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Fact Sheet -March ZQ1 1
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A Draft Amended Remedial Action Play
for Chico Municipal Airport is Available
for Public Review
~..T~Ye Mission of
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The Department of vv ~ ~.iu~Ec~w~ atiree~:
e d ter Sikreat
Toxic Substances ''~~ ~, T`` .k~,r Fs~~q,'kr y~~i r` `C' " ~~i~h
Control (DTSC) ~.' -~ ' 7 ~ i
invites the public to ~ ~ ~' ~;~. ~ ~,
review and make - - _ ~ ' ' "
comments on the - ~F~ y.. ~'~ .
Draft Amended ; ~ _ _ _~ - .-~ ~:
Remedial Action Plan "_~""'
,, ~~ ~ ~ ~;
(RAP) for the former y _ .~
Victor industries -~_=
Corporation (VlC) ~~ ~ , -- ~ .
located at G51 _ _ -
and 6$ i 1/iberator
Street in Chico, ~ Chico Municipal AirporE
California (within -°
the Chico Municipal Airport, or CMA). The initial RAP issued in 2002 was to address
contamination in soil and groundwater, caused by the use of chemicals during business
operations at CMA. The primary chemicals of concern at the CMA (Site) includes
volatile organic compounds (VOCs) including Trichloroethylene (TCE). Since
approval of the initial RAP in 2002 and implementation of the remediation, DTSC has
identified appropriate changes ro the remedy, which are included in the Draft Amended
RAP. During a 30-day period, the public will have opportunity to review and submit
comments on the Draft Amended RAP.
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:City Councit Conference, Room 1
City Of Chico
42~ Main Street
Chico, California 98528
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'~~ ~~Site,H~sto`r~ and Background
Th'~ C11~fA is located in the northern part of the
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' •' City of Chico (City}, California. The Site was first
used as a municipal airport in 1935. From I942
to I945, the U.S. Army Air Corps used the facility
For training. Aircraft maintenance was conducted
as part of these activities. From 1947 to 1958,
Victor Industries leased several buildings along
Liberator Street, including buildings T 80, T-85,
and T-90, which are now known as 651 and 6S 1
Liberator Street. Victor Industries manufactured
aluminum tubes and cans, using solvents, such. as
TCE, for degreasing. From approximately 1958
to 1972 buildings G51 and 681 Liberator Street
remained vacate and from 1972 to 1984, Sierra
Pacific Industries conducted wood treating at G51
and 681 Liberator Street. Sierra Pacific reportedly
used pentachlorophenol, acetone, and 1,1,1-
trichloroethane (1,1,1-TCA).
In 1984, the presence of VOCs in groundwater was
first discovered when the three public supply wells
owned by California Water Service were sampled
in response to California Assembly Bill 1$03
{AB 1803). TCE and tetrachloroethylene (PCE)
were detected in one well at concentrations up to
543 micrograms per liter (mg/L) and 12 mg/L,
respectively. The affected well was- subsequently
shut down and abandoned. In 19$6, the California
Department of Health Services (DHS), now
DTSC, assumed the lead regulatory oversight role
for the Site. In 1985, a contractor for the state
agencies conducted soil, soil-gas, and groundwater
testing at CMA. The investigation identified the
presence of TCE, PCE, and other VOCs in the
vicinity of buildingT-90.
In 1991, a soil vapor extraction system was installed
in the source area and in 1994, an air sparging
system was installed to address groundwater
impacts in the source area. The soil vapor extraction
and air sparging systems were operated until I997,
until low in flowing concentrations resulted in
their shutdown. A total of 3,804 pounds of TCE
were reported to have been removed by the soil
vapor extraction and air sparging systems. In 1994,
the groundwater extraction and treatment system
(GWETS) for extraction well BCVE-1 (BCVE-
1 GWETS} was installed adjacent to the airport
runway, downgradient of the source area. The
BCVE-1 GWETS was operated until 1997. A
total of 56.4 million gallons of groundwater were
reported to have been treated and disposed to the
sanitary sewer by the BCVE-1 GWETS from 1994
to 1997.
Regulatory Summary
In 1989, DISC issued a Remedial Action Order
to the VIC for the Site. Approximately a year later
this order was replaced with an Imminent and
Substantial Endangerment Order. As discussed
earlier, from 1990 through 1994, a remedial
investigation and interim remedial actions were
conducted at CMA. In 1993, on behalf of DTSC,
the Stare of California Attorney General's office
filed an action in the U.S. District Court for the
Eastern District of California seeking recovery
of past response casts and adjudication of
responsibility For remediation of the Site.
A Feasibility Study (FS) For the Site was submitted
in 1994 and conditionally approved by DTSC.
The FS identified monitored natural attenuation
(MNA) as the preferred remedy for part of the
plume. In 1999, a Draft RAP was submitted to
DTSC and this document proposed the remedy of
groundwater extraction and treatment, air sparging
in the northwest part of the plume and MNA for
the southwest part of the plume.
In 2000, a Focused FS was submitted, which
evaluated additional alternatives for groundwater
conditions at CMA. The Focused FS formed the
basis for final RAP, submitted in 2002.
In September 2002, DTSC and the defendants
entered into a settlement agreement and Consent
Decree {CD). As part of the CD, the City assumed
the role of the party responsible for implementing
the RAP and complying with the conditions of the
CD. The contaminants of concern identified and
the cleanup levels for the Site are are shown in table
1 on page 4.
The CD required that the City conduct
groundwater extraction and treatment at an
existing facility located in the central part of the
groundwater plume (referred to as the BCVE-1
Groundwater Extraction and Treatment System,
or GWETS), and at another location on private
property located to the southwest of the CMA
property (referred to as the BCVE-2 GWETS).
Remedy Implementation
The BCVE-1 GWETS system was refurbished and
began operation in March 2003. Design and
permitting activities were also conducted for
theBCVE-2 GWETS. Tkze City of Chico, however,
was unable to construct the BCVE-2 GWETS as
a result of the presence of substantial vernal pools,
other wetlands, and
endangered species, such as the Butte County
Meadowfoam. As an' alternative to the BCVE-2
GWETS, the City of Chico began groundwater
extraction and treatment from an existing
monitoring well, BCV 27, located on the western
edge of the CMA property as an interim remedy.
The BCV-27 interim system has been operating
since July 2007 and has been successful in
containing the TCE plume and substantially
reducing TCE concentrations in the groundwater.
Draft Amended Remedial Action Plan
The revised remedy presented in the Draft
Amended RAP is a combination of groundwater
extraction and treatment (pump-and-treat} at
the BCVE-1 GWETS and the BCV-27 system,
monitored natural attenuation (MNA), and a
contingency plan.
Groundwater will continue to be extracted from
BCVE-1 and BCV 27, treated using activated
carbon, and discharged to the sanitary sewer using
existing pipelines.
Once the above conditions have been achieved
BCV#-1 and BCV 27 will be shut down and the
system evaluated for its effectiveness achieving the
Remedial Action Objectives {RAOs}. For the MNA
portion of the remedy action, TCE concentrations
will continue to be monitored in the same
wells currently monitored, following existing
monitoring protocols. The MNA data collected
from monitoring will confirm whether or not the
following conditions are being met:
1. TCE concentrations are remaining stable or
decreasing across the Site; and
2. The extent ofTCE-impacted groundwater is
not enlarging.
The paint of compliance far MNA will be wells
BCV-29 and BCV 30. TCE is currently not
present at the location of these two wells. As long
as TCE is not present at these two wells, or is not
indicating an increasing trend in concentrations
then MNA will be considered effective. ~ If,
however, monitoring data shows a presence of
TCE consistently. at the point of compliance, and
concentrations are increasing or may increase ro
levels in excess of those appropriate to achieve the
RAOs, as listed above, then the contingent remedy
.described below will be implemented.
The contingency plan consists of two parts:
1. Additional monitoring down gradient of
the point of compliance but upgradient of
potential receptors; and
2. Active groundwater extraction and treatment to
contain the TCE plume and achieve the RAOs
at the point of compliance.
If conditions indicate that the contingency
plan must be implemented, then an additional
first water-bearing zone monitoring well will be
installed near Sycamore Creek; down gradient of
the point of compliance. IfTCE concentrations
continue to increase in the point of compliance
wells, then groundwater extraction from existing
wells will be re-started.
California Enr-ironmental Quality Act
Draft En~ironmen#al Impact Report
If an activity is found to be subject to the
California Environmental Quality Act {CEQA)
based on the preIirninary review of activity
information, DTSC then reviews the
proposed project to determine if it may be
categorically or statutorily exempt from CEQA.
DTSC has evaluated possible impacts the proposed
removal activities may have on this site, as required
under CEQA and have determined that a Draft
Notice of Exemption (NOE} is appropriate. The
Draft NOE states that the cleanup activities
proposed will not have significant impacts on
the environment. The Draft NOE is available
for public review, along with other supporting
documents at designated repositories.
Information Repositories
The Draft Amended RAP, draft Environmental
Impact Report and other Site-related documents
may be viewed at the following locations:
Meriam~ Library
Special Collection Department
Chalifornia State University,
Chico, Califonia 95929
(530}s95-5710
Butte County Library
Chico Branch
1108 Sherman Avenue
Chico, California 95925
(530) 891-27G2
DTSC Sacramento Office: Pile Room
5500 Cal Center Drive
Sacramento, California 95526-3200
Call for an appointment (916) 255-3758
3
Contact fnformat~on
For more information abc
For the cleanup process
McKinley Lewis, fir.
DTSC Project Manager
{91b)255-3625
MLewis(~dtsc.ca.gov
rut CMA and related documents, please contact:
For public participation Fox media questions contact:
Veronica Lopez-Villasenor Charlotte Fadipe
DTSC Public Participation Specialist DTSC Public Information Officer
(91 G}255-3651 (916} 323-3395
VI..o ezvi~~dtsc.ca. ov CFadi e~ydts„„ __~
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' Table: Summary of bite Contambniation
CONTAMINANT HIGHEST LEVELS
DETECTED *CLEANUP GOAIL
(fig/L) MCL
(deg/L)
PCE (Tetrachloroethylene) < 58 ~cg/L < 5.0 5.0
TCE (Trichloroethylene) 2800 ~g/L < 5A 5.0
Carbon Tetrachloride < 50 ~.g/L < 0.5 0.5
1, 1,2-Trichloroethane (1,1,2-TCA) < 50 ~g/L < 5.a 5.0
aglL = R9icragrams par liter. ' SWRCB Lwel MCL = Maximum Contaminant Level for California
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Chico Municipal Airport Map