T793 Camp Parks CSTC Dublin Crossing FOST 16SEP13

User Manual: T793

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DRAFT_FINAL_FOST_Document (9-20-13)-no-markups
ECP Map dated 23 Nov. 2010
Pages from Camp Parks Signed ROD (28 OCT)

DRAFT FINAL

FINDING OF SUITABILITY TO TRANSFER

(FOST)

United States Army Combat Support Training Center, Camp Parks

Dublin Crossing Real Property Exchange Parcel

16 September 2013

FINDING OF SUITABILITY TO TRANSFER

(FOST)

United States Army Combat Support Training Center, Camp Parks

Dublin Crossing Real Property Exchange Parcel

16 September 2013

1.0 PURPOSE.

The purpose of this Finding Of Suitability To Transfer (FOST) is to document the environmental

suitability of certain parcels or property at the United States Army Combat Support Training

Center, Camp Parks (Parks) for transfer to the Dublin Crossing CP, Limited Liability

Corporation, consistent with Comprehensive Environmental Response, Compensation, and

Liability Act (CERCLA) Section 120(h) and Department of Defense (DOD) policy. In addition,

the FOST includes the CERCLA Notice, Covenant, and Access Provisions and other Deed

Provisions and the Environmental Protection Provisions (EPPs) necessary to protect human

health or the environment after such transfer.

2.0 PROPERTY DESCRIPTION.

The Property consists of approximately 171.6 acres, which includes 22 current buildings and no

acres of undeveloped land. The property was previously used as training facilities, vehicle repair

facilities, supply buildings and warehouses, medical training groups, medical facilities, fire and

police facilities, office and administrative buildings, recreational facilities, a parade ground, a

helicopter pad, infrastructure maintenance facilities, barracks, dining facilities, and a museum.

The property is intended to be transferred as a mixed-use master-planned community1 and is

consistent with the intended reuse of the property as set force in the Dublin Crossing Draft

Specific Plan (RBF, 2013) and Dublin Crossing Environmental Impact Report (RBF, 2013). A

site map of the property is attached (Enclosure 1). The proposed property to be transferred

excludes three interior parcels: The 8.5 acre National Aeronautics and Space Administration

(NASA) property and warehouse (Building 121), under control of the U. S. Air Force, the 3.98

acre Parks Reserve Forces Training Area (PRFTA) 2 site (also known as the Building 109

former incinerator site) and the 2.62 acre PRFTA-13 site (also known as the Former Fuel Storage

Area 761). The parcels have been surveyed and metes and bounds have been assigned. Transfer

of these inholdings will be covered by separate FOST documents.

1 The current proposed use is residential (14 % single family, 31 % townhomes), retail and multifamily (5%),

office/hotel (5%), civic (3%), open space (26%), school (4%), and infrastructure (11%)

3.0 ENVIRONMENTAL DOCUMENTATION.

A determination of the environmental condition of the property was made based upon the

Environmental Baseline Survey (USACHPPM, 2002e) and Environmental Condition of Property

(ECP) (USACHPPM 2011) and the ECP Recertification Memo (Parks CTSC, 2013). The

information provided is a result of a complete search of agency files during the development of

these environmental surveys.

A complete list of documents providing information on environmental conditions of the Property

is attached (Enclosure 2).

4.0 ENVIRONMENTAL CONDITION OF PROPERTY.

The DOD ECP categories for the Property are as follows:

ECP Category 1: F101-F105, F110-F112, F115, F140, F141, F152, F161, 162, 171, 180, 634,

F635, F725-F727, 730A, 730B, 730C, 713, F732, F735, F761, F785, F790, 791, T793, F793,

793, F794, F795, 796, F797, F798, F831, F832, F833, F850 – F857, F861-F865, 861, 862, F870-

F874, 880, 881, F880, F891-F897, F902-F905, F910, F911, F920-F923, Site 38, Site 39

ECP Category 2: F635, F732, and F761 (PRFTA 13); Trench 3, Site 36, and Site 39

ECP Category 3: F132, F151, F636, F781, F782, F783, F784, 791, 792, F888, Site 28, Site 37,

Site 40, Site 41

ECP Category 4: Buildings 130, 131, 150, 170, 730, 792, 860; Former RTS MED Motor

Pool; Former Building 926

A summary of the ECP Categories for specific buildings, parcels, or operable units and the ECP

category definitions is provided in Table 1 – Description of Property (Enclosure 3).

4.1 ENVIRONMENTAL REMEDIATION SITES.

There were eleven remediation sites located on the Property: A summary of the environmental

remediation sites on the property is as follows:

Building/Site1 Parcel

Number1

ECP

Area

Type

Environmental Concerns Current

Status

130 5 4 LBP

Sampling and remediation complete.

CDTSC has issued letter stating site is

suitable for unrestricted use.

131 6 4 Radionuclides, LBP

Release of radionuclides and lead.

Remediation complete for both.

Closure granted for radionuclides.

Building/Site1 Parcel

Number1

ECP

Area

Type

Environmental Concerns Current

Status

150 9 4 LBP

Release of lead to surface soil. CDTSC

has issued letter stating site is suitable

for unrestricted use.

170 12 4 LBP

Release of lead to surface soil;

remediation completed. CDTSC has

issued letter stating site is suitable

for

unrestricted use.

730 17 2

Petroleum-related

compounds, VOCs, SVOCs,

metals

Release of TPH-DRO to subsurface

soil, remediation complete, closure

granted.

792 26 4 LBP

Sampling complete, release of lead to

soil, remediation complete. CDTSC

has

issued letter stating site is suitable

for unrestricted use.

860 31 2

Petroleum-related

compounds from < 5-gallon

spill

Cleaned up at the time of the spill, non

reportable

Former RTS Med

Motor Pool

32 2

Petroleum-related

compounds

Sampled as part of

SEQA, see below

926 35 4 PCBs

Previous remediation for minor PCB

spill. Additional sampling complete, no

release and no further action required.

Site 36

Diesel & oil

20 cubic yards soil bioremediated onsite

Trench 3

Diesel & oil

20 cubic yards soil bioremediated onsite

1) As referenced in the June 2011 ECP Report.

All environmental soil and groundwater remediation activities on the property have been completed

or are in place and operating properly and successfully.

A summary of the environmental remediation sites is provided in Table 2 – Notification of

Hazardous Substance Storage, Release or Disposal (Enclosure 4).

[Author’s note: We will need closure, concurrence, or no further action memos from DTSC for

Trench 3, Site 36 (Category 2), Site 37 and Site 39 (Category 1)

[Author’s note: We may require a CERCLA Record of Decision for all ECP Category 3 and

Category 4 sites]

STORAGE, RELEASE, OR DISPOSAL OF HAZARDOUS SUBSTANCES.

Hazardous substances were stored for one year or more and released or disposed of on the

property in excess of reportable quantities specified in 40 CFR Part 373. All hazardous

substance storage operations have been terminated on the property. Hazardous substances were

released in excess of the 40 CFR 373 reportable quantities at the following sites2

F132, F636, 730, F781-F784, 860, Southeast Quadrant Area, Former Hazardous Waste

Accumulation Area, 791/792 Fuel Storage Area

The release or disposal of these hazardous substances was remediated at the time of the release

or as part of the Installation Restoration Program (IRP). See Section 4.1 for additional

information. A summary of the buildings or areas in which hazardous substance activities

occurred is provided in Table 2 – Notification of Hazardous Substance Storage, Release, or

Disposal (Enclosure 4). The CERCLA 120(h)(3) Notice, Covenant, and Access Provisions

(Enclosure 6) will be included in the Deed.

4.2 PETROLEUM AND PETROLEUM PRODUCTS.

4.2.1 Underground and Above Ground Storage Tanks (USTs/ASTs).

Current UST/AST Sites.

There are no underground and two above-ground petroleum storage tanks on the Property. There

is no evidence of petroleum releases from these sites.

Former UST/AST Sites.

There were eleven underground and four above-ground petroleum storage tanks on the property

that have been removed or closed in place. Petroleum product releases occurred at the following

sites:

Two of the ASTs were former USTs that were removed and subsequently used as ASTs at

PRFTA 13 (Former Fuel Storage Area/Area 761). Petroleum hydrocarbon releases occurred at

the following sites:

Former Building 732, and Former Building 888.

Former Building 732.

Former Building 732 was a fuel point constructed in 1942 and demolished in 1992. Two

underground storage tanks (USTs) were removed from the site in 1993. Petroleum hydrocarbons

and VOCs were detected in soil and groundwater at concentrations less than the ESL applicable

at the time of sampling (USACHPPM, 2002e). Site closure was granted by the Alameda County

Department of Public Health on 28 March 2001.

2 note that release of lead to soil from lead-based paint (LBP) on exterior building surfaces is not listed in this

section; see section 4.6

Former Building 888.

Building 888 was a gas station constructed in 1952, demolished in 1998, and located on 4th

Street between Monroe Avenue and Arnold Road. Two hydraulic lifts, one 10,000-gallon UST

formerly containing gasoline, one 10,000-gallon UST formerly containing diesel fuel, one 500-

gallon UST formerly containing waste oil, two pump dispensers and associated piping, and one

oil/water separator were located at the former gas station. The tanks were installed in the 1950s

(Tung, 2001; Woodward-Clyde Federal Services, 1994d). Woodward-Clyde Federal Services

removed three USTs in July 1996. In 1998, Cal, Inc. conducted limited over-excavation and

confirmatory soil and groundwater sampling near the former fuel dispenser island (Cal Inc.,

1998a). Petroleum hydrocarbons were detected in soils at concentrations greater than the ESL

applicable at the time of sampling. Approximately 20 cubic yards of soil were removed and

three soil samples were collected from the excavation. Metals, bis(2-ethylhexyl)phthalate (an

SVOC), and VOCs were detected in groundwater at concentrations less than, or greater than but

the same order of magnitude as, the ESLs applicable at the time of sampling (USACHPPM,

2009b). However, the CRWQCB determined the exceedences did not pose a threat to human

health or the environment and issued a No Further Action Letter on 17 April 2009 (D’Onofrio,

2009).

The release of these petroleum products was remediated at the time of the release or as part of

UST/AST closure. See (BSK and Associates, 1997) for additional information.

A summary of the UST/AST petroleum product activities is provided in Table 3- Notification of

Petroleum Products Storage, Release, or Disposal (Enclosure 5).

4.2.2 Non-UST/AST Storage, Release, or Disposal of Petroleum Products.

There was non-UST/AST storage of petroleum products in excess of 55 gallons for one year or more

on the property. The petroleum was used for the following types of activities: motor pool

operations, industrial operations, fire station.

All non-UST/AST petroleum product storage operations have been terminated on the property. There

was no evidence of petroleum releases in excess of 55 gallons as a result of these activities.

A summary of the non-UST/AST petroleum activities is provided in Table 3 – Notification of

Petroleum Products Storage, Release, or Disposal (Enclosure 5).

4.3 POLYCHLORINATED BIPHENYLS (PCBs).

There is evidence of releases from the PCB-containing equipment at the following site: Former

Building 926 PG&E Substation. The PCBs were remediated at the time of the release or as part

of the installation restoration program. See (BSK and Associates, 1997) and (USACHPPM,

2004) for additional information. PG&E pole-mounted transformer at 4th & Davis: The PCBs

were remediated by PG&E (TES, 2001).

4.4 ASBESTOS.

There is asbestos-containing material (ACM) in the following buildings:

Building

Survey and Date

ACM Materials Identified

(>1.0 % asbestos)

Materials

Friability

Quantity

141

1988 Occusafe Survey

Cement panels

(interior and exterior)

Non-friable

423 square

feet

Cement flue pipe

Non-friable

15± square

feet

9” x 9” floor tiles

Non-friable

8,750 square

feet

2002 HLA2 Survey

12” x 12” floor tiles

(below newer floor tiles and carpeting)

Non-friable

8,622 square

feet

Concealed exterior cement panels

Non-friable

5,287 square

feet

162

1988 Occusafe Survey

Cement panels

(exterior)

Non-friable

3,000± square

feet

2002 HLA Survey

Sealant on asphalt sheet siding

(hidden behind cement panel siding))

Non-friable

1,500 linear

feet

TSI3 on pipes of chilled water system

Friable

encapsulated

25± linear

feet

TSI on pipes of high-pressure steam lines

Friable

encapsulated

30± linear

feet

TSI on pipe fitting (joints and valves) of chilled

water system

Friable

encapsulated

9/2005 fittings

Cement boiler flue

Non-friable

15/35 ± linear

feet

2002 HLA Survey

Asbestos cement sheet siding

Non-friable

200± square

feet

Tar finish over cork insulation

Non-friable

49,900±

square feet

Wallboard compound

Non-friable

2,430± square

feet

180 1988 Occusafe Survey Brown flooring

Non-friable

7,200± square

feet

Beige floor tile mastic6

Non-friable

400 ± square

feet

2002 HLA Survey

No additional material identified

None

1) Samples of roofing material were not collected in either survey. Roofing materials should be assumed to contain

ACM unless demonstrated otherwise.

2) HLA = Harding Lawson, Associates.

3) TSI = thermal system insulation.

5) Quantities indicate those estimated by Occusafe above slash and those estimated by HLA below slash.

6) Material not located in later survey by HLA.

The ACM includes: floor tiles, cement panels, pipe insulation, asphalt sheet siding. See (HLA,

1997a, 1997b) and (Harding ESE, 2001a, 2001b, 2002) for additional information. The ACM

does not currently pose a threat to human health or the environment because all friable asbestos

that posed an unacceptable risk to human health has been removed or encapsulated. The deed

will include an asbestos warning and covenant (Enclosure 6).

4.5 LEAD-BASED PAINT (LBP).

The following buildings are known or presumed to contain lead-based paint (LBP):

Building

Phase II

Lead > ESL

1 Phase III

Lead > ESL

Parks DPW XRF

Sampling and Soil

Removal

Current Status

130

Warehouse Yes Yes Yes

Building still present. DTSC

issued concurrence letter

1 October 2008.

131

Warehouse

Yes Not sampled2 Yes Building still present.

F132

Warehouse

Yes Not sampled3 No

Risk Assessment completed. Property

closure granted.

141

Classrooms

No Not sampled No

Building still present. No further

action required.

150

Warehouse Yes Not sampled2 Yes

Building still present. DTSC

issued concurrence letter

1 October 2008.

162

Warehouse

No Not sampled No

Building still present. No further

action required.

170

Warehouse Yes Yes Yes

Building still present. DTSC

issued concurrence letter

1 October 2008.

171

Warehouse

No Not sampled No

Building still present. No further

action required.

180

Admin &

signal

equipment

Yes No No Building still present.

790

Administrative

Yes No No Building still present.

791

DPW

Maintenance

& Repair

No Not sampled No Building still present. No further

action required.

792

Warehouse Yes Yes Yes

Building still present. DTSC

issued concurrence letter

1 October 2008.

F796

Not sampled

Building demolished, 2004.

1) Yes means at least one sample from USACHPPM Phase II or Phase III studies contained lead at a concentration

greater than the environmental screening level (ESL) applicable at the time of sampling (200 mg/kg, current ESL is

150 mg/kg).

2) USACHPPM recommended additional sampling under different mechanism than the Phase III EBS.

3) Lead in soil assessed in conjunction with other sampling at the site. Analytical data indicate no release of lead to

soil.

See (USACHPPM 2002e, 2003, 2005) for additional information.

The property was not used for residential purposes and the transferee intends to convert the

property to residential use in the future. The deed will include a lead-based paint warning and

covenant (Enclosure 6).

4.6 INDOOR FIRING RANGES.

There are no indoor firing ranges on the property.

4.7 RADIOLOGICAL MATERIALS.

The following building was used for radiological activities: Building 130 and Building 131.

There was a release of radiological material at Building 131. The following actions were taken

to remediate the radiological material: Soil removal. All radiological materials have been

removed from the property.

On 29 April 2002 through 3 May 2002 the Army conducted a radiological site assessment of the

Property in compliance with the accepted protocol. The Radiological Site Assessment Report

[26 August 2002] found no evidence to suggest that any radiological commodities were

improperly managed at the site or that any residual radiological material is present at the site and

concluded that no further action is required with respect to the radioactive devices or materials

identified. On 30 August 2002 the U.S. Army Center for Health Promotion and Preventive

Medicine concluded the site is free of radiological concerns. See (USACHPPM, 2002b) for

additional information.

4.8 RADON.

Radon surveys were conducted in 19 buildings on the property. Radon was not detected at above the

EPA residential action level of 4 picocuries per liter (pCi/L) in these buildings.

4.9 MUNITIONS AND EXPLOSIVES OF CONCERN (MEC).

Based on a review of existing records and available information, there is no evidence that

Munitions and Explosives of Concern (MEC) are present on the property. In addition, available

documentation indicates no areas within the proposed transfer area were ever used as ranges,

training areas, or for other purposes that might indicate MEC is present. The term “MEC” means

military munitions that may pose unique explosives safety risks, including: (A) unexploded

ordnance (UXO), as defined in 10 U.S.C. § 101(e)(5); (B) discarded military munitions (DMM),

as defined in 10 U.S.C. § 2710(e)(2); or (C) munitions constituents (e.g. TNT, RDX) as defined

in 10 U.S.C. § 2710(e)(3), present in high enough concentrations to pose an explosive hazard.

4.10 OTHER PROPERTY CONDITIONS.

There are no other known property conditions that pose an unacceptable risk to human health

and the environment.

5.0 ADJACENT PROPERTY CONDITIONS.

The following potentially hazardous conditions exist on adjacent property: PRFTA-02 (The

Former Building 109 Site). This Site is currently undergoing remediation involving removal of

soil and future groundwater monitoring for metals and dioxins. The presence of these hazards on

the cited adjacent property does not present an unacceptable risk to human health and the

environment because the site is currently undergoing remediation, or remediation has been

completed, and remedial efforts should eliminate all potential risk for that site and adjacent sites.

6.0 ENVIRONMENTAL REMEDIATION AGREEMENTS.

There are no environmental remediation orders or agreements applicable to the property being

transferred. The deed will include a provision reserving the Army’s right to conduct remediation

activities, if necessary, in the future (Enclosure 6).

7.0 REGULATORY AND PUBLIC COORDINATION.

The Environmental Protection Agency (EPA) Region 9, the CDTSC, the CRWQCB, and the

public were notified of the initiation of this FOST.

[Reviewers Note: Action item to be done when report is final].

Regulatory/public comments received during the public comment period will be reviewed and

incorporated, as appropriate. A copy of the regulatory/public comments and the Army Responses

will be included at Enclosure 8 and Enclosure 9.

8.0 NATIONAL ENVIRONMENTAL POLICY ACT (NEPA) COMPLIANCE.

The environmental impacts associated with the proposed property transfer have been analyzed in

accordance with National Environmental Policy Act (NEPA). The results of this analysis are

documented in the Final Environmental Impact Statement and ROD (signed on 28 October 2009)

(Department of the Army, 2009). The NEPA analysis identified several encumbrances. These

encumbrances and the corresponding mitigation and monitoring procedures, are presented in

Enclosure 10

9.0 FINDING OF SUITABILITY TO TRANSFER.

Based on the above information, I conclude that all removal or remedial actions necessary to

protect human health and the environment have been taken and the property is transferable under

CERCLA section 120(h)(3). In addition, all Department of Defense requirements to reach a

finding of suitability to transfer have been met, subject to the terms and conditions set forth in

the attached Environmental Protection Provisions that shall be included in the deed for the

property (Enclosure 11). The deed will also include the CERCLA 120(h)(3) Notice, Covenant,

and Access Provisions and Other Deed Provisions. Finally, the hazardous substance notification

(Table 2) shall be included in the deed as required under the CERCLA Section 120(h) and DOD

FOST Guidance

[Author’s Note: Signature Authority Not Decided]

CHRISTOPHER P. GERDES

DATE

LTC, MP, U.S. Army

Commanding

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10 Enclosures

Encl 1: Site Map of Property

Encl 2: Environmental Documentation and References

Encl 3: Table 1- Description of Property

Encl 4: Table 2. Notification of Hazardous Substance Storage, Release, or Disposal

Encl 5: Table 3. Notification of Petroleum Product Storage, Release, or Disposal

Encl 6: CERCLA Notice, Covenant, and Access Provisions and Other Deed Provisions

Encl 7: Environmental Protection Provisions

Encl 8: Regulatory Agency/Public Comments (Final FOST)

Encl 9: Army Response to Comments (Final FOST)

Encl 10: ROD Encumbrances

ENCLOSURE 1

SITE MAP OF PROPERTY

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ENCLOSURE 2

ENVIRONMENTAL DOCUMENTATION AND REFERENCES

E-5

ENCLOSURE 2

ENVIRONMENTAL DOCUMENTATION AND REFERENCES

Anonymous, 1945. Map of U.S. Construction Battalion Replacement Depot, Camp Parks,

California, Showing Conditions on 30 June 1945.

Anonymous, 1989. Annual Installation Utilization Survey Parks Reserve Forces Training Area,

March 1989.

Anonymous, 1993. Lead-Based Paint and Asbestos Survey for Building Demolition - Phase II,

Parks Reserve Forces Training Area, California, April 1993.

Archaeological Resource Service, 1981. Cultural Resources Literature Search and Field

Reconnaissance of Camp Parks, Alameda and Contra Costa Counties, California, Report

prepared for Earth Metrics, Incorporated, Report Number ARS 81-82.

ASTM International, 2002. Standard Practice D 5746-98 (2002), Standard Classification of

Environmental Condition of Property Area Types for Defense Base Closure and Realignment

Facilities.

ASTM International, 2005a. Standard Practice D 6008-96 (2005), Standard Practice for

Conducting Environmental Baseline Surveys.

ASTM International, 2005b. Standard Practice E 1527-05, Standard Practice for Environmental

Site Assessments: Phase I Environmental Site Assessment Process.

Babcock, T., 2003. Letter Report From: Mr. Timothy Babcock, Hazardous Substances Removal

Incorporated, To: Mr. Timothy Schafstall, USACHPPM, Subject: Parks RFTA -

Documentation of Potholing Exploration Contract DABJ05-03-1419, 14 November 2003.

BSK and Associates, 1995, Phase I Environmental Site Assessment, Department of Military,

Camp Parks, Dublin, California

BSK and Associates, 1997. Supplemental Environmental Baseline Study, (Phase I Site

Assessment), Department of the Military, Camp Parks, 18 June 1997.

Cal Inc., 1998a. Final Closure Report Volume 1, Building 200 and Building 888, Contract No.

DACA05-97-D-0014, Task Order 007, Prepared on behalf of: U.S. Army Engineer District,

Sacramento, Corps of Engineers, December 1998.

Cal Inc, 1998b. Statement of Work, Closure of Oil Water Separator and Removal of Fuel

Dispensing Islands, Camp Parks RFTA - Building 888, Contract Number DACA05-97-D0014,

Task Order No. 0007, CAL Inc, 26 February 1998.

E-6

Cal Inc, 1998c. Statement of Work, Closure of Oil Water Separator and Removal of Fuel

Dispensing Islands, Camp Parks RFTA - Building 888, Contract Number DACA05-97-D0014,

Task Order No. 0007, 20 March 1998.

California Regional Water Quality Control Board, 2008b. Groundwater Monitoring at PRFTA

13, U. S. Army Combat Support Training Center, Camp Parks, Dublin, Alameda County,

California. .

California Regional Water Quality Control Board, 2009. Approval of Sampling and Analysis

Plan Addendum, Confirmation Soil Borings - PRFTA 13, U. S. Army Combat Support Training

Center, Camp Parks, Dublin, Alameda County, California. Letter dated 17 February 2009

California Zone 7 Water Agency, undated. Groundwater Contour Map, Internet Website

http://www.zone7water.com/Layout-2.pdf

Camp Parks, Undated a. Historical real property records.

Camp Parks, Undated b. Statement of Work, Underground Storage Tank Investigation, Closure

of Oil Water Separator and Removal of Fuel Dispensing Islands, Camp Parks RFTA - Buildings

200 and 888.

Camp Parks, 2013, Recertification of Final Environmental Condition of Property Report No. 38-

Eh-3589-10 Dublin Crossing (Formerly the 180-Acre) Real Property Exchange Area U.S. Army

Combat Support Training Center And Camp Parks

CH2MHill, 2005. Camp Parks Training Site Summary Report - Soil and Groundwater

Investigation of the Oakland Real Property Exchange (RPX) 32-Acre Parcel, Dublin, California.

Report prepared for Engineering and Environment, Inc., July 2005.

Department of the Army, 2009. Record of Decision for the real Property Master Plan and Real

Property Exchange at United States Army Garrison, Camp Parks, California. Department of the

Army, Installation Management Command.

Deputy of the Under Secretary of Defense and Environmental Protection Agency, 1999. Lead-

Based Paint Guidelines for Disposal of Department of Defense Residential Real Property - A

Field Guide, Interim Final, December 1999.

http://www.denix.osd.mil/shf/upload/dod_leadpaintpolmemo_0.pdf

D’Onofrio, F, 2007, Letter from Francesca D’Onofrio, Hazardous Substances Scientist,

California Department of Toxic Substances Control, to Mr. Paul Kot, Combat Support Training

Center Camp Parks. Final Summary Report, Removal of Oil Drainage Pit, Dublin Crossing,

Building 730, Camp Parks Training Site, Dublin, California May 22 2007

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D’Onofrio, F, 2008a, Final Summary Report, Lead-Contaminated Soil Removal, Buildings 150,

130, 170 and 792, Camp Parks, Combat Support Training Center, Dublin, California October 1

2008

D ‘Onofrio, F, 2008b. Letter from Francesca D’Onofrio, Hazardous Substances Scientist,

California Department of Toxic Substances Control, to Mr. Paul Kot, Engineering and

Environment, Incorporated. Final Summary Report, Lead-Contaminated Soil Removal,

Buildings 150, 130, 170, and 792, Camp Parks, Combat Support Training Center, Dublin,

California October 1 2008

D’Onofrio,F, 2009a, Final Groundwater Sampling Report No. 38-EH-07A8b-07, Southeast

Quadrant Area, U.S. Army Combat Support Training Center, Camp Parks, Dublin, California,

May 28 2009

D ‘Onofrio, F, 2009b. Letter from Francesca D’Onofrio, Hazardous Substances Scientist,

California Department of Toxic Substances Control, to LTC John Cushman, Commander, U.S.

Army Combat Support Training Center, Camp Parks. Final Ground-Water Sampling Report No

38-EH-07A8a-07, Former Building 888, ULS (sic) Army Combat Support Training Center,

Camp Parks, Dublin California, April 17 2009

Eckardt, J, A., 1945. Map of U.S. Construction Battalion Replacement Depot, Camp Parks,

California.

Environmental Data Resources, Inc, 2010. The EDR Radius Map with GeoCheck, Camp Parks

Dublin Blvd., Dublin, CA 94566. EDR Inquiry Number 2686499.2s.

Environmental Chemical Corporation, 2006. Removal of Oil Drainage Pit, Dublin Crossing,

Building 730 – Camp Parks Training Site, Dublin, California. Report prepared for the United

States of Engineers, Sacramento District - Valley Resident Office, October 2006.

Environmental Science Associates, 1986. Structures Evaluation for National Register of Historic

Places for the Parks Reserve Forces Training Area, Contra Costa and Alameda Counties,

California, Report prepared for the United States of Engineers, Sacramento District.

Environmental Science Associates, 1990. 47-Acre Surplus Parcel at Parks Reserve Forces

Training Area, Dublin, California, Environmental Baseline Survey, September 1990.

Environmental Quality Management, Incorporated, 2008. Camp Parks Combat Support Training

Center (CTSC) Dublin, California Final Summary Report, Lead-Contaminated Soil Removal,

Buildings 150, 130, 170, and 792. Report prepared for the U. S. Army Engineering District,

Louisville, Contract Number W912QR-04-D-0036, Task Order 0010.

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Environmental Protection Agency, 2010. Region 9 Regional Screening Levels (Formerly PRGs)

Master Table, December 2009. Internet site:

http://www.epa.gov/region09/superfund/prg/index.html

Escarda, Terry, 2013, Letter from Terry Escarda, Hazardous Substances Scientist, California

Department of Toxic Substances Control, to LTC Christopher P Gerdes , Commander, U.S.

Army Combat Support Training Center, Camp Parks, Trench 3 and Site 36, Army Combat

Support Training Center, Camp Parks, Dublin California {to be written prior to final FOST]

Escarda, Terry, 2013, Letter from Terry Escarda, Hazardous Substances Scientist, California

Department of Toxic Substances Control, to LTC Christopher P Gerdes , Commander, U.S.

Army Combat Support Training Center, Camp Parks, Site 37 and Site 39, Army Combat Support

Training Center, Camp Parks, Dublin California [to be written prior to final FOST]

General Services Administration, undated. Public Buildings Service Pamphlet: Office of

Property Disposal, Title X: The Residential Lead-Based Paint Hazard Act New Regulations.

Governor’s Office of Planning and Research, 1997. California Base Closure News, Newsletter

No. 18, August 1997.

Harding ESE, 2001a. Asbestos Survey, Camp Parks U.S. Army Reserve Center (USARC),

Building 141,USAR Center, Dublin, California.

Harding ESE, 2001b. Asbestos Survey, Camp Parks U.S. Army Reserve Center (USARC),

Building 162, General Purpose Warehouse, Dublin, California.

Harding ESE, 2002. Asbestos Survey, Camp Parks U.S. Army Reserve Center (USARC),

Building 170, USARC - Cold Storage Warehouse, Dublin, California.

Harding Lawson Associates, 1997a. Asbestos Survey, Camp Parks U.S. Army Reserve Center

(USARC), Building 1141, 91 Division LDRACAD, Dublin, California.

Harding Lawson Associates, 1997b. Asbestos Survey, Camp Parks U.S. Army Reserve Center

(USARC), Building 162, General Purpose Warehouse, Dublin, California.

Hart, 2011, No Further Action Concurrence, Former Building 636, U.S. Army Combat Support

Training Center, Camp Parks, Dublin, Alameda County, July 14 2011

Hart, 2012, Final Environmental Condition of Property (ECP) Report, Dublin Crossing, Camp

Parks, Dublin, Alameda/Contra Costa Counties

HDR, 2012, Final Integrated Natural Resources Management Plan, Parks Reserve Forces

Training Area, Dublin, California, Report Submitted to the United States Army Corps of

Engineers Contract #W912DQ-06-D-0026, March 2012.

E-9

Jones and Stokes Associates, Inc. 1995. Inventory of Special-Status Plant and Wildlife Species

at Parks Reserve Forces Training Area, Report prepared for the United States of Engineers,

Sacramento District, Report Number JSA 93-240, 1995

Jones and Stokes, Associates, Inc., 1998a. Cultural Resources Inspection at the Proposed

Location of a New Front Gate at Parks Reserve Forces Training Area, Report prepared for the

United States of Engineers, Sacramento District.

Jones and Stokes, Associates, Inc., 1998b. Field Investigation of Previously Recorded Cultural

Resource Sites in Parks Reserve Forces Training Area, Letter report prepared for the United

States of Engineers, Sacramento District.

Jones and Stokes, Associates, Incorporated, 1998c. Draft Parks Reserve Forces Training Area

Built Environment Inventory and Evaluation, Report prepared for the United States Army Corps

of Engineers, Sacramento District.

Jones and Stokes, Associates, undated. Geologic Map of Parks Reserve Forces Training Area.

Map prepared for the United States Army Corps of Engineers, Sacramento District.

JRP Historical Consulting Services, 2002. Inventory and Evaluation of Previously Unevaluated

WWII and Cold War Era Buildings, Parks Reserve Forces Training Area. Report prepared for

the United States Army Corps of Engineers, Sacramento district.

Leyva, G, 2009. Letter from George Leyva, Project Manager, California Regional Water Quality

Control Board to Douglas Guenther, Compliance Manager, HQ, US Army Combat Support

Training Center, Fort Hunter Liggett, California. RE: Groundwater Monitoring at Building 791,

Former Fuel Storage Area, U. S. Army Combat Support Training Center, Camp Parks, Dublin,

California, 12 March 2009.

RWQCB, 2010, Letter from George Leyva, Project Manager, California Regional Water Quality

Control Board to LTC Michael P Friend ,No Further Action, Building 791, Former Fuel Storage

Area, U.S. Army Combat Support Training Center, Camp Parks, Dublin, Alameda County

Mike Bobbitt and Associates, 2005. Comprehensive Magnetometer Survey for Underground

Storage Tanks at West Coast Garrison (Provisional), Camp Parks Training Site, Dublin,

California. Report prepared for the USACHPPM.

Mike Bobbitt and Associates, 2006. Comprehensive Magnetometer Survey for Underground

Storage Tanks at US Army, Combat Support Training Center and Camp Parks, Dublin,

California. Report prepared for the US Army, Combat Support Training Center.

E-10

Nelson, M. C., 1993. Memorandum From: Mark C. Nelson, LTC, EN Commanding, Parks

RFTA, For: Director of Engineering and Housing, ATTN: AFZH-DE (L.W. Burnett), HQ, I

Corps and Fort Lewis, Subject: Abandoned POL Farm at PRFTA, Date: 5 April 1993.

Office of the Under Secretary of Defense, 2000. Memorandum From: Office of the Under

Secretary of Defense, For: Assistant Secretary of the Army, Assistant Secretary of the Navy,

Assistant Secretary of the Air Force, Director, Defense Logistics Agency, Subject: Lead-Based

Paint Policy for Disposal of Residential Real Property, 07 Jan 2000.

http://www.denix.osd.mil/shf/upload/dod_leadpaintpolmemo_0.pdf

Rainie Rodgers Associates, 1986. A Cultural Resources Investigation of the Proposed Veterans

Administration, Northern California National Cemetery Sites at Santa Nella and Camp Parks,

Report prepared for Resource Assessment, Incorporated.

RBF Consulting, 2013, Dublin Crossing Draft Specific Plan, June 2013

http://www.dublincrossingca.com/specific-plan.pdf

RBF Consulting, 2013, Dublin Crossing Draft Environmental Impact Report, June 2013

http://www.dublincrossingca.com/EIR.pdf

Rothwell Consulting, Inc., 2002a. Letter Report From: Eric Rothwell, To: Mr. Manual Cunha,

Subject: Soil Sampling and Analysis in Sewer Trenches and Stockpile, 8 January 2002.

Rothwell Consulting, Inc., 2002b. Letter Report From: Eric Rothwell, To: Mr. Manual Cunha,

Subject: Soil Sampling and Analysis in Sewer Trenches, 23 October 2002.

Rothwell Consulting, Inc., 2002c. Letter Report From: Eric Rothwell, To: Mr. Manual Cunha,

Subject: Soil Sampling and Analysis in Sewer Trenches and Stockpile, 8 January 2002.

Roy F. Weston, 2000, Site Specific Health & Safety Plan Including Work Plan, Polychlorinated

Biphenyl (PCB) Abatement, Parks Reserve Forces Training Area, Dublin, California

Roy F. Weston, 2001a. Magnetometer Survey of the Tassajara Disposal Trenches and Bldg 109

Incinerator Areas, Parks Reserve Forces Training Area, June 2001.

Roy F. Weston, 2001b. Field Summary Report, Polychlorinated Biphenyl (PCB) Analytical

Sample Review and Site Abatement at Buildings 331, 334, 730, and 792, 2 March 2001.

Roy F. Weston, 2002. Comprehensive Magnetometer Survey for the Presence of Underground

Storage Tanks at Parks Reserve Forces Training Area, Dublin, California, 11 April 2002.

Sarmiento, R. A., 2006. Letter from Riz A. Sarmiento, Staff Toxicologist, California

Department of Toxic Substances Control, to Francesca D’Onofrio, California Department of

E-11

Toxic Substances Control, RE: Health Risk Assessment No. 39-DA-04GJb-06, Former Building

132 Site and Health Risk Assessment No. 39-DA-04GJa-06, Former Hazardous Waste

Accumulation Site, Camp Parks, Dublin, California, 16 August 2006.

SCS Engineers, 2005. Temporary Well Installation and Groundwater Sampling Report, Camp

Parks Training Site, West Coast Garrison, Dublin, CA. Report prepared for FedSource, Brea,

California. Task Order Number LOS12970, Contract Number BPA-6551.

Sonoma State University, 2001. A Cultural Resources Overview of the United States Army

Parks Reserve Forces Training Area, Near Dublin, Alameda and Contra Costa Counties,

California, Report prepared for David Small, Director of Public Works, Parks Reserve Forces

Training Area, 7 September 2001.

Strope, W. E. 1961. U.S. Naval Radiological Defense Laboratory, USNRDL Shelter Research

Program, Reviews and Lectures, No. 119, 21 August 1961.

Technial and Ecological Services, 2001, Remediation Activities for Polychlorinated Biphenyls at

Camp Parks Reserve Forces Training Area, 4th & Davis Street, Dublin, California, Report

#402.331-01.89

Tung, 2001. Correspondence From: Mee Ling Tung, Alameda County Health Care Services

Agency, Environmental Health Services, Environmental Protection; To: Mr. Marshall Marik,

Parks RFTA; Subject: Remedial Action Completion Certification (Enclosure: Case Closure

Summary), 28 March 2001.

United States Army Center for Health Promotion and Preventive Medicine (USACHPPM), 1998.

Relative Risk Site Evaluation 38-EH-8204-98, Parks Reserve Forces Training Area, August

1998.

USACHPPM, 1999. Final Sampling Plan, Site Inspection No. 38-EH-8703-99, Parks Reserve

Forces Training Area, Dublin, California.

USACHPPM, 2002a. Phase II Site Inspection No. 38-EH-5027-02, Parks Reserve Forces

Training Area, Dublin, California.

USACHPPM, 2002b. Radiological Historical Site Assessment No. 26-MF-3589-H-02,

U. S. Army Parks Reserve Forces Training Area, Dublin, California.

USACHPPM, 2002c. Quarterly Ground-Water Monitoring Report - First Quarter, Data for

Samples Collected During November 2001, Parks Reserve Forces Training Area, 18 January

2002.

E-12

USACHPPM, 2002d. Parks Reserve Forces Training Area, Quarterly Ground-Water Monitoring

Report for Second Quarter and Aquifer Hydraulic Conductivity Test Results, Data for Samples

Collected During February 2002, 19 April 2002.

USACHPPM, 2002e. Draft Environmental Baseline Survey No. 38-EH-3589-02, 187-Acre Real

Property Exchange, Parks Reserve Forces Training Area, Dublin (Alameda and Contra Costa

Counties), California, 22 April to 3 May 2002.

USACHPPM, 2002f. Site Inspection No. 38-EH-2938-02, Former Tank Farm (PRFTA13),

Parks Reserve Forces Training Area, Dublin California, 15-21 May 2002.

USACHPPM, 2002g. Phase II Site Inspection No. 38-EH-6665-02, Former Tank Farm

(PRFTA13), Parks Reserve Forces Training Area, Dublin, California, 11-15 October 2002.

USACHPPM, 2003. Results of Environmental Sampling in the 187-Acre Real Property

Exchange, Camp Parks, Dublin (Alameda and Contra Costa Counties), California, USACHPPM

Project No. 38-EH-003K-04, October 2003.

USACHPPM, 2004. Results of Environmental Sampling in the 187-Acre Real Property

Exchange, Camp Parks, Dublin (Alameda and Contra Costa Counties), California, USACHPPM

Project No. 38-EH-003K-04, October 2003.

USACHPPM, 2005. Sampling Results, Phase III Environmental Baseline Survey No. 38-EH-

003K-05, 187-Acre Real Property Exchange, Camp Parks, California, November 2004.

USACHPPM, 2006a. Final Environmental Baseline Survey No. 38-EH-04HW-05, Building 121

(NASA Site), U.S. Army Combat Support Training Center – Camp Parks, Dublin (Alameda and

Contra Costa Counties), California.

USACHPPM, 2006b. Health Risk Assessment Study No. 39-DA-04GJ-06a, Building 132 Site,

Camp Parks, California, May 2006.

USACHPPM, 2006c. Ground-Water Sampling Results, Northern Cantonment Area (Former

Building 636), U. S. Army Combat Support Training Center, Camp Parks, 1 to 19 December

2005.

USACHPPM, 2006d. Soil Sampling Results No. 38-EH-04CS-06, Building 730 Drainage

Ditch, U.S Army Combat Support Training Center, Camp Parks, Dublin, California,

19 and 20 November 2005.

USACHPPM, 2006e. Soil and Ground-Water Sampling Results No. 38-EH-05ELb-06, Building

791, Former Fuel Storage Area, U.S Army Combat Support Training Center, Camp Parks,

Dublin, California, 8 to 15 August and 9 to 26 September 2006.

E-13

USACHPPM, 2006f. Health Risk Assessment Study No. 39-DA-04GJ-06b, Hazardous Waste

Accumulation Site, Camp Parks, California, May 2006.

USACHPPM, 2007a. Ground-Water Sampling Results No. 38-EH-05ELa-06, Former Building

636, U. S. Army Combat Support Training Center, Camp Parks, Dublin, California, 8 to 15

August and 9 to 26 September 2006.

USACHPPM, 2007b. Ground-Water Sampling Results No. 38-EH-05ELb-06, Former Building

791, U. S. Army Combat Support Training Center, Camp Parks, Dublin, California, 8 to 15

August and 9 to 26 September 2006.

USACHPPM, 2008a. Final Soil Sampling Results No. 38-EH-04CU-06a, Former Building 132,

U.S Army Combat Support Training Center, Camp Parks, Dublin, California, 1 to 19 December

2005.

USACHPPM, 2008b. Final Ground-Water Sampling Results No. 38-EH-07A7-07, Former

Building 636, U. S. Army Combat Support Training Center, Camp Parks, Dublin, California,

March 2008.

USACHPPM, 2008c. Final Ground-Water Sampling Results No. 38-EH-07A7-07, Building

791, Former Fuel Storage Area, U.S Army Combat Support Training Center, Camp Parks,

Dublin, California, March 2007.

USACHPPM, 2008d. Final Ground-Water Sampling Report No. 38-EH-07A8a-07, Southeastern

Quadrant Area, U.S Army Combat Support Training Center, Camp Parks, Dublin, California,

August 2007.

USACHPPM, 2009a. Draft Remedial Investigation/Feasibility Study No. 38-EH-077T-07,

Former Building 109 Incinerator, U.S Army Combat Support Training Center, Camp Parks,

Dublin, California, April 2009.

USACHPPM, 2009b. Final Ground-Water Sampling Results No. 38-EH-07A7-07, Building

791, Former Fuel Storage Area, U.S Army Combat Support Training Center, Camp Parks,

Dublin, California, March 2007

USACHPPM, 2009c. Final Ground-Water Sampling Report No. 38-EH-07A8a-07, Former

Building 888, U.S Army Combat Support Training Center, Camp Parks, Dublin, California,

February 2009.

USACHPPM, 2010. Draft Environmental Condition of Property Report for the Dublin Crossing

(Formerly the 180-Acre) Real Property Exchange Area, U.S Army Combat Support Training

Center, Camp Parks, Dublin, California, January 2010.

E-14

USACHPPM, 2011. Final Environmental Condition of Property Report No. 38-EH-3589-10

Dublin Crossing (Formerly the 180-Acre) Real Property Exchange Area, U.S Army Combat

Support Training Center and Camp Parks, Dublin, California, June 2011.

United States Army, 2005, Memorandum from Assistant Secretary of the Army Subject:

Transmittal of Model Language for Finding of Suitability to Transfer (FOST) and Deeds

Pertaining to Army Real Estate, January 10 2005 with May 1 2013 update

United States Army Corps of Engineers, 1951a. Site Drawing 350102.2 (sheet 8 of 12), Bliss &

Hurt, Trudell & Berger Architects and Engineers, 25 August 1951.

United States Army Corps of Engineers, 1951b. Engineering Drawing No. 38 09 02.4, Sheet 15

of 18, Parks Air Force Base, Processing Building No. 2 (Building 870), Heating Plan,

28 November 1951.

United States Army Corps of Engineers, 1951c. Engineering Drawing No. 38 09 02.3, Sheet 16

of 18, Parks Air Force Base, Processing Building No. 2 (Building 870), Heating Details,

28 November 1951.

United States Army Corps of Engineers, 1952. COE, San Francisco District, Engineering

Drawing Number 36 29 01, Sheet 9 of 10, Structural Fire Station Plumbing Plan, Building 636,

13 May 1952.

United States Army Corps of Engineers, 1954. Engineering Drawing: Modification of Building

151, 3275th Air Force Indoctrination Wing, Parks Air Force Base, 28 July 1954.

United States Army Corps of Engineers, 1955. Engineering Drawing, Rehabilitation of Quonset

Hut for Petroleum Offices, Site and Plot Plans, 6 January 1955.

United States Army Corps of Engineers, 1993. Building Demolition - Phase II, Photograph,

Floor Plan, and Record Data for Buildings 781, 782, and 783, Sheet C18, 20 of 21, File No. 381-

25-0022.

United States Army Corps of Engineers, 1994. Site Drawing 6402916, Upgrade Washrack,

Department of the Navy, Naval Facilities Engineering Command, Navy Public Works Center,

18 August 1994.

United States Army Corps of Engineers, 2003. Ordnance and Explosives Archives Search

Report, Conclusions and Recommendations, Parks Reserve Forces Training Area, Dublin,

California, United States Army Corps of Engineers, Rock Island District, Defense Environmental

Restoration Program.

E-15

United States Army Public Health Command, 2010. Monitoring Well Decommissioning Report

No. 38-EH-0CGV-10, U.S Army Combat Support Training Center (USACSTC), Camp Parks,

Dublin, California, 26 October - 10 November 2009.

URS, 2007, Final Historical Records Review, United States Army Combat Support Training

Center & Camp Parks, Dublin, California, Military Munitions Response Program

Wolfe, BH, 2010, No Further Action, Building 791, Former Fuel Storage Area, US Army

Combat Support Training Center, Camp Parks, Dublin, Alameda County

Wood, WS, 2006, Memorandum for Record Subject: Closure of Hazardous Waste Sites at Camp

Parks, May 16, 2006

Woodward-Clyde Federal Services, 1993a. 47-Acre Surplus Parcel Preliminary Assessment

Screening, Parks Reserve Forces Training Area, December 1993.

Woodward-Clyde Federal Services, 1993b. 12-Acre Proposed California National Guard

Armory Site Limited Preliminary Assessment Screening, Parks Reserve Forces Training Area,

27 December 1993.

Woodward-Clyde Federal Services, 1994a. Preliminary Assessment for Parks Reserve Forces

Training Area, Dublin, California, 27 May 1994.

Woodward-Clyde Federal Services, 1994b. Site Characterization Work Plan Building 109 UST,

Parks Reserve Forces Training Area, 8 July 1994.

Woodward-Clyde Federal Services, 1994d. Remedial Investigation Services for Suspected Soil

Contamination and UST Sites, 28 September 1994.

Woodward-Clyde Federal Services, 1994e. Tank 732-2: Subsurface Investigation at Building

732 - Final Report, Camp Parks Reserve Forces Training Area, Contract DACA05-92-D0032, 20

October 1994.

Woodward-Clyde Federal Services, 1996b. Closure Report for Tanks at Bldgs 770, 1135, 1136,

and 1180, Parks Reserve Forces Training Area, 18 January 1996.

Woodward-Clyde Federal Services, 1996c. Letter Report From: William Loskutoff, To: Ms Eva

Chu, Hazardous Materials Specialist, Alameda County Health Care Services Agency, Subject:

Underground Storage Tank Removal Report, Parks RFTA, POL Point - Building 888, 22

November 1996.

E-16

E-17

ENCLOSURE 3

TABLE 1- DESCRIPTION OF PROPERTY

E-18

TABLE 1. DESCRIPTION OF PROPERTY

Building Number and

Property Description

Parcel

Designation

Condition

Category

Remedial Actions

F101

Confinement Facility

None

F102

Administrative Bldg

None

F103

Administrative Bldg

None

F104

Administrative Bldg

None

F105

Police Station

None

F110

Administrative Blvd

None

F111

Clothing & Equipment

Repair Shop

None

F112

Flammable material storage

None

F115

Sewage pump house

Flammable material storage

None

140

Sentry Hut

None

141

Classrooms, Administrative

None

F152

Unknown

None

F161

Bakery

None

162

Warehouse

11(

None

171

Warehouse

13(

None

180

Administrative & signal

equipment ops

14(

None

634

Fire Dept Storage

None

F635

10.0 Fire Dept Storage

15(

None

F725

Warehouse

None

F726

Unknown

None

F727

Warehouse

None

E-19

Building Number and

Property Description

Parcel

Designation

Condition

Category

Remedial Actions

730A

Hazardous Waste Storage

None

730B

Hazardous Waste Storage

None

730C

Vehicle Washrack

(3)

None

731

Electronics repair,

Administrative

None

F732

Fuel Point

19(

None

F735

Vehicle Storage

None

740

Sewer Screw

None

F770

Underground personnel

shelter

21(1)

None

F785

Latrine

None

790

Administrative

23(

None

791

DPW maintenance & repair

shop

25(

(Wolfe, 2010)

T793

DSRSD Field Opns Center

None

F793

Facilities Engineering

None

793

Hazardous Waste Storage

27(

None

F794

Small parts storage

29(

None

F795

Administrative

None

796

Training aids workshop,

shipping & receiving,

museum

30(

None

F797

Unknown

None

F797

Flammable Materials

Storage

None

F798

Storage

None

F831

Unknown

None

F832

None

E-20

Building Number and

Property Description

Parcel

Designation

Condition

Category

Remedial Actions

Tool room, shop, bin

storage

F833

unknown

None

F850

Barn/small office area

None

F851

barracks

None

F852

Barracks

None

F853

Barracks

None

F854

Barracks

None

F855

Barracks

None

F856

Barracks

None

F857

Barracks

None

F860

Barracks

None

F861

Barracks

None

861

Warehouse

None

F862

Barracks

None

862

Vehicle Maintenance

None

F863

Barracks

None

F864

Barracks

None

F865

Unknown

None

F870

Personnel processing,

medical admin

33(1)

None

F871

Barracks

None

F872

Barracks

None

F873

Barracks

None

F874

Barracks

None

880

Classrooms, administrative

None

E-21

Building Number and

Property Description

Parcel

Designation

Condition

Category

Remedial Actions

F880

Gymnasium

None

881

Classrooms,

administrative

None

F891

Barracks

None

F892

Barracks

None

F893

Barracks

None

F894

Barracks

None

F895

Barracks

None

F896

Barracks

None

F897

Barracks

None

F902

Barracks

None

F903

Barracks

None

F904

Barracks

None

F905

Barracks

None

F910

Barracks

None

F911

Barracks

None

F920

Barracks

None

F921

Barracks

None

F922

Barracks

None

F923

Barracks

None

Potential Construction

Debris Dump Sites

36(1)

None

Former Lumber Yards

38(3)

None

Stockpiled Soils, East

Side of Fernandez Ave

39(

None

730

Vehicle Maintenance

17(

Diesel release to soil, remediation complete, site closed (Wood, 2006)

F132

Recycling Center

7(3)

Release of metals to soil. Risk assessment complete, no further action

required, closure granted (Sarmiento 2006)

F151

10(3)

Release of VOCs to soil. no further action required (Hart, 2012)

E-22

Building Number and

Property Description

Parcel

Designation

Condition

Category

Remedial Actions

Commissary

F781-F784

Self help complex

22(3)

Release of petroleum, VOCs and metals to soil. Risk assessment

complete, no further action required, closure granted (Wood, 2006)

F636

Fire Station

16(3)

Release of diesel and metals to soil and groundwater below regulatory

limits, monitoring wells destroyed, site closed. (Hart , 2011)

Building 791-792 Fuel

Storage Area

24(3)

Release of diesel and metals to groundwater below regulatory limits,

monitoring wells destroyed, site closed (Hart, 2012)

319th Sig Battalion Yard

Area

28(3)

Release of diesel and metals to soil and groundwater below regulatory

limits, site closed (Hart, 2012)

SEQA

40(3)

Release of metals to groundwater below regulatory limits, monitoring

wells destroyed, site closed (D’Onofrio, 2009)

Former Hazardous Waste

Accumulation Site

41(3)

Release of pesticides to soil. Risk-based closure. Site closed.

(Sarmiento, 2006)

F888

Gasoline Station

34(3)

Release of metals to groundwater below regulatory limits, no

remediation required. Monitoring wells destroyed. Site closed.

(D’Onofrio 2009)

Railroad spurs

37(3)

Herbicides, PCBs, SVOCs. Site closed (Escarda, 2013)

130

Warehouse

5(4)

Lead in soil. Remediation complete. Cleaned to unrestricted

use/unlimited exposure (D’Onofrio, 2008)

131

Warehouse

6(4)

Release of lead and radionuclides to soil. Remedy complete, site closed

(Hart, 2012)

150

Warehouse

9(4)

Lead in soil. Remediation complete. Cleaned to unrestricted

use/unlimited exposure (D’Onofrio, 2008)

170

Meat packing plant,

warehouse

12(4)

Lead in soil. Remediation complete. Cleaned to unrestricted

use/unlimited exposure (D’Onofrio, 2008)

792

Warehouse, vehicle

maintenance

26(4)

Lead in soil, cleanup complete. Cleaned to unrestricted use/unlimited

exposure (D’Onofrio, 2008)

860

RTS

-MED Center

31(4)

Approximately 2 gallons of diesel fuel was reported to have spilled onto

the soil near the

north gate of this facility in February 1994 (Woodward-

Clyde Federal Services, 1994a). The contaminated soil was excavated

and disposed in May 1994 (Woodward

-Clyde Federal Services, 1994d).

(Hart, 2012)

Former RTS Med Motor

Pool

32(4)

Sampled as part of Southeast Qu

adrant Area

926

PG&E Substation

35(4)

Soil removal for minor PCB release, no further action(Hart, 2012)

Category 1: Areas where no release or disposal of hazardous substances or petroleum products

has occurred. (Including no migration of these substances from adjacent areas)

Category 2: Areas where only release or disposal of petroleum products has occurred

Category 3: Areas where release, disposal, and/or migration of hazardous substances has

occurred, but at concentrations that do not require a removal or remedial response.

Category 4: Areas where release, disposal, and/or migration of hazardous substances has

occurred, and all removal or remedial actions to protect human health and the environment have

been taken.

E-23

ENCLOSURE 4

TABLE 2. NOTIFICATION OF HAZARDOUS SUBSTANCE STORAGE, RELEASE, OR

DISPOSAL

E-24

Table 2. NOTIFICATION OF HAZARDOUS SUBSTANCE STORAGE, RELEASE OR

DISPOSAL

Building

Number

Name of

Hazardous

Substance(s)

Date of Storage, Release, or

Disposal

Remedial Actions

130

Warehouse

Lead-based

paint (LBP)

1944-present

LBP in soil. Remediation complete. Cleaned to

unrestricted use/unlimited exposure (D’Onofrio, 2008)

131

Warehouse

LBP

1952-present

Release of LBP and radionuclides to soil. Remedy

complete, site closed (Hart, 2012)

F132

Recycling

Center

Metals

1944-1993

Chromium was released to soil adjacent to Former

Building 132, (USACHPPM, 2004; 2005; 2008a).

Although chromium was detected in soil at

concentrations greater than the environmental screening

level (ESL) applicable at the time of sampling, a human

health risk assessment concluded there was no risk to

human health (USACHPPM, 2006b). The California

Department of Toxic Substances Control (CDTSC)

concurred with this finding in a letter dated 16 August

2006 (Enclosure 4).

150

Warehouse

LBP

1944-present

LBP in soil. Remediation complete. Cleaned to

unrestricted use/unlimited exposure (D’Onofrio, 2008)

F151

Commissary

VOCs

1944-unknown

Release of VOCs to soil. no further action required

(Hart, 2012)

170

Meat packing

plant,

warehouse

LBP

1944-present

LBP in soil. Remediation complete. Cleaned to

unrestricted use/unlimited exposure (D’Onofrio, 2008)

F636

Fire Station

VOCs,

metals

1953-2005

Metals and petroleum hydrocarbons were detected in

soil and groundwater samples at Former Building 636

(USACHPPM, 2006c; 2007a; 2008b). USACHPPM

conducted quarterly groundwater monitoring at this site

from September 2006 to March 2008. Some petroleum

hydrocarbon concentrations exceeded the ESLs

applicable at the time of sampling; however, the

exceedences were only slightly greater than the ESLs

and the CDTSC and CRWQCB has determined no

further action is required. (DTSC, July 14 2011)

E-25

Building

Number

Name of

Hazardous

Substance(s)

Date of Storage, Release, or

Disposal

Remedial Actions

730

Vehicle

Maintenance

VOCs,

SVOCs,

metals

1952-present

Building 730 is a vehicle repair facility that contains, or

formerly contained, three washracks, several oil/water

separators, two oil drainage pits, and five hydraulic lift

systems. The hydraulic lift systems are discussed

further in Section 4.4. Arsenic, petroleum hydrocarbons,

and volatile organic compounds (VOCs) were released

to soil in concentrations greater than the ESLs applicable

at the time of sampling (USACHPPM, 2002e; 2010).

Two of three washracks have been removed and the

third is currently in use. One oil drainage pit and

associated soil, concrete, and asphalt containing

petroleum hydrocarbons was removed and properly

disposed in May 2006 (Environmental Chemical

Corporation, 2006). The CDTSC issued a No Further

Action letter for the oil drainage pit removal on 22 May

2007 (Enclosure 4). The arsenic and VOC release

occurred in a drainage ditch adjacent the northern site

boundary. USACHPPM collected confirmatory samples

from this ditch in 2004. Arsenic and VOCs were not

detected at concentrations greater than ESLs applicable

at the time of sampling (USACHPPM, 2004; 2005). The

sampling was conducted with that for Former Buildings

781-784 (see below, this section; same drainage ditch).

The CRWQCB issued a No Further Action letter for the

drainage ditch on 4 May 2006 (Enclosure 4).

F781-F784

Self help

complex

VOCs,

metals

1959-unknown

Chromium, lead, and petroleum hydrocarbons were

detected in soil samples from a drainage ditch adjacent

to these former buildings in 2003 and 2004

(USACHPPM, 2004; 2005). Some concentrations

exceeded the ESLs applicable at the time of sampling;

however, the exceedences were only slightly greater

than the ESLs and the CRWQCB issued a No Further

Action letter on 4 May 2006 (Enclosure 4).

Building 791-

792 Fuel

Storage Area

metals

1952-unknown

Metals, petroleum hydrocarbons, and semivolatile

organic compounds (SVOCs) were detected in soil and

groundwater samples from a former fuel dispensing area

located between Buildings 791 and 792 (USACHPPM,

2004; 2005; 2006e; 2007b; 2008c). USACHPPM

conducted quarterly groundwater monitoring at this site

from September 2006 to March 2008. Some petroleum

hydrocarbon, SVOCs, and metals concentrations

exceeded the ESLs applicable at the time of sampling;

however, the exceedences were only slightly greater

than the ESLs and the CRWQCB issued a No Further

Action letter in January 2010 (Enclosure 4).

E-26

Building

Number

Name of

Hazardous

Substance(s)

Date of Storage, Release, or

Disposal

Remedial Actions

792

Warehouse,

vehicle

maintenance

LBP

1953-present

LBP in soil, cleanup complete. Cleaned to unrestricted

use/unlimited exposure (D’Onofrio, 2008)

860

RTS-MED

Center

TPH-d

1993-present

Approximately 2 gallons of diesel fuel was reported to

have spilled onto the soil near the north gate of this

facility in February 1994 (Woodward-Clyde Federal

Services, 1994a). The contaminated soil was excavated

and disposed in May 1994 (Woodward-Clyde Federal

Services, 1994d).

F888

Gasoline

Station

VOCs,

metals

1952-1998

Release of metals to groundwater below regulatory

limits, no remediation required. Monitoring wells

destroyed. Site closed. (D’Onofrio 2009)

926

PG&E

Substation

PCBs

Unknown

Soil removal for minor PCB release, no further

action(Hart, 2012)

319th Sig

Battalion

Yard

Area

Metals

Unknown

Release of diesel and metals to soil and groundwater

below regulatory limits, site closed (Hart, 2012)

SEQA

VOCs,

metals

1942, 1952

Metals and petroleum hydrocarbons were detected in

groundwater at this site in 2003 at concentrations

exceeding the ESLs applicable at the time of sampling.

USACHPPM conducted quarterly groundwater sampling

at the site from November 2004 to August 2007. All

exceedences were within the same order of magnitude

as the ESLs and the CDTSC issued a No Further Action

letter for the SEQA on 28 May 2009 (Enclosure 4).

Former

Hazardous

Waste

Accumulation

Site

Pesticides,

herbicides,

metals

unknown

Barium, zinc, and pesticides were detected in soils at

this site and in an adjacent drainage ditch in 2004.

Subsequent sampling did not confirm the presence of

barium and zinc, but did confirm the presence of

pesticides at concentrations greater than the ESLs

applicable at the time of sampling (USACHPPM 2004;

2005). USACHPPM conducted a Risk Assessment for

the site in 2006 and concluded the site did not pose a

risk to potential residents, construction workers, or

wildlife receptors (USACHPPM, 2006f). The CDTSC

issued a letter concurring with USACHPPM findings on

16 August 2006 (Enclosure 4).

Site 37

Railroad spurs

Herbicides,

PBCs,

SVOCs

unknown

Site closed (Escarda, 2013)

• The information contained in this notice is required under the authority of regulations promulgated under

section 120(h) of the Comprehensive Environmental Response, Liability, and Compensation Act (CERCLA or

E-27

Building

Number

Name of

Hazardous

Substance(s)

Date of Storage, Release, or

Disposal

Remedial Actions

‘Superfund”) 42 U.S.C. 9620(h). This table provides information on the storage of hazardous substances for

one year or more in quantities greater than or equal to 1,000 kilograms or the hazardous substance’s CERLCA

reportable quantity (whichever is greater). In addition, it provides information on the known release of

hazardous substances in quantities greater than or equal to the substances CERCLA reportable quantify. See

40 CFR Part 373

E-28

ENCLOSURE 5

NOTIFICATION OF PETROLEUM PRODUCT STORAGE, RELEASE, OR DISPOSAL

E-29

Table 3. Notification of Petroleum Product Storage, Release, or Disposal.

Building

Number

Name of

Petroleum

Product(s)

Date of Storage, Release, or

Disposal

Remedial Actions

F112

Flammable

Materials

Storage

Unknown - 1993

No release

F115

Flammable

Materials

Storage

1942-1994

No release

180

Administrative

& supply

1952-present

500 gallon AST. No release

F635

Fire Dept

Storage

1953-2005

No release

F636

Fire Station

Diesel

1953-2005

Release of diesel and metals to soil and groundwater

below regulatory limits, monitoring wells destroyed, site

closed. (Hart , 2011)

730

Vehicle

maintenance

Diesel

1952-present

Release of diesel to soil, remedy complete, site

closed. (Wood, 2006)

F732

Fuel point

Diesel

1952-1993

No release

F770

Underground

personnel

shelter

Diesel

1959-1994

700 gallon diesel UST. No release

F781-784

Self help

complex

1959-unknown

Release of petroleum, VOCs and metals to soil. Risk

assessment complete, no further action required, closure

granted (Wood, 2006)

791/792

Fuel Storage

Area

Diesel

1952-unknown

1,000 gallon AST. Release of diesel and metals to

groundwater below regulatory limits, monitoring wells

destroyed, site closed (Hart, 2012)

793

Hazardous

Waste Storage

1998-present

No release

319th Sig Bn

Yard Area

Diesel

Unknown

Release of diesel and metals to soil and groundwater

below regulatory limits, site closed (Hart, 2012)

Former RTS

Med Motor

Pool

Diesel

1993-unknown

< 5 gallons diesel

F888

Gasoline

Station

Gasoline

Diesel

Waste Oil

1952-1998

10,000 gallon gasoline UST, 10,000 gallon diesel UST,

500 gallon waste oil UST. Release of metals to

groundwater below regulatory limits, no remediation

required. Monitoring wells destroyed. Site closed.

(D’Onofrio 2009)

E-30

Building

Number

Name of

Petroleum

Product(s)

Date of Storage, Release, or

Disposal

Remedial Actions

Site 40 / SEQA

Maintenance

Shops

1942, 1952

No petroleum release, release of metals to groundwater

below regulatory limits, monitoring wells destroyed, site

closed (D’Onofrio, 2009)

Trench 3

Probably

mineral-oil

based

hydraulic

fluid

Unknown

Soil removal, composting/landfarming treatment, no

further action (Escarda, 2013)

Site 36

Diesel

Unknown

Soil removal, composting/landfarming treatment, no

further action (Escarda, 2013)

E-31

ENCLOSURE6

CERCLA NOTICE, COVENANT, AND ACCESS PROVISIONS AND OTHER DEED

PROVISIONS

E-32

ENCLOSURE 6

CERCLA NOTICE, COVENANT, AND ACCESS PROVISIONS AND OTHER DEED

PROVISIONS

I. Property Covered by Covenant and Access Rights Made Pursuant to Section

120(h)(4)(D) of the Comprehensive Environmental Response, Compensation, and

Liability Act of 1980 (40 U.S.C. Section 9620(h)(4)(D)(i)):

For parcels in Phase 1A Planning Area 2C, Phase 1B Planning Area 4A, Phase 2 Planning Area

4A and Planning Area 8, Phase 3 Planning Area 5A and 5C and Phase 4 Planning Area 4B and 8

of the Property, the Grantor provides the following covenants and retains the following access

rights:

A. Covenant Pursuant to Section 120(h)(4)(D)(i) of the Comprehensive Environmental

Response, Compensation, and Liability Act of 1980 (CERCLA) (42 U.S.C. §

9620(h)(4)(D)(i)):

Pursuant to Section 120(h)(4)(D)(i) of the Comprehensive Environmental Response,

Compensation and Liability Act of 1980 (42 U.S.C. § 9620(h)(4)(D)(i)), the United States

warrants that any response action or corrective action found to be necessary after the date of this

deed for contamination existing on the property prior to the date of this deed shall be conduced

by the United States.

B. Access Rights Pursuant to Section 120(h)(3)(A)(iii) of the Comprehensive Environmental

Response, Compensation, and Liability Act of 1980 (42 U.S.C §9620(h)(3)(A)(iii):

The United States reserves a perpetual and assignable easement and right of access on, over,

and through the property, to enter upon the property in any case in which a remedial action or

corrective action is found to be necessary on the part of the United States, without regard to

whether such remedial action or corrective action is on the Property or on adjoining or nearby

lands. Such easement and right of access includes, without limitation, the right to perform any

environmental investigation, survey, monitoring, sampling, testing, drilling, boring, coring,

testpitting, installing monitoring or pumping wells or other treatment facilities, response action,

corrective action, or any other action necessary for the United States to meet its responsibilities

under applicable laws and as provided for in this instrument. Such easement and right of access

shall be binding on the Grantee and its successors and assigns and shall run with the land.

In exercising such easement and right of access, the United States shall provide the Grantee or

its successors or assigns, as the case may be, with reasonable notice of its intent to enter upon the

property and exercise its rights under this clause, which notice may be severely curtailed or even

eliminated in emergency situations. The United States shall use reasonable means to avoid and

to minimize interference with the Grantee’s and the Grantee’s successors’ and assigns’ quiet

enjoyment of the property. At the completion of work, the work site shall be reasonably

E-33

restored. Such easement and right of access includes the right to obtain and use utility services,

including water, gas, electricity, sewer, and communications services available on the property at

a reasonable charge to the United States. Excluding the reasonable charges for such utility

services, no fee, charge, or compensation will be due the Grantee, nor its successors and assigns,

for the exercise of the easement and right of access hereby retained by the United States.

In exercising such easement and right of access, neither the Grantee nor its successors and

assigns, as the case may be, shall have any claim at law or equity against the United States or any

officer or employee of the United States based on actions taken by the United States or its

officers, employees, agents, contractors of any tier, or servants pursuant to and in accordance

with this clause: Provided, however, that nothing in this paragraph shall be considered as a

waiver by the grantee and its successors, and assigns of any remedy available to them under the

Federal Tort Claims Act.

II. Property Covered by Notice, Description, Access Rights, and Covenants Made

Pursuant to Section 120(h)(3)(A) of the Comprehensive Environmental Response,

Compensation, and Liability Act of 1980 (40 U.S.C. Section 9620(h)(3)(A)):

For parcels in Phase 1A Planning Areas 6B, 6D, 6E, Phase 1B Planning Areas 6A, 6C, Phase 2

Planning Areas 2A, 2B, 3A, 3B, 7D, 7E, Phase 3 Planning Areas 2A, 3C, 3E, 5B, 7A, 7B, 8,

Phase 4 Planning Areas 1B, 3D, 4B and 8 and for Phase 5 of the Property, the Grantor provides

the following notice, description, and covenants and retains the following access rights:

A. Notices Pursuant to Section 120(h)(3)(A)(i)(I) and (II) of the Comprehensive

Environmental Response, Compensation, and Liability Act of 1980 (CERCLA) (42 U.S.C.

§9620(h)(3)(A)(i)(I) and (II)):

Pursuant to Section 120(h)(3)(A)(i)(I) and (II) of the Comprehensive Environmental

Response, Compensation, and Liability Act of 1980 (CERCLA) (42 U.S.C. §9620(h)(3)(A)(i)(I)

and (II)), available information regarding the type, quantity, and location of hazardous

substances and the time at which such substances were stored, released, or disposed of, as

defined in section 120(h), is provided in Exhibit 1, [Insert the deed exhibit number for FOST

Table 2 – Hazardous Substance Storage, Release and Disposal, which will be included in the

deed as an exhibit], attached hereto and made a part hereof.

B. Description of Remedial Action Taken, if Any, Pursuant to Section 120(h)(3)(A)(i)(III) of

the Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (42

U.S.C. §9620(h)(3)(A)(i)(III)):

Pursuant to section 120(h)(3)(A)(i)(III) of the Comprehensive Environmental Response,

Compensation, and Liability Act of 1980 (42 U.S.C. §9620(h)(3)(A)(i)(III)), a description of the

remedial action taken, if any, on the property is provided in Exhibit 1, attached hereto and made

a part hereof.

E-34

C. Covenant Pursuant to Section 120(h)(3)(A)(ii) and (B) of the Comprehensive

Environmental Response, Compensation, and Liability Act of 1980 (42 U.S.C

§9620(h)(3)(A)(ii) and (B)):

Pursuant to section 120(h)(3)(A)(ii) and (B) of the Comprehensive Environmental Response,

Compensation, and Liability Act of 1980 (42 U.S.C §9620(h)(3)(A)(ii) and (B)), the United

States warrants that –

(a) All remedial action necessary to protect human health and the environment with respect to

any hazardous substance identified pursuant to section 120(h)(3)(A)(i)(I) of the

Comprehensive Environmental Response, Compensation, and Liability Act of 1980 remaining

on the property has been taken before the date of this deed, and

(b) Any additional remedial action found to be necessary after the date of this deed shall be

conducted by the United States.

D. Access Rights Pursuant to Section 120(h)(3)(A)(iii) of the Comprehensive

Environmental Response, Compensation, and Liability Act of 1980 (42 U.S.C

§9620(h)(3)(A)(iii):