

s wes

t of s

ourc

e6

0.00

350.

0059

Still

Wat

er's

Aca

dem

y 4

8008

43r

d A

ve. (

900

met

ers w

est o

f sou

rce)

0.2

0.00

310.

0052

Eld

er C

reek

Ele

men

tary

479

34 L

emon

Hill

Ave

. (90

0 m

eter

s wes

t of s

ourc

e)0.

20.

0031

0.00

52

101

1SM

AQ

MD

Sig

nific

ance

Thr

esho

ld

Loc

atio

nR

ecep

tor

Tab

le 6

Sum

mar

y of

Car

cino

geni

c R

isks

and

Non

-Can

cer

Haz

ard

Indi

ces

SNG

S Fl

orin

Fac

ility

Sacr

amen

to, C

A

Not

es:

1.

Chr

onic

HI =

HQ

benz

ene +

HQ

n-he

xane

2.

The

PM

I ref

lect

s res

iden

t exp

osur

e as

sum

ptio

ns, t

houg

h th

ere

are

no re

side

nces

at t

his l

ocat

ion.

The

refo

re, t

he S

MA

QM

D S

igni

fican

ce T

hres

hold

is n

ot

exce

eded

. 3

. Pe

r OEH

HA

gui

danc

e, th

e ai

r con

cent

ratio

n us

ed in

eva

luat

ion

of th

e ch

roni

c H

I for

the

MEI

W w

as a

djus

ted

to a

ccou

nt fo

r non

-con

tinuo

us e

xpos

ure

(e.g

., 24

5 da

ys/3

65 d

ays a

nd 8

hou

rs/2

4 ho

urs)

. 4

. A

s a c

onse

rvat

ive

estim

ate,

no

adju

stem

nt w

as m

ade

for e

xpos

ure

dura

tion

at th

e sc

hool

rece

ptor

s. A

bbre

viat

ions

: H

I - H

azar

d In

dex

HQ

- H

azar

d Q

uotie

nt M

EIR

- M

axim

ally

Exp

osed

Indi

vidu

al R

esid

ent

MEI

W -

Max

imal

ly E

xpos

ed In

divi

dual

Wor

ker

PM

I - P

oint

of M

axim

um Im

pact

SM

AQ

MD

- Sa

cram

ento

Met

ropo

litan

Air

Qua

lity

Man

agem

ent D

istri

ct

Sour

ce:

Cal

iforn

ia E

nviro

nmen

tal P

rote

ctio

n A

genc

y (C

al/E

PA).

2003

. Air

Toxi

cs H

ot S

pots

Pro

gram

Ris

k A

sses

smen

t Gui

delin

es, t

he A

ir To

xics

Hot

Spo

ts P

rogr

am

Gui

danc

e M

anua

l for

Pre

para

tions

of H

ealth

Ris

k A

sses

smen

ts,"

OEH

HA

, Aug

ust.

Sac

ram

ento

Met

ropo

litan

Air

Qua

lity

Man

agem

ent D

istri

ct (S

MA

QM

D).

200

4. G

uide

to A

ir Q

ualit

y A

sses

smen

t in

Sacr

amen

to C

ount

y. J

uly.

E N

V I

R O

N

Page 41: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

APPENDIX A-4 Odor Analysis

Prepared by Impact Sciences, Inc.

August 2008

Page 42: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

INTENTIONALLY LEFT BLANK

Page 43: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

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Page 44: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

INTENTIONALLY LEFT BLANK

Page 45: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

APPENDIX A-5 Greenhouse Gas Emissions—Construction

Prepared by Dudek

August 2008

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INTENTIONALLY LEFT BLANK

Page 47: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

Adjustment of Estimated Construction Emissionsto Account for Other GHG Emissions

from Construction Worker Vehicle Trips

Emission SourceData

SourceWorker Trips 1 392 tons CO2

2 413 tons CO2E

Project Total 1 979 tons CO2

Diesel Equipment and Vehicles calc 587 tons CO2

Adjusted Total calc 1,000 tons CO2Ecalc 907 metric tons CO2E

Notes:1. tons of CO2 from SNGS, Supplemental PEA (2007).2. US EPA, Office of Transportation and Air Quality, Greenhouse Gas Emissions from a Typical Passenger Vehicle (EPA420-F-05-004) , (2005) 4

Project Construction Emissions

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INTENTIONALLY LEFT BLANK

Page 49: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

APPENDIX A-6 Greenhouse Gas Emissions—Operational

Prepared by Dudek and Impact Sciences, Inc.

August 2008

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INTENTIONALLY LEFT BLANK

Page 51: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

Sac

ram

ento

Nat

ural

Gas

Sto

rage

Com

pari

son

of G

reen

hous

e G

as E

mis

sion

s fr

om E

lect

ric

Mot

ors

and

Nat

ural

Gas

-Fir

ed In

tern

al C

ombu

stio

n E

ngin

es

CO

2EC

O2E

Em

issi

onE

mis

sion

Ann

ual C

O2E

Ann

ual C

O2E

Fact

or 3

Fact

or 4

Em

issi

ons

Em

issi

ons

Sou

rce

Ann

ual E

nerg

y U

sage

(lbs

CO

2E/k

W-h

r)(lb

s C

O2E

/MM

Btu

)(t

ons

CO

2E/y

r)(M

T C

O2E

/yr)

Ele

ctric

Mot

or-D

riven

Com

pres

sors

16,

222,

000

kWh/

yr0.

714

2,22

1

2,01

5

Eng

ine-

Driv

en C

ompr

esso

rs 2

63,1

93M

MB

tu/y

r11

7.3

3,70

7

3,36

3

Diff

eren

ce in

GH

G E

mis

sion

s(1

,486

)

(1,3

48)

Sou

rces

:1.

SN

GS

est

imat

es th

at th

e el

ectri

c-po

wer

ed c

ompr

esso

rs w

ould

use

6,2

22,0

00 k

Wh/

yr fo

r inj

ectin

g ga

s in

to th

e re

serv

oir.

2. A

ssum

ptio

ns fo

r eng

ine-

pow

ered

com

pres

sors

Com

pres

sors

wou

ld b

e dr

iven

by

two

Cat

erpi

llar 3

612

engi

nes

rate

d at

3,5

50 H

P e

ach.

Eng

ines

wou

ld c

ombu

st 7

,470

Btu

/HP

-hr a

t HH

V.

Eng

ines

wou

ld o

pera

te a

t equ

ival

ent l

evel

s (h

ours

and

load

) to

that

for e

lect

ric-p

ower

ed c

ompr

esso

rs.

3. S

MU

D. A

nnua

l Em

issi

ons

Rep

ort.

http

s://w

ww

.clim

ater

egis

try.o

rg/C

AR

RO

T/p

ublic

/Rep

orts

.asp

x (R

epor

t is

for 2

006,

but

it a

lso

repo

rts d

ata

for 2

007)

.

T

able

s C

.6 a

nd C

.7.

Whe

re:

CO

2EC

arbo

n di

oxid

e eq

uiva

lent

kW-h

rki

low

att-h

our

lbs

poun

dsM

Tm

etric

tons

(= 2

,204

.623

lbs)

yrye

ar

4. C

alifo

rnia

Clim

ate

Act

ion

Reg

istry

, Gen

eral

Rep

ortin

g P

roto

col:

Rep

ortin

g E

ntity

-Wid

e G

reen

hous

e G

as E

mis

sion

s V

ersi

on 3

.0, (

2008

)

Page 52: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

Sacramento Natural Gas Storage

Heat Input Rating 3.0 MMBtu/hrOperating Hours 3,075 hr/yr

CO2 CH4 N2OEmission Factor kg/MMBtu 53.06 0.0059 0.0001Global Warming Potential 1 21 310

Greenhouse Gas Emissions metric ton/yr 491tons/yr 541

Source:Operating Hours: Environ, Health Risk Assessment Screening Analysis - ProposedSNGS Project, 3/25/08.Emission Factors for Natural Gas Combustion: CCAR, General Reporting Protocol, 2008.

Greenhouse Gas Emissions from Glycol Reboiler

Impact Sciences, Inc. August 2008

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8/11

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8/11

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8/11

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Page 56: APPENDIX A dividers - California Public Utilities … Home-Shop Home-Other Commute Non-Work Customer Residential Commercial Urban Bus 0.0 0.0 0.0 0.0 Motor Home 0.0 11.1 77.8 11.1

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