Document 2137989

EXHIBIT 1
July 24, 2013
ested Partie
es:
To Intere
LUTION NO
O. R6V-2013-0060 CE
ERTIFYING
G A FINAL
ADOPTED RESOL
ONMENTAL
L IMPACT REPORT, COMPREH
HENSIVE G
GROUNDW
WATER
ENVIRO
CLEANU
UP STRAT
TEGY FOR HISTORIC
CAL CHRO MIUM DISC
CHARGES
S FROM
PACIFIC
C GAS & ELECTRIC
E
COMPANY
C
Y'S HINKLE
EY COMPR
RESSOR STATION,
SAN BE
ERNARDIN
NO COUNTY
Y
Enclosed is a copy
y of Resoluttion No. R6V-2013-006
60 that wass adopted a
at the Regio
onal
Board meeting
m
held
d in Barstow
w, CA on Ju
uly 17 & 18
8, 2013. If yyou have an
ny questions,
please contact
c
our office at (5
530) 542-54
400.
Amber Wike
W
Office Technician
Enclosure
CALIFORNIA REGIONAL WATER QUALITY CONTROL BOARD
LAHONTAN REGION
RESOLUTION NO. R6V-2013-0060
CERTIFYING A FINAL ENVIRONMENTAL IMPACT REPORT
FOR
COMPREHENSIVE GROUNDWATER CLEANUP STRATEGY FOR HISTORICAL
CHROMIUM DISCHARGES FROM PACIFIC GAS AND ELECTRIC COMPANY'S
HINKLEY COMPRESSOR STATION (STATE CLEARINGHOUSE NO. 2008011097)
_________________________San Bernardino County__________________________
WHEREAS the California Regional Water Quality Control Board, Lahontan Region
(Water Board), finds:
1) The Pacific Gas and Electric Company's (PG&E's) Hinkley Compressor Station is
located southeast of the community of Hinkley, about 8 miles west of Barstow in
San Bernardino County. The Compressor Station has operated since 1952.
From 1952 to 1965, hexavalent chromium-based corrosion inhibitor was added to
water used in the cooling towers, and the untreated cooling tower water was
discharged to unlined evaporation ponds. The unlined ponds have since been
closed, covered, and replaced by lined evaporation ponds. In 1987, PG&E
reported to the State that total chromium and hexavalent chromium
concentrations exceeding the California drinking water standard of 50 parts per
billion (ppb) total chromium were found in groundwater beneath and down
gradient of the site.
2) Since 1987, The Water Board has been requiring PG&E to carry out investigation
and cleanup actions for chromium in groundwater at the Hinkley Compressor
Station. Various cleanup methods have been operated on a limited-scale basis
to stop the spreading of chromium in groundwater and to test cleanup methods to
remove chromium from soils and groundwater, including excavation of
contaminated soil, groundwater extraction and agricultural land treatment, in-situ
(subsurface) treatment, and freshwater injection into the aquifer.
3) In Cleanup and Abatement Order (CAO) No. R6V-2008-0002 dated
August 6, 2008, the Water Board directed PG&E, among other things, to develop
a Feasibility Study for a comprehensive cleanup strategy for chromium in
groundwater. Amended CAO R6V-2008-0002A1 established background
chromium concentrations to be used to assess cleanup strategies.
-2-
Resolution No. R6V-2013-0060
4) PG&E submitted a Feasibility Study (FS), dated August 2010, presenting four
action alternatives for final cleanup of the chromium-contaminated groundwater,
along with a "no action" alternative. The action alternatives involved different
combinations and intensities of four cleanup technologies, three of which were
already being implemented on a limited scale (as described in finding 2, above).
In addition to the three implemented technologies, the FS also proposed ex-situ
remediation, which involves groundwater extraction and chromium removal at an
aboveground facility. The four action alternatives evaluated cleanup to the
currently adopted maximum background levels of 3.1 parts per billion (ppb)
hexavalent chromium and 3.2 ppb total chromium. The 2010 FS estimated the
time required to clean up groundwater to maximum background levels ranged
from 110 to 260 years.
5) Current cleanup activities are regulated under individual and general Waste
Discharge Requirements (WDRs) and/or monitoring orders. Implementation of
any final cleanup proposal will require new and/or additional WDRs. The
expansion of remediation activities using existing or new technologies may result
in potentially significant impacts to the environment that were not analyzed in
previous environmental documents. In addition to issuing general (project areawide) WDRs for implementation of the cleanup, the Water Board will also
consider issuance of a new CAO, which will specify cleanup levels and time
requirements. The issuance of new WDRs and a CAO are discretionary actions
subject to the California Environmental Quality Act (CEQA). Therefore, the Water
Board, as Lead Agency in accordance with CEQA, must certify an Environmental
Impact Report (EIR) before taking these discretionary actions.
6) On November 24, 2010, a Notice of Preparation of a Draft EIR was circulated for
a 30-day comment period. A CEQA scoping meeting was held in Hinkley to gain
input from the public on the scope and content of the Draft EIR. As required by
California Water Code section 13307.5, a 30-day public review period on the
Feasibility Study was also initiated.
7) On January 26 and 27, 2011, Water Board staff held public information meetings
in Hinkley to discuss comments received on PG&E's FS and the scope and
content of the EIR, and provide information on the chromium plume boundary
and PG&E's cleanup activities.
8) At its regular meeting in March 2011, the Water Board held a public workshop on
the Draft EIR. The workshop focused on key issues to be examined in the Draft
EIR, including cleanup levels to be considered in the EIR; whether the
alternatives in PG&E's FS represented a reasonable range of cleanup times and
best available technologies; and the types of environmental impacts that should
be considered in the EIR. Members of the public expressed concerns over the
lengthy time periods required for all alternatives to achieve final cleanup.
-3-
Resolution No. R6V-2013-0060
9) Water Board staff requested review of PG&E's FS from the California
Department of Toxic Substances Control and the US Environmental Protection
Agency. Both agencies had suggestions to strengthen the FS, but generally
agreed that the range of technologies proposed represented best available
technologies for chromium groundwater remediation.
10) To address concerns over the cleanup times estimated in PG&E's FS, Water
Board staff directed PG&E to propose additional alternatives with reduced
cleanup times. Throughout 2011 and into 2012, PG&E submitted FS addenda
proposing optimized combinations of the four cleanup technologies to reduce the
time required to clean up the chromium from groundwater. Staff selected five of
the most promising optimized alternatives to analyze in the Draft EIR, along with
the "No Project" alternative as required by CEQA. The five action alternatives
estimated cleanup of groundwater to maximum background levels to take
between 29 to 50 years; estimates to clean up to the average background
hexavalent chromium level of 1.2 ppb ranged from 75 to 95 years. Cleanup of
groundwater to below 50 ppb chromium (the current drinking water standard for
chromium) were estimated to take between 3 and 20 years.
11) Throughout development of the EIR, the Water Board has sought to involve and
inform interested stakeholders, and to exceed the public noticing and review
requirements specified by CEQA. For example, from 2010 through 2013, Water
Board staff held seven informational meetings at the Hinkley School to hear
public input and provide information on the Draft EIR. The Draft EIR or related
topics were also on the agenda at five Water Board public meetings held in
Barstow during EIR development from 2011 through 2013. Spanish-language
interpreters were present at meetings and Spanish translation of notices, fact
sheets and meeting materials were provided.
12) On August 20, 2012, a Notice of Availability of a Draft EIR was mailed to
interested parties, distributed via an electronic mail subscription service, posted
to the Water Board's webpage, and published in three newspapers of regional
interest, including one Spanish-language newspaper. A Notice of Completion
was filed with the State Clearinghouse to notify responsible and trustee agencies
of the availability of the Draft EIR. The Draft EIR was circulated for a 76-day
public review and comment period, exceeding CEQA's 45-day review
requirement. At a Water Board meeting on September 12, 2012, the Draft EIR
was summarized, and a court reporter was present to transcribe all verbal
comments made to the Water Board on the Draft EIR. Two public information
meetings on the Draft EIR were also held in Hinkley in August and October 2012.
13) Following the close of the comment period, Water Board staff and its EIR
consultant, ICF International, prepared responses to comments and made
revisions to the Draft EIR. Comments received were summarized at a public
meeting of the Water Board on January 16, 2013, held in Barstow.
-4-
Resolution No. R6V-2013-0060
14) Revisions to the Draft EIR were made to provide additional detail and information
on several key issues raised during the comment period:






Expanded project boundaries to account for chromium detections in domestic
wells in the northern and western project areas
Identification of an "environmentally superior alternative"
Changed significance conclusion to “less than significant” for the impact of
potential aquifer compaction based on new information
Additional details on remediation byproducts, including requirements for
monitoring prior to any increase of in-situ remediation
Enhanced investigation on stability of trivalent chromium in soils
Literature evaluation of electrocoagulation technology
Numerous other revisions were made to provide clarity or additional information,
correct typographical errors, and improve readability. All revisions are clearly
shown in strikeout and underline format in Volume II of the Final EIR. Volume I
of the Final EIR contains comment letters, and responses to all comments
received, including those transcribed at the September 12, 2012 Water Board
meeting in Barstow.
15) Although not required by CEQA, the Water Board released the entire Final EIR
62 days prior to the Water Board's consideration of certification of the Final EIR.
This was not a recirculation of the EIR pursuant to CEQA, as none of the
revisions resulted in “significant new information”, as that term is defined in
CEQA regulations. Rather, recognizing the volume and complexity of the
document, staff opted to provide an extended period to review the responses and
revisions contained in the Final EIR.
16) On June 6, 2013, Water Board staff held a public meeting in Hinkley to review
the Final EIR, including the key revisions bulleted in finding 14, above. In
addition to the responses to comments, the Final EIR describes the cleanup
project's goals and objectives, provides details on five "action alternatives" to
meet those goals, and discusses impacts associated with each alternative.
Ways to avoid or reduce impacts (mitigation measures) are outlined. Impacts
which cannot be avoided or reduced to less than significant levels are clearly
identified in the Final EIR.
17) In a letter dated June 24, 2013 (shown in Attachment 1 to this Resolution), PG&E
requested changes to the Final EIR. Water Board staff's response to PG&E's
letter is included in Attachment 2, and proposed revisions to the Final EIR are
shown in Attachment 3 (Errata Sheet). The proposed revisions correct a
typographical error, and clarify certain mitigation requirements related to
biological resources. As such, the revisions are not significant new information to
the Final EIR, and recirculation is not required. The Attachments, including the
Errata Sheet are made a part of the Final EIR and its record.
-5-
Resolution No. R6V-2013-0060
18)Water Board staff will develop draft WDRs and a CAO for public review and
comment in fal l 2013. When the Water Board adopts WDRs and a CAO in winter
2014, it will make the findings required by CEQA sections 15091 th rough 15093,
regard ing any significant environmental effects of the project, including a
statement of overriding considerations before adopting a project which may result
in unavoidable significant impacts.
19)1 n summary, the Water Board finds that the record as whole demonstrates that
the Final EIR analyzes a reasonable range of alternatives which would feasibly
attain the project's goals and objectives, and would avoid or substantially lessen
the significant impacts of the project. Impacts wh ich cannot be avoided or
reduced to less than significant levels are clearly identified in the Final EIR.
Public involvement and consultation requirements of CEQA were met or
exceeded throug hout the development of the EIR.
THEREFORE, BE IT RESOLVED that:
Pursuant to§ 21080, et seq. of the California Public Resources Code, the Lahontan
Water Board, after considering the entire record , including written and oral testimony at
the hearing, certifies that:
a.
b.
c.
The Final EIR, including Attachments 1 and 2, and the Errata Sheet
(Attachment 3), has been completed in compliance with CEQA.
The Lahontan Water Board has reviewed and considered the information
in the Final EIR, and Attachments 1 and 2, and the Errata Sheet
(Attachment 3).
The Final EIR, Attachments 1 and 2, and Errata Sheet (Attachment 3)
reflect the independent judgment and analysis of the Lahontan Water
Board .
CERTIFICATION
I, Lauri Kemper, Acting Executive Officer, do hereby certify the foregoing is a full , true,
and correct copy of a Resolution adopted by the California Regional Water Quality
Control Board , Lahontan Region on July 17, 2013.
Rl KEMPER, P.
Acting Executive 0
Attachments:
1. Comment letter from PG&E, dated June 24, 2013
2. Water Board staff responses to PG&E letter
3. Errata Sheet, Final EIR
C
Comments
Respo
onses
1. Sign
nificant impacts rrelated to chrom
mium increases in
n a water
supply well are definedd in the EIR as exxceedances of th
he currently
d maximum bacckground levels. The maximum b
background
adopted
level fo
or Cr6 is currentlyy 3.1 ppb. There
e is no current M
MCL
specific
cally for Cr6.
gnificance criterioon is consistent with State Wate
er Board
This sig
Anti-de
egradation Policyy, which requiress that high qualityy waters be
maintaiined unless certaain findings are m
made, and Reso
olution 9249, which states, in parrt, that attaining b
background wate
er quality
s the goal for cleeanup and abate
ement of polluted
d
levels is
groundwater. Thereforre, using the maxximum backgrou
und value of
a
to deefine significant iimpacts under C
CEQA.
Cr6 is appropriate
ells due to
In order to mitigate incrreases in Cr6 in water supply we
al actions to a leevel of insignifica
ance, replacement water is
remedia
required. Replacementt water quality m
must be equal to or better
e maximum bacckground level fo
or Cr6. This is co
onsistent
than the
with the
e requirements oof Water Code se
ection 13304(f), which
requires that the replaccement water “meet not only all a
applicable
hat it also is
federal, state and local drinking water sstandards,” but th
parable quality too that pumped b
by the … private well owner
of comp
prior to the discharge oof waste.”
uture (unknown) MCL for
The background value, rather than a fu
ement water beca
ause if the
Cr6 is the appropriate level for replace
future MCL
M
for Cr6 wass adopted at a le
evel higher than tthe
maximu
um background, then replaceme
ent water quality could be
provide
ed at a quality woorse than the wa
ater quality in an impacted
well. This
T
situation wouuld render the m
mitigation measurre
ineffecttive for its intendded purpose – to
o mitigation impacts from
the rem
mediation projectt to a level of insignificance, whe
ere feasible.
Providing replacement water at a qualitty worse than tha
at in the
ed well would noot meet this purp
pose.
impacte
ore, no revisionss to the Final EIR
R are proposed.
Therefo
C
Comments
Responses
e response to com
mment 1 regardiing why maximum
2. See
backgro
ound values are appropriate to d
define significantt impacts
that trig
gger mitigation raather than the un
nknown future M
MCL for Cr6.
es of EIR mitigattion are
"Actually affected wellss" for the purpose
maximum background
determined using exceeedances of the m
um values as onne threshold. Th
his criterion is based on the
chromiu
significa
ance criteria speecified in the Dra
aft and Final EIR
R.
se it is unknown at this time wha
at the future MCL
L for Cr6
Becaus
might be,
b using the futuure MCL to defin
ne affected wells could
result in
n one of two unaacceptable situattions:
e MCL is set low
wer than the maxiimum backgroun
nd level for
a. If the
Cr6, afffected wells cou ld include those containing naturallyoccurrin
ng Cr, requiring PG&E to mitigatte impacts for wh
hich it may
not be responsible for. This would be inconsistent with State of
nia policies and rregulations, and CEQA regulatio
ons.
Californ
e future MCL for Cr6 was adopte
ed at a level high
her than
b. If the
maximu
um background, then a well wou
uld not be consid
dered
affected
d until the Cr6 leevels rose to excceed that MCL. D
Depending
on the level of the futurre Cr6 MCL, this could allow sign
nificant
aquifer, inconsistent with
degradation to the wateer quality in the a
ate Board's Resoolution 68-16 (Sta
atement of Policcy with
the Sta
Respec
ct to Maintaining
g High Quality Waters).
ore, no revisionss to the Final EIR
R are proposed.
Therefo
&E has already bbeen collecting T
TDS and uranium
m data for
3. PG&
agriculttural fields currenntly in operation and could reaso
onably
submit its investigation plan within mon
nths of the appro
oval of a
alf a year to complete the
general WDR, having sstill more than ha
gation. Thus, thee request to have
e up to a year following
investig
workpla
an approval doess not appear neccessary. Howevver, in the
unlikely
y occurrence thaat Water Board s
staff's approval of an
investigation plan is delayed such that completing the
investigation within one year of WDR approval is not feasible,
PG&E may always request an extension to the due date for the
investigation completion.
Therefore, no revisions to the Final EIR are proposed.
C
Comments
Respo
onses
4. While the wording inn various section
ns of the EIR reg
garding the
n plume finger iss not exactly the same, Water Bo
oard staff
western
do not believe that this presents an inco
onsistency. On page 3.1ation of the plume
e finger
50, the paragraph statees that the migra
ars to be a result of two actions . . . ." This is not a
"appea
conclus
sive statement o
on the cause of p
plume migration, and the
two acttions discussed iin that paragraph
h are reasonable
e scenarios
based on
o pumping andd injection data.
ore, no revisionss to the Final EIR
R are proposed.
Therefo
propriate for resiidential and
5. The 100-point screeening table is app
ercial projects. T
The EIR project ((groundwater rem
mediation)
comme
does no
ot fit into the screeening table fram
mework and thuss it would
be inap
ppropriate to do a 100-point equivalent. The 100
0 points
corresp
ponds roughly too 31% on average. Thus, the pro
oject should
be requ
uired to reduce eemissions by 31%
%.
ore, no revisionss to the Final EIR
R are proposed.
Therefo
C
Comments
Respo
onses
6. PG&
&E is correct tha
at there is no form
mal approval pro
ocess
through
h the California D
Department of Fiish and Wildlife rregarding
mitigatiion for impacts too special status plants. Therefore, deleting
the requirement that CA
A DFW approve measures relate
ed to
special status plants is appropriate. Water Board staff will consult
ppropriate agenccies as needed, a
and retain the ab
bility to
with ap
enforce
e mitigation meassures related to special status plants.
nal EIR will be reevised as suggessted.
The Fin
Comments
Responses
7. The first part of this ccomment suggessts a revision to correct an
scribing where hhabitat for Mojavve fringe-toed liza
ards occurs
error des
in the prroject area.
al EIR will be revvised as suggestted.
The Fina
ment 7 suggestss clarifying that the 3:1 ratio
The second part of comm
pensatory mitigaation for the loss of Mojave fringe
e-toed lizard
for comp
applies to
t permanent losss of habitat, rath
her than tempora
ary
impacts.. This is correct.
al EIR will be revvised as suggestted.
The Fina
C
Comments
Responses
ERRATA SHEET
FINAL ENVIRONMENTAL IMPACT REPORT, COMPREHENSIVE GROUNDWATER
CLEANUP STRATEGY HISTORICAL CHROMIUM DISCHARGES FROM PG&E'S HINKLEY
COMPRESSOR STATION, SAN BERNARDINO COUNTY
The following revisions, shown in strikeout and underline format, are made to the Final
EIR.
Section, pages, line numbers
Revision
3.7, 3.7-42, lines 8 to 10
Desert dunes habitat is located in the south part of the project
area (below the Mojave River) and in the northwestern eastern
part of the project area (See Figure 3.7.1)
3.7, 3.7-55, lines 20 to 34

If any listed plant species are observed during focused
surveys of the work areas, the extent of the population will
be clearly demarcated in the field by protective fencing, lath
stakes, and/or flagging, as appropriate, for avoidance and
the regulatory agencies will be notified. If project related
impacts to a listed plant species will occur, initiation of
consultation with CDFG and or USFWS as appropriate will
be required. Avoidance of listed species is the first priority;
disturbance shall only be approved if the Water Board,
CDFG and/or USFWS all determines, after consultation
with CDFG and/or USFWS and approval of the appropriate
agency if a take permit is required, that complete
avoidance is infeasible.

3.7, 3.7-55, lines 40 to 42

If any plant species that are not listed under CESA or ESA
but are identified as special-status species (“non-listed
plant species”) are observed during focused surveys of the
work areas, the extent of the population will be clearly
demarcated in the field by protective fencing, lath stakes,
and/or flagging, as appropriate, for avoidance. Avoidance
will occur to the maximum extent feasible. If impacts are
proposed to non-listed CRPR rank 1A, 1B, or 2 plant
species, a brief analysis will be completed to determine the
appropriate mitigation. Additional measures as a result of
this analysis may be required, such as seeding,
transplanting, collection of seeds to be used for the future
conservation of the species, and/or compensatory
mitigation habitat. Avoidance of non-listed, but rare species
is the first priority; disturbance shall only be approved if the
Water Board and CDFG both determines, after consultation
with CDFG, that complete avoidance is infeasible.
Compensatory mitigation for the loss of Mojave fringe-toed
lizard habitat will be determined through consultation with
CDFG. The minimum compensation ratio for the permanent
loss of suitable Mojave fringe-toed lizard habitat will be 3:1.
EXHIBIT 2
11
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EXHIBIT 3
EXHIBIT 3