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SUMMARY REPORT: BULK ASBESTOS, LEAD-BASED
PAINT AND HAZARDOUS MATERIALS SURVEY
ALCATRAZ CELLHOUSE - CITADEL LEVEL
GOLDEN GATE NATIONAL RECREATIONAL AREA
SAN FRANGISCO, GALIFORNIA
PREPARED FOR:
MR. DANIEL EILBECK
WISS JANNEY ELSTNER ASSOCIATES INC.
2000 PowELL $TREET, SUITE 1650
EMERWILLE, CA 94608
PREPARED BY:
SCA
eruvrnorufo=r\rAl, lNc.
334 1gTH STREET.
OAKLAND, CA94612
TEL: (510) 645-6200
eFAX: (415) 962-0736
SCA PROJECT NO.: B-9873.AS
DECEMBER 13, 2O1O
SIJMMARY REPORT
BI]LKASBESTOS, LEAD-BASED PAINT & HAZARDOUS MATERIALS SURVEY
ALCATRAZ CELLHOUSE _ CITADEL LEVEL
GOLDEN GATE NATIONAL RECREATIONAL AREA
SAN FRANCISCO, CALIFORNIA
CONDUCTED FOR
MR. DANIEL EILBECK
WISS JANNEY ELSTNER ASSOCIATES INC.
2000 PowELL STREET, SUITE 1650
EMERYVTLLE, C494608
DECEMBER 13,2010
SCA PROJECT NO. B-9873.4S
PREPARED BY:
GLENN R. CASS, CIH, PE, C^C #92-0092
VICE PRESIDENT
scA ENVTRONMENTÄL, rNC.
334 19ÏE STREET
OAKLAND, CA94612
TEL: (s10) 645-6200 eFAX: (415) 962-0736
Summary Report for Asbestos and Lead Paint Survey Alcatraz Cellhouse Citadel Level, Golden Gate National Recreational Area, San Francisco, CA a"O ,ro."., *o..,_n'^ paoe i
Table of Contents
3.1 Asbestcts Containing Materials '.'.........'......'...'4
3.2 Lead-Based Paints ........... .......'..4
3.3 Lead-Contaminated Soils & BulkAnalysess,.............. .'.'....'.4
4.1 Asbestos_Cont¿ining Materials
4.2 Lead-Based Paints ........... .'.....'...5
5.0 Results and Conc1usions................. '............'
5.2 Non-Asbestos Materials (non-ACM).. ....'.'
5.3 Lead-Based Paints ........... .'...".10
5 .4 Lead Contaminated Soils & Butk Analyses ................., ......... ' '..'.'.'.. '..... '. I I
6.0 Limitations and Exc1usions................,... ..".....'
Attachments
l. Laboratory Results - Asbestos
2. Representative Lead-Based Paint XRF Sampling Results
3. Soil Sampling Results
4. Field Data Sheets
5. Sampling Location Drawings
6. Previous Asbestos Sampling Results
7. Previous Lead Bulk Sampling Results
8. Remedial Action Alte¡ratives
Alcatraz'cellhouse citadel Level, Golden Gate National Recreational Area, san Francisco, cA
Paqe ii
List of Common Acronyms and Abbreviations
AJA,{ : Assumed Asbestos-Containing Materials
ACM : Asbestos-Containing Materials AHERA : Asbestos HazardEmergency Response Act BAAQMD : the Bay Area Air Qualþ Management District
BK : black paints
Bt : blue paints
BR : brownpaints CAC : Certifred Asbestos Consultant
CaVOSHA : the California Division of Industrial Safety and Health
CaVEPA : the California Environmental Protection Agency
CAULK : window and doorperimeter caulking
CCR : California Code of Regulations
CERCLA : Comprehensive Environmental Response, Compensation, and Liability Act
CFR : Code of Federal Regulations
CHMM : Certified Hazardous Materials Manager
CIH : Certified Industrial Hygienist CPSC : Consumer Product Safety Commission
CR : cream-colored Paints CSST : Certified Site Surveillance Technician
DOHS : the California Department of Health Services
DSIPLM : Polarized Light Microscopy with Dispersion Staining
EpA : the U.S. payj¡snmental Protection Agency
EPRI : Electric Power Research Institute
E)GJNT : expansion joint FIFRA : Federal Insecticide, Fungicide, and Rodenticide Act
FLVCS : linoleum flooring FLVCT : vinyl composite floor tiles # : square feet
GN : green Paint-s GROUT : ceramic tile and concrete grouts
GY : grayPaints
HIID : the U.S. Department of Housing and Urban Development
LBP : Lead-Based Paints
LF : linear feêt
¡t"g/ct* : micrograms per centimeter squared
ILC\C : microgram per gram or equivalent to parts per million pglm3 = micrograms per cubic meter rm : microns mglcrÊ : milligrams per squared centimeter mg/xg : milligrams Per kilogram MR : maroon paints
OL : olive paints
OR : orange Paints osHA : the federal occupational Safety and Health Administration
OW : off white paints
PCB : Polychlorinated BiphenYl
PEL : Permissible ExPosure Level Penta : PentachloroPhenol
Summary Report for Asbestos and Lead Palnt Survey
ÃË"iä'C.iifioúte Citadet tevel, èãi¿en Gate National Recreational Area, San Francisco, CA
PISTM
PK
ppm
PUTTY
QA/QC
RCRA
Rcw
RD
REA
RFAG
RTPTCH
RFROLL
RWQCB
SF
TN
TSI
WAC
WH
WLCER .
WLPL
YW
List of Common Acronyms and Äbbreviations Cont'
: steam thermal system pipe insulation : pinkpaints : parts per million : windowpane putly : Qualify Assurance/Quaüty Control : Resource Conservation Recovery Act : Regulated Controlled Waste : red paints : Registereä Envi¡onmental Assessor : built-up tar and gravel roofing : roof patching comPounds : rolled roofing : the Regional Water Quãlity Control Board
- square feet : tan paints : Thennal System Insulation : Washinefon Admiùistrative Code : white paints : ceramic walltiles : wall plaster : yellow paints
Alcatraz Óellhouse Citadel Level, Golden Gate National Recreational Area, San Francisco, CA
Paoe I
1.0 Executive SummarY
SCA Environmental, Inc. (SCA) conducted apafüalpre-renovation hazardous materials survey for lead-based paints, asbestos-containing construction materials, and associated environmental hazards at the Alcatraz Cellhouse Citadel
Level at Golden Gate National Recreational Area i¡ San Francisco, CA (hereafter referred to as "the Building") on
Tuesday, November 16, 2010.
Prior to any renovations or demolition, the National Emission Standard for Hazardous Air Pollutants (NESHAP) mandated by the Envi¡onmental Protection Agency (EPA) and locally enforced by the Bay Area Air Quality Management District (BAAQMD) require that buildings be inspected for asbestos-containing materials (ACM) and materials subject to damage or which will be made friable, be removed.
Sampling by SCA in November 2010 found the following ACM:
. None identif,red at the Citadel Level.
Sampling by Cal Inc. in November 2002 simila¡ly found all tested substrates in the Citadel to be non-4sbestos (see
Attachment 6): -
"Ttaee" asbestos-containing materials (>0.1% and<lo/o asbestos byweight) sampled by SCA include:
. None identified for the Citadel Level.
Non-asbestos materials sampled and documented by SCA i¡clude:
. Gray mortars at Citadel brick construction [SCA Sample I.D. CIT-MORTAR-101-1 thru 3].
. Red brick at Citadel partially painted [SCA Sample I.D. CIT-BRICK-102-1 thru 3].
. Wall plasters at interior cells on masonry walls at Citadel Level [SCA Sample I.D. CIT-WLPL-103-1 thru 3 and Cal Inc. Sample I.D. 01 thru 031.
. Concrete beams with brick aggregate and white surface paints ISCA Sample I.D. CIT-CONC-104-I thru 3 and Cal Inc. Sample I.D. 04 thru 061.
o Unpainted concrete and brick floors throughout Citadel areas fSample I.D. CONC-]N\T].
Lead-based paints (LBP), as defined by U.S. Deparbnent of Housing and Urban Development (HUD), were identifred in the building, including but not necessarily limited to the following:
o Blue and green paints at interior cell door frames on the Citadel Level [GR-03-1 8.BL-04-I & 2 with >5.0 mflcn2l.
. White pai:rts on fueplace bricks at interior cells at the Citadel Level ISCA Sample I.D' WH-01-6 with 1'2 mglcrll.2l.
¡ White paints on plaster wall across from the fireplace il interior cells at Citadel Level ISCA Sample I.D.
WH-01-7 with >5.0 m¡el cú1.
See Attachment2 for a suÍrmary of tested painted substrate ¡esults. Also included within the Summary Table are lead bulk sampling results compiled by Cal Inc. and RGA Envi¡onmental, Inc. :m2002 and2003, respectively'
Most other tested paints and ceramic ftle glazng have a lead content below the HIID def,rnition for LBPs' All site paints shall be treaied as having a lead content greater than 600 ppm requiring demolition dust controls and personal protective procedures in compliance with CaVOSIIA's Construction Lead Standard, 8 CCR 1532'l-
In general, any interior and exterior paints found to be peeling and chipping will require stabilization or scraping prior to the proposed renovations or demolition. All intact painted substrates may be removed and disposed of as non-hazardous 'ffaste.
Alcatraz'Cellhouse Citadel Level, Golden Gate National Recreational Area, San Francisco, CA
,"0" , In addition to the XRF sampling, SCA collected bulk samples of the brick and concrete with brick aggregate substrates to verifu the potential lead content ofthe masonry. Both samples found negligible lead concentrations at
1.6 and 8.3 ppm, respectivelY.
Soil samples were collected using a hand trowel at the south and east facades to determine the potential level of contamjnation of exposed soils immediately under loose and peeling exterior paints. Both samples were analyzed fot total lead by EpA Method SV/ 6010, which is perforrred using inductively coupled plasma atomic emission
,p""t o."opy. All samples were analyzed by McCampbell Analytical Inc.'s California Department of Public Health
E^nvironmentalLabor{tory Accreditation Program (ElAP)-accredited laboratory (ELAP #1644). Reporting limits for lead in soil for EPA Method SW 6010 is 5 mg/kg (5 ppm).
Surface soils were fo¿nd to have a total threshold lead concentration of 3,100 and 830 ppm, respectively' The eastern garden sample has an elevated lead concentration exceeding the CallEPA Tttle 22 standards, classifiing it as a hazardous waste. Both samples were above the EPA and HUD standard of 400 ppm for children play areas, indicating that some remediation of drip line soils will be necessary'
Alcatraz-cellhouse c¡tadel Level, Golden Gate National Recreational Area, San Francisco, cA
Paoe 3
2.0 Introduction
This report suÍìmarizes the results of the fulI demolition hazardous materials survey conducted Ncabraz Cellhouse at
Golden Gate National Recreational Area in San Francisco, CA (hereafter referred to as "the Building") on June 1, 2010. The pu{pose of the survey was to determine the presence of regulated and./or potentially bazardous building materials inìtre Uuit¿ing, which is slated for demolition. Materials addressed in the survey include:
o Asbestos-containingmaterials(ACM);
. Lead-based paints (LBP);
. Lead content inbrick and concrete withbrick aggregate substrates;
o Lead content at exterior drip line at soils; and
. Other environmentalhazards as noted.
Individuals involved in the s¡rvey, and their technical certifications, i¡clude:
The contract laboratory that provided analytical services for the project was:
Laboratory Asbestos TEM Laboratory, Berkele¡ CA
Bulk Asbestos Analysis by Polarized Light Microscopy (PLM)
¡ National Voluntary Laboratory Accreditation Program (N\¡LAP # 101891-0).
o CaliforniaEnvironmental Laboratory Accreditation Prosram (ELAP).
McCampbell Analytical, Inc. Lead Soil & Bulk Subbtrate Analyses
. CaliforniaEnvironmentalLaboratory Accreditation Prosram (ËLAP #1644).
pre-renovation lead-based paint and representative soil and wipe sampling were conducted at the Citadel site and throughout the majority of the cellblo ck n 2002 by Cal Inc. Sampling n 2002 showed a high concentration of lead o., -ãoy of the painteá wa[s and paint chips at the based on the walls throughout the Citadel. Partial stabilization and remediation has occurred within the Citadel to remediate surface lead concentrations previously measured at 510 to 4,000 pglSF in Nove mbet 2002 [Cal Inc. Sample I'D. C-4 úru C-8].
Despite the presence of elevated wipe samples and loose and peeling paints in 2002, aßborte lead concentrations were all found to be under the NAAQS standard of 1.5 pgl#, indicating that when left undisturbed, the presence of lead hazards poses minimal impact to infrequent occupants. Airborne lead concentrations in the Citadel and
Cellblockrangld tott <0:77 to it.1 pglm3 inNovember 2002lCaIInc. Sample I.D. PbO1 thru Pb05l'
General cleanup and remediated occurred in January-February 2003 by Miller Thompson Constructors to include surface vacuuming. Current conditions on-site are considered fairly simila¡ within the Citadel today as the post-remediation conditions found in 2003.
Role
Glenn R. Cass, PE, CIH, CAC
Senior Consultant . Certified Asbestos Consultant (CAC #92-0092);
. Certified Industrial Hygienist (CftI#A4847);
. California Dept. of Public Health Certified Lead
Inspector/Assessor, Project Designer & Project Monitor (DHS #r/DÀ4-717);
. Professional (Mechanical) Engineer (PE #Ml8976), since r978;. OSHA 40-hr. HAZWOPER Trainingper 29 CFR 191.120;
. Registered Environmental Assessor (REA-06164); and . Radiation Safetv Specialist (Scitec & Niton XRF's)'
Alcatraz-cellhouse citadel Level, Golden Gate National Recreational Area, San Francisco, CA
Paqe 4 SCA Proiect No.: 8-9873
3.0 MethodologY
3.1 Asbestos Containinq Materials
Asbestos sampling was performed in a fastrion designed to minimize exposure of the surveyor.or others to airborne asbestos frbers. Sãmples were typically removed from the substrate utilizng a knife or hollow drill bit bored through a wet sponge; the ìample mâierial was then placed into an airtight plastic vial. The vial's exterior was decontaminated with u -át ,porrg", and a unique sample I.D. written on the vial. The vial was then stored in a plastic bag. Sample substrates were patihed with a high-temperatur€ caulking compound, where required.
Samples of suspect materials were collected using triplicate sampling procedures. Under these procedures, the hrst ru*it" is analyzed. If it tests positive for asbestos (>lyo), the anaþis is suspended for further samples of that matårial. If the f1¡st sample tests only trace positive (between 0.I to 7%o), or negalive, then the second and thi¡d samples arc analyzed sequentjally, in order to deterrnine the possible presence of asbestos. If all three samples test
'r"gåti,u., the matenal is óonsiderèd as non-asbestos. If one or more samples test "trace" positive (<Io/o), the material is considered to be trace positive. If one or more samples are positive for asbestos, the material is considered positive.
Certain materials, such as plasters and gypboard or sheetrock syst€ms, are frequently non-homogeneous in content.
For such materials, multipie samples were gathered at various points in the buitding, with all samples analyzed to determine the possible presence of asbestos'
All asbestos samples collected were submitted to ATEM for analysis by polarized light microscopy with dispersion staining (DS/?LM). The Bay Area Ai¡ Quality Management District's (BAAQMD), the Federal Environmental protectloà Agenc/s (EpA), and California Environmental Protection Agency's (CaVEPA) regulations all specify the
DSIPLM method.
3.2 Lead-Based Paints
Construction records or drawings concerning paints in the buildings were not available. Paint samples from different exterior surfaces were analyzel ín-situ to identify the presence and extent of lead-containing paints. This included samples from exterior frnishes tlroughout the building. Samples werc analyzed using a Niton XL-700 X-Ray
Fluorescence Q(RF) spectrum analyzér. The XRF analyzer can measure lead contents of several layers of paint without disturbing tie surfaces, thus giving immediate feedback on lead çontents of paint without destructive testing.
The XRF is sensitive to 0.1 milligrams per square centimeter (mg/cm2) of lead, or well below HUD guideline levels of 1 .0 mglcm2 of lead in paints.
XRF analysis data are reported as L-shell values. The L-shell value is the lower energy fluorescence showing the level of fhe surface layàr that is readily disturbed and potentially made airborne, thereby posing a potential constructi on h ealth hazar d.
please note that although LBP were defined against the HUD standard, CaVOSHA's Construction Lead Standard, 8
CCR 1532.1, applies to alt paints with any measured lead content, requiring dust control measures to reduce ai¡bome and ingestion lead dust hazards.
3.3 Lead-Contaminated Soils & Bulk Anabtses
Soil samples were collected using a hand trowel at the south and east facades to deterrnine the potential level of contamination of exposed soils immediately under loose and peeling exterior paints. Both samples were analyzed for total lead by EpA Method SV/ 6010, which is performed using inductively coupled plasma atomic emission spectroscopy. A1l samples were analyzed by McCampbell Analytical Inc.'s California Department of Public Health
ÉnvironmentalLaboratory Accreditation Program (ElAP)-accredited laboratory (ELAP #1644)' Reporting limits for lead in soil for EPA Method SW 6010 is 5 mg/kg (5 ppm).
Alcatraz'cellhouse citadel Level, Golden Gate National Recreational Area, san Francisco, cA
Paoe 5SGA Proiect No.: 8-9873
4.0 Applicable Standards
4.1 Asbestos-ConJq!.n!.nLlu[si[9Llglt
ACM is defined by EPA regulations as those substances containing greater than l%o asbestos. The BAAQMD and the CallqpAprovide local enforcement of these regulations. Friable ACM with greater than l%o asbestos needs to be disposed of as asbestos waste.
prior to demolition of a building, the BAAQMD requires abatement of Regulated Asbestos Containing Materials
RACM þractically, this means all friable and non-friable ACM).
RACM is defhed as (a) Friable - the material can be crumbled, pulverized o¡ reduced to powder by hand pressure,
(b) Category 1 that are subjected to sanding, grinding, cutting or abrasion, (c) Category I materials that becomes friable during demolition or renovation activities, or (d) Category II materials that become friable during demolition or renovatioû activities.
Federal Occupational Safety and Health Administratiòns (OSHA) regulations, locally enforced by CAL/OSHA, defines ACNI as substances that contain greater Ihan I%o asbestos. CaVOSHA also mandates special training, medical exams, personal protective equipment and record keeping for employees working with ACM. If a material contains less than 1% asbèstos but more than 0.1%o asbestos, the material may be disposed of as non-ACM, but the
CaVOSHA requirements would still have to be followed regarding workers'protection and Contractor licensing'
"Trace" materials are currentþ regulated in Califonria and require the following:
r Removal using wet methods;
. Prohibition of removal using abrasive saws or methods which would aerosolize the material;
o Prompt clean-up of the impactedzone,using HEPA-filtered vacuums, as applicable;
o Employer registration by CaVOSHA for removal quantities exceeding 100 sq. ft. per year; and r CaVOSIIA Carcinogen Registration by the Demolition or Abatement Contractor impacting such materials.
Further detail regarding various California asbestos regulations can be found from the following websites:
. http://www.dir.ca.eov/title8/1529.html
. http://www. ciwmb.ca. gov/reeulations/title 14lch3 5.htrn
. htto://www.baaqmd. gov/dst/¡egulations/rg 1 1 02.pdf
¡ htÞ ://www. epa. sov/asbestos/pubs/help'html o http://www. epa. eov/asbestos/pubs/asbre g.hhnl
4 2 Lead-Based Pqints
Since elemental lead is a suspect carcinogen and known teratogen and neurotoxic in high doses, lead-containing materials need to be identified prior'to the on-set of demolition activities. Using combinations of engineering controls and personal protective equipment, lead-containing materials can be remediated safely, Several sources of applicable standards are listed as follows:
Alcatraz ôellhouse Citadel Level, Golden Gate NatioÀal Recreational Area, San Francisco' CA
l. Occupational Exposure: Lead exposures in th€ worlqplace are regulated by CaVOSHA, which has certain regulatory requirements foì identi$ring and controlling potential iead exposures. Currentþ applicable regulâtions for the construction industry have been adopted by CaVOSHA (8 CCR
I'5i21) f¡om the Federal OSH+ regulations. The current OSHA 8-hour Permissible Exposure rcvel (rnt) for lead is 50 pglm3'
2, Lead Waste: The regulatory standards disposal inconsistent, and continually fluctuating, to consistent whether the trend is for a more or less c A myria regulatory standards exist characteizng land use planning objectives and hazardous waste disposal requirements.
In Califomia, effective from January I, lggg to July l,2006,1oose and peeling LBP or other wastes require characterization and testing for leachability, following the standards noted below:
a. If the Total Th¡eshold Level Concentration (TTLC) is <50 ppm, it is considered non-
RCRA, non-hazardous waste since it is impossible to exceed the WET test limit of 5 mgll using the 10 to I ratio.
b. If the TTLC is <350 ppm and the WET test is <5 mgll then the waste has low leachability and is classif,red non-RCRA non-hazardous wast€'
c. If the TTLC is >350 ppm and the WET test is <5 mgll then if agan has low leachability and is classif,red as non-RCRA, non-hazardous waste'
d. If the TTLC is >350 ppm and the V/ET test results are >5 mgll, then the TCLP must be run. Then if the TCLÞls >5 mg/l the waste must be stabilized and if <5-mg/l stabilization is not required. Whether stabilized or not, both conditions are classified as RCRA hazardous waste.
The 350 ppm limit under Health & Safety Code $25157.8 sunset on July 1,2006 and reverted to the previous 1,000 ppm TTLC limit identihed under Title 22 ç6626L34' Nevertheless, SCA recommends mainta^ining the 350 ppm standard for waste characteizalion purposes as the likelihood of this level being reestablished is high' please note that in the above scenario, loose and peeling paints are treated as a separate waste stream; whereas, intact paints may be combined for disposal purposes and classified as
.architectural *urt".' This has allowed for disposal of painted concrete in a Class 3 landfill for many years without limitations. In essence, the total weight of the paint versus the weight of a concrete substrate for intact paints is negligible. One must keep in mind that because of the heterogeneity of typical waste streams, some subsamples or components of that_waste steam may e*"""1h*urdousÇaste thresholds if subsamples or components are small enough. To account for this heterogeneity, waste classification decisions are normally made by DTSC for the 'average' properties of an identified waste stream.
The EpA in 1998 passed a ¡ule which suspended temporarily the applicability of the Resource
Conservarion and Recovery Act (RCRA) Toxicity Characteristic (TC) Rule (40 CFR 267.24) to debris generated during leãd-based paint (LBP) abatement projects conducted at tatget housing;
deleading projects conà'ucted at public or commerciat buildings; and renovation or remodeling and demolition activities attargethousing, public buildings, or coÍrmercial buildings. Instead of being subject to the TC Rule, LÈP debris rèsulting from the above-mentioned activities would be subject to ihe management and disposal standards being proposed today under Title IV of the Toxic
Substances Control Act (TSòA). The EPA proposed this temporary suspension of the TC rule in accordance with RCRA sections 1006(bX1) and 2002 to avoid duplication and inconsistent regulation of LBP debris and to allow the Agency sufficient time to assess whether any RCRA re[uirements, in addition to TSCA Title IV requirements, are necessary to assure proper management and disposal of such debris.
In 1998, the Califomia Department of Toxic Substance Control (DTSC) also reclassified lead construction debris waste from RCRA to TSCA. At that time DTSC retracted their earlier
ÃËåii"l'c"iiriou.e Citadet t-eu"i, êãuen Gate Natioñal Recreational Area, San Francisco, CA statement allowing for disposal of 'architectural waste' in Class 3 landhlls, but they failed to fully $25157.8 on JulY 1, Ord, have run pilot e on-site, DTSC has
Dilution of RCRA hazardous waste for this purpose is specifically disallowed under 40. cFR Part
26I. Ifithe case of recycling of 'architecturál \¡/ãrt"' from Fort Ord, CA, the DTSC st¿ted that the waste stream was not-teing- aitutea, since no materials were being added to the waste stream'
DTSC further went oo to "ã"o*uge recycling and reuse of waste materials as much as possible'
The Fort Ord operations did, however, occur on federal lands and to that extent they were not necessarily bound to state regulations.
while DTSC encourages the recycling of painted substrates, where feasible,maîy local concrele recycler are now hesiìant to accept *y pãiotta substates' in such cases must assess the economic impacts of r.ttstruæ strlpping for recyc sposal as of painted substrates within an approved landhll. Locafórdinance requ recycling may have bearing on the ultimaæ determination of the handling and disposal of intact painted subst¡ate'
For disposal purposes, the following charactetizalions standards apply:
Ãmirar'Cellirouse Citadel Level, èolden Gate Natioñal Recreational Area, San Francisco, CA aste
Segregate Components & Draw Representative Samples ra
Below TTLC (California Standard) Total Threshold Limit Concentration of 1000 mgikg
Per EPA Test SW846?
Greater than 50 mg/kg?
N (Cannot fail WET or TCLP tests)
TCLP
Toxicity Characteristic Leaching
Procedure. ComPare result to
Soluble Threshold Limit Concentration Federal Test for Leachable Metals
Less than 5mg/l?
Dispose of as Class I Hazardous Waste, Stabilization is Required (RCRA
Hazardous Waste)
Dispose of as Glass I Hazardous waste, Stabilization not required' (non-RCRA California Hazardous
Waste)
Test SWS+ Califoùia test for total lead concentration
WET Waste Extraction Test - CALIF test for leachable lead
TCLP Toxicity Characteristic Leaching Procedure'
Federal test for leachability of lead
Total Threshold Limit Concentration (TTLC) 1000 nis/ks Soluble Threshold Limit Concentration (STLC): 5 mg/l
Soluble Threshold Limit Concenffation (STLC): 5 mg/l
Disposal OptÍons:
Class I - Hazardous:
Non-RCRA (Califomiaflazardous) if total lead >1,000 mglkg or
WET >5mg/1 & TCLP <5 mgÂ
RCRA if TCLP > 5 mgll (requires stabilization)
Class II - non-Hazardous il V/ET between L5 &' 5 mgll
Class III - non-Hazardous, including Intact Painted A¡chitectural Components, or
Non-Desiggrated Waste VSTLC <L5 mg/r
3 Dehnitions & Notifications: The major defuritions of LBP or lead-coated surfaces are listed as follows:
a. HUD def,rnes LBP as paint that contains either >0.5% by weight of lead, or >l mglcrf,'
Summary Report for Asbestos and Lead Pa¡nt Survey
Ãtcairaz'Cellnouse C¡tadel Level, Golden Gate Natioñal Recreational Area' San Francisco' CA
4.
b. Consumer product Safety Commission (CPSC) prohibits the manufacturing of paurt that contains more than 600 ppm (0'06%) of lead'
Given the myriad of confusing defrnitions and regulations, this report uses the HUD's definition for the purpose- of identificationi, but compliance to CaVOSIIA's Construction Lead Standard is required for all paints with any measurable lead content'
California proposition 65: Leadis on the "Proposition 65" list, given its toxic potential in causing reproductive hazards.
Worker Certification: The California Department of Public Health (CDPH) requires the use of
Certifred Lead Workers and Supervisors for lead abatement projects at public buildings with a greater than2} years expect is completed specifi faints as defined bV HUO' requirements do not
Lo*"u"r, dust controls and still required under through 36100.
New Renovation, Repair and Painting Rules finalized by the U.S. Environmental Protection
Agency on June iZ,Z¡Og,authorizedunder section a02@)(3) ofthe Toxic Substances Control Act
(T'SCA) require any Contractor or Maintenance Personnel disturbing more than 6 sq. ft' of interior ò, ZO sq. ft. of exterior lead-based paints (LBPs) in pre-1978 housing or chìld-occupied facilities to qompleie EpA-accreditetl training or 4-b¡. EPA-accredited refresher training, as applicable, for iead^safe work practices. Persons performing renovations, repairs andlor painting projects in target housing or chilà-occupied facilitiés must provide "Renovate fught" brochures to the Owners and o""opuï, after Decemb er 22, 2008. Window replacements are subject to the standards, These standards prohibit certain dangerous work practices, such as open flame burning or torching of lead-based paints. Required work practices include posting of wanrin-g signs, restricting occupants from work areas, contãining work areas to prevent dust and debris from spreading, conducting a thorough cleanup and veriffing that the cleanup is effective. Additional rules and information are available at www.epa.sov/1ead, "Certified Renovators" shall perform the following tasks:
o perfo.rq or direct uncertif,red workers perforrning regulated renovation activities;
o Provide training to uncertified workers on lead safe work practices;
o Be on-site during key stages of the renovation and otherwise be available on-site or by telephone at other times;
. Use an acceptable lead test kit to determine whethe¡ lead-based paints are present in an aflected area.
Firrns may apply for ce¡tification beginning in October 2009 and must be certified by April
2010.
San Francisco Exterior Lead-Based Paint Ordinance: The San Francisco Building Department requires tenant and neighborhood notifications and dust control procedures for impacts to interior or exterior HUD-defrnãd and presumed LBPs exceeding 100 sq. ft. This ordinance also prohibits power washing as an abatement method.
Ãlcatraz'Cellhouse citadel Level, Golden Gate Natioàal Recreational Area, San Francisco, CA
5.0 Results and Conclusions
5.1 Asbestos
A total of l2 bulk samples of suspect ACM were collected with 36 materials analyzed considering the multiple layers and serial analyses foi some maierials. The detailed results are shown in the Laboratory Report in Attachment 1'
Sample locations are shown on the drawings included ¿5 {¡¡¿çhment 5'
Sampling by SCA in November 2010 found the following ACM:
. None identifred at the Citadel Level.
sampling by cal Inc. in November 2002 similarþ found all tested substrates in the citadel to be non-asbestos (see
Attacbment 6).
"TÍaee" asbestos-containing materials (>0.1% and<lo/o asbestos by weight) sampled by SCA include:
o None identified at the Citadel Level'
5.2 Non-AsbestosMaterials(non-ACMI
Non-asbestos materials sampled by SCA irclude:
. Gray mortars at Citadel brick construction ISCA Sample LD. CIT-MORTAR-101-1 thru 3].
. Red brick at Citadel partiallypainted [SCA Sample I.D. CIT-BRICK-102-1 thru 3]'
. Wall plasters at interior cells on masonry walls at Citadel Level ISCA Sample I.D. CIT-WLPL-103-1 thru 3 and Cal Inc. SamPle I'D. 01 thru 031.
. Concrete beams with brick aggregate and white surface paints ISCA Sample I.D. CIT-CONC-104-1 thru 3 and Cal Inc. Sample I.D. 04 thru 061.
¡ Unpainted concrete and brick floors throughout Citadel areas [Sample I'D. CONC-NNNI.
t 3 Lead-Based Paints
Lead-based paints (LBP), as defured by U.S. Departnnent of Housing and Urban Development (HUD), were identifred at the site, including but not necessarily limited to the following:
o Blue and green paints at interior cell door frames on the Citadel Lovel [GR-03-1 &,BL-04-1& 2 with >5'0 mglcrn2).
. White paints on fireplace bricks at interior celis at the Citadel Level [SCA Sample I.D. WH-01-6 with 1'2 m/cm2l.
o White pdints on plaster wall across from the fireplace in interior cells at Citadel Level ISCA Sample I'D'
WH-O I -7 with >5.0 mgl cm2\
See Attachment 2 for a summary of tested painted substrate results. Also included within the Summary Table are lead bulk sampling results compiied by Cal Inc. and RGA Envi¡onrnental, Inc. t1'2002 and 2003, respectively'
Few site paints were found to be below the HUD LBP criteria, although s are required trrorghoot the demolition of painted elements to comply with the cavosHA R 1532'1' All site p-aints shall be treated as having a lead conteni greater than 600 ppm procedures in compliance with 8 CCR 1532.1.
Loose and peeling paints should be removed under controlled procedures prior to any demolition of the structure.
ñorr. of tn. uppi*i*ute regulations require removal of LBP prior to demolition or renovation if the paints are s..rrr"ly adherËá to the sub'strates (i.e.,ion-flaking or non-peeling). Disposal of the demolition debris in this case
ÃÈatraz'ce¡tfiouse Citadel Level, Golden Gate Natioñal Recreational Area, sân Francisco, CA canb€hand1edaSnon-hazardouSandnon-RCItAwaSteaftertleloose"" as demolition practices do not compromise worker safety'
Conventional demolition techniques should be employed for all painted surfaces with the Contractor complying with applicable OSHA and CaVOSHA statutes regardirg:
o Worker a'lvareness training;
o Exposure monitoring, as needed;
. Medical examinations, including blood lead level testing; and o Establishing a written respiratory protection program.
5.4 Lead Contaminated Soils & Bulk Analvses
In addition to the )CRF sampling, SCA collected bulk samples of the brick and concrete with brick aggregate substrates to verifi the potential lãad content of the masonry. Both samples found negligible lead concentrations at
1.6 and 8.3 ppm, resPectivelY.
Surface soils were found to have a total threshold lead concentration of 3,100 and 830 ppm, respectively' The eastern garden sample has an elevated lead concentration exceeding the CaVEPA Title 22 standards, classiffing it as a hazardous waste. Both samples were above the EPA and HUD standard of 400 ppm for children play ateas, indicating that some remediation of drip line soils will be necessary'
Ãeirai'CettÉouse Citadel Level, Golden Gate Natioñal Recreational Area, San Francisco, CA paae 12
6.0 Limitations and Exclusions
SCA warrants that this survey was perforned using due care and state of the art techniques. Beyond this, SCA does
,o-.y. Despite
- identified' or ideniified.
-Thi construction materials, and/or
This document is not a stand-alone document; abatement of materials is recommendçd to be completed under the oversight and design of an AHERA-accredited project Designer and certified Asbestos consultant' Although due care is exercised in the course of the survey, conðealed mãterials may be found in the course of perfonrring the abatement or demolition; a contingency buáget should be included in any cost estimates to cover unexpected conditions.
Note that SCA survey was not a comprehensive survey of the entire site and was limited to the areas designated by
WfS fo, planned ,"pãitr. Areas with similar materiaÍs and appearances not otherwise surveyed shall be treated in kind.
Ãlcatra= ôeltirouse citadel Level, Golden Gate Nat¡onal Recreational Area, san Francisco, cA
SCA Proiect No.: 8-9873
Attachment 1
Laboratory Results - Asbestos
Ãlcatraz'cellhouse Citadel Level, Golden Gate National Recreational Area, San Franc¡sco' cA
SCA Proiect No.: 8-9873
Attachment 2
Representative Lead-Based Paint XR-F Sampling Results
8-9873.AS XRF Results
REPRESENTATIVE SAMPLING OF LEAD-BASED PAINTS
ALCATRAZ CITADEL LEVEL SURVEY, SAN FRANCISCO' CÄ
SAMPLED BI' SCA ENVIRONMENTAL,INC. ON 1]^n6,20l0,cAl, INC. ON 1216/2002 & RGA ON 2/5i2003
SCA PROJECT NO.: B-9873'AS
Location Floor Condition
WH-O1 I 1|r6120t0 East Moat Citadel White Wall Brick 0.20 No Intact wH-O1 2 tv76l2010 East Moat citadel White Wal1 Brick 0.02 No Intact
BK-02 I tu76l20).0 East Moat Citadel Black Beam Steel 0.10 No Chipped & Rustv wH-O1 3 1111612010 Central Corridor Citadel White Inhll Plaster 0.40 No Intact
GR-03 1 tvr6l20t0 Cell Citadel Green Door Frame Wood >5.00 Yes lntact wH-O1 4 t!r612010 Central Corridor Citadel White Beam Concrete <0.01 No Spalling
BL-04 1 rU16l20r0 Cell Citadel Blue Door Frame Wood >5.00 Yes Intact
PK-05 I rUt6l20 0 Central Corridor Citadel Pink V/all Plaster 0.24 No lntact wH-O1 5 rrlt6l20 0 Cell Citadel White Pipe Cast Iron 0.50 No Intact wH-01 6 rvt6/20 0 Cell Citadel White Firenlace Brick t.20 Yes Peeline wH-01 7 tU16l20 0 Cell Citadel White Wall Plaster >5.00 Yes lntact v/H-O1 8 tUr6l20 0 North Moat Citadel White V/all Brick <0.01 No Intact wH-O1 9 tUr6l20 0 North Moat citadel V/hite Beam Concrete <0.01 No Spalling
RD-O6 1 rvt6l20 o West Moat Citadel Red Floor Brick <0.01 No Intact wH-O1 l0 tUt6l20 0 West Moat Citadel White Wall Brick 0.04 No Intact
SI-07 I r1lt6120 0 'West Moat Citadel Silver Door Metal 0.04 No Peeling
RD-06 2 ry16l20 0 WestMoat Citadel Red Wall Brick 0.02 No Intact wH-01 11 111t6120 0 Cell Citadel White Ceiline Brick 0.02 No Intact wH-O1 l2 rIr6120 0 West Moat Citadel White Beam Concrete <0.01 No Spalling
BK-02 2 tUr6120 0 South Moat Citadel Black Pipe Cast Iron 0.02 No Intact
RD-06 J tU16l20 0 South Moat Citadel Red Wall Brick 0.01 No Intact
GY-08 I tur6l20 0 East Moat Citadel Grav Door Metal 0.02 No Peelins
BK-02 .) 7t/r612010 South Moat Citadel Black Beam Steel 0.0r No Chipped & Rustv
Page 1 of4
8-9873.4S XRF Results
REPRESENTATIVE SAMPLING OF LEAD-BASED PAINTS
ALCATRAZ CITADEL LEVEL SURVEY, SAN FRANCISCO, CA
SAMPLED BY SCA ENVIRONMENTAL,INC. ON IIIIúI2OIO,CAL INC. ON 12i6l2002 & RGA ON 2i5l2003
SCA PROJECT NO.: B-9873.4S
Floor ov/-O9 I rvr6l2010 Cell Citadel Off-V/hite Arch Plaster 0.02 No Peeling
V/H- OlPC
121612002 Sheer Wall A Citadel White Wall Brick 480 No Not Listed wH-
O2PC
t21612002 Shear Wall B Citadel White Wall Plaster 160 No Not Listed wH-
O3PC
12t6t2002 Main Corridor
Citadel White 3rd Column Concrete 9800 Yes Not Listed wH-
O4PC
t2t6t2002 Shear'Wall F East Side citadel White Wall Plaster 690 No Not Listed
V/H-
O5PC
121612002 V/est End Citadel White Column 6 Concrete <100 No Not Listed
150052 21512003 West End citadel White North Face
Column I Concrete 93 No Not Listed
1s0069 2tst2003 'West End Citadel White West Face Column 4
Concrete 369 No Not Listed
I 50053 21512003 Central Cell Citadel White South Face Column l0
Concrete 255 No Not Listed
I 50057 21512003 Central Corridor Citadel White West Face
Column 12
Concrete <93 No Not Listed
I 5 0070 2ts/2003 Central Cell Citadel White East Face Column 13
Concrete 985 No Not Listed r50068 2tst2003 Central Corridor Citadel White East Face Column 7
Concrete <98 No Not Listed
150051 2t512003 Shear Wall A East End
Citadel Tan Watl @ Footing
Brick 652875 Yes Not Listed r50067 21s12003 East End Cell Shear Wall B
Citadel White North Face Wall Ø Footins
Brick r80 No Not Listed
150061 2/s12003 Central Cell Shear
V/all C
Citadel White North Face Wall Ø Footins
Brick 103 No Not Listed
8-9873.AS XRF Results
REPRESENTATTVE SAMPLING OF LEAD-BASED PAINTS
ALCATRAZ CITADEL LEVEL SURVEY, SAN F'RANCISCO' CA
SAMPLED BI. SCA ENVTRONMENTAL, rNC. ON lln6t20t0,c.Al. rNC. ON 1216/2002 8¿ RGA ON 2/5/2003
SCA PROJECT NO.: B-9873.4S
Date Condition
15006s 2tst2003 Central Cell Shear Wall D
Citadel White West Face Wall @ Footine
Brick 214181 Yes Not Listed
150054 2/5/2003 Central Cell Shear Wall E
Citadel Blue South Face
Column at Shear Wall tr'ootins
Concrete 233505 Yes Not Listed
150064 2/512003 West End Cell Shear Wall F
Citadel V/hite West Face @ V/all
Brick 118 No Not Listed
A 21s12003 Shear Wall B @ Column 20
Citadel Column Debris Concrete 49 No Debris
B 2ts12003 Soil at Shear'Wall
@ Column 20
Citadel Soil Debris Soil 10 No Debris
C 21s12003 Shear Wall B @ Column 20
Footins
Citadel Oxidized Rebar Metal 48 No Debris
D 2tst2003 Shear Wall B fDl Cohrmn 20
Citadel Chimney Brick 21234 Yes Debris
E 2t5t2003 West End Column L
Citadel Dust & Debris
1020 Yes Debris
F 21512003 Collector Beam Gridline B
Citadel Concrete Debris <8 No Not Listed
* HUD definition for Lead-Based Paints is >1.0 mglctr; or>O.SYo lead by weight.
Note: paints and glazing with a detectable lead content are subject to the Contractor's conrpliance with cavosHA regulation 8 ccR 1532.1during demolition, scraping
REPR.ESENTATIVE SAMPLING OF LDAD-BASED PAINTS
ALCATRAZCITADELLEVELstIRvEY,SANTRA¡tcISco'cA SAMPLED BY SCA ENVIRONMENTAL,INC. ON 11/16/2010'Ci{L INC' ON 121612002 & RGA ON 2/5/2003
SCA PROJECT NO.: B-9873'AS
@Labatementpriorto torching or cùttiig, ete'
Figures in bold represent lead-based paints (tBP) per HLID definition'
B-9873.4S XRF Results
Aìcafaz cellhouse citadel r_"u"i, ôãl¿"n Gate National Recreational Area, san Francisco, cA
Attachment 3
Soil Sampling Results
1534 WillowPass Road' Pittsburg, CA 94565-1701
Web: ww mccampbell com E-mail: main@mccampbell'comMcCampbell Analvtical. Inc.
SCA Enviromental, lnc.
334 19th Street
Oakland, CA 94612
Client Project ID: #8-9873.4S; Alcatraz Citadel Date Sampled: 11116110
DateReceived: 11116110
Client Contact: Glenn Cass DateReported: 1Il17ll0
Client P.O.: DateCompleted: lll17l10
'WorkOrder: 1011474
November 17,2010
Dear Glenn:
Enclosed within are:
1) The results of the 4 analyzedsamples from your project: #B-9873'AS; Alcatraz citadel'
2) A QC rePort for the above samPles,
3) A copY ofthe chain ofcustodY, and
4) An invoice for anal¡ical services'
All analyses were completed satisfactorily and all QC samples v/ere found to be within our control limits'
Ifyouhaveanyquestionsorconcerns,pleasefeelfreetogivemeacall' Thankyouforchoosing
McCampbell Analytícal Laboratories for your analytical needs'
Best regards, J,0"_ AngelaRydelius Laboratory Manager
McCampbell AnalYtical, Inc.
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McCampbell Analytical, Inc.
1534 Willow Pass Rd
Pittsburg, CA 94565-1701
(92s) 2s2-9262
Report to:
Glenn Cass SCA Enviromental, lnc.
334 19th Street Oakland, CA 94612
(510) 645-6200 FAX (510) 83s-620
G HAIII.O Í.GUSTO IIY R TG O RII Page I of I
IWaterTrax !WriteOn
Email: gcass@sca-enviro.com cc:
PO:
ProjectNo: #B-9873.AS: Alcatraz Citadel
WorkOrder: l0ll474
!EDF flExcel nFat IEmail
Bill to:
Accounts Payable SCA Enviromental, lnc.
334 19th Street Oakland, CA94612
ClientCode: SCAO
! HardCopy ! ThirdParty
Requested TAT:
Døle Received:
Date PrÍnted:
flJ-flas
1 day
LL/1612010
rt/16/2010
Requested Tests (See leqend be
1011474-001 clT-BRlcK- 102-1 Sod 11t16t2010 A 1011474-002 ctT-coNc - 104-1 Sod 11t16t2010 A 10't 1474-003 Soil-SW-2 (O Librarv So 1M6t2010 n A 1011474-OO4 Soil-W6-Eäst Soil 11t16t2010 A
Lab lD
Test Leqend:mm
24hrRUSH
Glient lD Collection Date Hold m m mm mm m t0
Prepared by: Shino Hamilton
NOTE: So¡l samples are discarded 60 days after results are reported unless other arrangements are made (Water samples are 30 days).
Hazardous samples will be returned to client or d¡sposed of at client expense.
Comments:
1534 WillowP¿ss Road, Pittsburg, CA 94565-1701 'Web:w.mccampbell.com E-mail: main@mccampbell.comMcCampbell Analvtical. Inc.
Client Name: SCA Enviromental' lnc.
Project Name: #B-9873.4S; Alcatraz Citadel
Workorder N": 101'1474 Matrix s¿!lþ!j!
Chain of custodY Present?
Chain of custody signed when relinquished and received?
Chain of custody agrees with sample labels?
Sample lDs noted bY Client on COC?
Date and Time of collection noted by Client on COC?
Sampler's name noted on COC?
Custody seals intact on shipping container/cooler?
Shipping container/cooler in good condition?
Samples in proper containers/bottles?
Sample containers intact?
Sufficient sample volume for indicated test?
All samples received within holding time?
Container/Temp Blank temperature
Water - VOA vials have zero headspace / no bubbles?
Sample labels checked for correct preservation?
Metal - pH acceptable upon receipt (pH<2)?
Samples Received on lce?
Sample Receipt Checklist
Chain of Custodv ICOCI lnformation
Date and Time Received: 1'11161201O 6:58:18 PM
Checklist completed and reviewed by: Shino Hamilton
Carrier: Derik Cartan (MAl Courier)
Samole ReceiPt lnformation
Yes ø
Yes ø
Yes Ú Yes ø
Yes E
Yes n
Yes n Yes M
Yes ø
Yes ø
Yes ø
Yes ¡
Yes ø Yes !
Yes ø
No!
No!
Nlo ¡
No!
Non
Noø
No¡ N¡o !
N¡o !
No!
No¡ l.lAø
Sample Preservation and Hold Time (HT) lnformation
Yes ø No!
Cooler Temp: 6.6"C l.lA!
No n No voA vials submitted Ø
No!
No!
N¡o n l.lAø
(lce TYPe: WET ICE
. NOTE: If the "No" box is checked, see comments below.
Date contacted: Contacted by:
Client contacted:
Comments:
McCampbell Analvtical. Inc.
"When Oualiv Counts"
1534 Vr'illow Pass Road, Pittsburg, CA 94565-1701
Web: w.mccampbell.com E-mail: main@nccampbell'com
Telenhone: 817-252-9262 Fax:925-252-9269 ;
SCA Enviromental, Inc.
334 19th Street
Oakland, CA94612
Client Project ID: #B-9873.4S; lJcatraz
Citadel
Date Sampled: 11116110
DateReceived: 11116ll0
Client Contact: Glenn Cass DateExtracted: 71116170
ClientP.O.: DateAnalyzed: l1/l1ll0
Extractionmethod: SW3050B
Læad by ICP-MS*
Analyticalmethods: SW6020 Work Ordec 1011474
Lab ID Client ID Mat¡ix KtractioD TYP( Lead DF %SS Comments
101 1474-0014 CIT-BRICK. I02-1 S TOTAL t6 123 t01t474-002¡^ CIT-CONC - 104-1 S TOTAL 83 t21 t0t1474-003/. Soil-SW-2 @Library S TOTAL 830 100 73 r0r1474-004¡. Soi1,W6-East S TOTAL 3 100 100 75
Reporting Limit fo¡ DF = 1 ;
ND means not detected at or w TOTAL NA velL
S TOTAL 05 mgKs all TCLP I STLC /DISTLC / SPLP extracts are reported in mg/L'
Iter'
# means suÍogate diluted out of range; ND means not detected above the reporting limilmethod detection limit; N/A means not applicable to this sample or instrument'
TOTAL = Hot acid digestion of a representative sample aiiquot'
TRM = Total recoverabÌe metals is the "direct analysis" ofa sample aliquot taken from its acid-preserved container'
DISS = Dissolved metals by direct analysis of 0.45 pm hltered and acidified sample.
%SS = Percent Recovery of Surrogate Standard
DF = Dilution Factor
DHS ELAP Cetifrcatíon | 644 4 *r.la Rydelius, Lab Manager
1534 Willow Pass Road, Piltsburg, CA 945ó5'1701
Web: w mccampbell.com E-mail: main@mccampbell'corn
:8'l'l-252-9262 Fax:925' McCampbell Analvtical. Inc.
QC SUMMARY REPORT FOR SW602o
EPA Method SW6020 Extraction SW3050B BatchlD: 5¿1474 Spiked Sample lD: 1011453-0024
Analyte Sample Spiked MS MSD MS.MSD Spiked LCS LCSD LCS.LCSD Acceptance Criteria (%) mg/Kg mg/Kg % Rec. % Rec. % RPD mg/Kg % Rec. % Rec. % RPD MS / MSD RPD LCS/LCSD RPD
Lead l8 50 113 99.7 o<? l0 ltl r08 2.46 75 t25 20 75 t25 20
ToSS: t02 250 109 101 8.30 250 118 r16 202 70- 130 ¿ll 70 - 130 20 I
All target compounds in the Method Blank of this ext¡actioû batch were ND less than the method RL with the following exceptions:
NONE
W.O. SamPle Matrix: Soil/Solid QC Matrix: Soil
BATCH 54474 SUMMARY
Date Analyzed Lab lD
WorkOrder 1011474
Date Sampled Date Extracted Date Analyzed
¿p
Date Sampled Date Extracted rOt1474-002A 11/16110 ll/16/10 1llr7l10 12:45 PM
4'14-004A 11'116110 11116110 1111'7/10 12:56t01 1474-0014 lllI6ll0 11116110 11/t'7/10 12:40 PM
1474-OO3A ltlr6/10 trll6/10 llll'7 110 12:50 PM plicate; RPD = Relative Percent Deviâi¡on'
% Recovery = 100. (Ms-sample)/ (AmountSpiked); RPD = 100'(MS' MSD) / (MS + MsD) /2)'
MS / MSD spike recoveries and / or %RpD may fall outside of laboratory acceptance criteria due to one or more of the following reasons: a) the sample is inhomogenous AND contains significant concentrat¡ons of analyte relative to the amount spiked, or b) the spiked semple's mâtrix interferes with the spike recovery'
N/A = not applicâble to this method.
NR=analyteconcentrationi ^.
DHS ELAP Certification 1644 QA/QC Officer
Rlcairaz'Cellhouse Citadel Level, Golden Gate Natioñal Recreational Area, San Francisco, CA
SCA Proiect No.: 8-9873
Attachment 4:
Field Data Sheets
SCA Environmental, lnc.
Asb Material/Sampling
Data Sheet
BLDG NAME:
BLDG NO:
DEPT CODE:
1. Aircell Type 2. Block
BoardTlpe 4.PaperV'lraP Loose Fill 6 Trowelled On
Mud Type L Sprayed On
Wool Felt 10 Beneath ACN¡
11. Mult Layers l2.ChunldPowder
Material Comments le lD (include BLÐG
Functional SpaceAllowed: blank, numbeieach comment and reference aboveCornments:
Updated 9-1 1-06 MSDS & FSDS_Asb & Pb_vert
Alcafaz'Cellhouse C¡tadel Level, Golden Gate Nat¡onâl Recreational Area, San Francisco' CA
SCA Proiect No.: 8-9873
Attachment 5
Sampling Location Drawings
? ??? 3?,??
llll- | - | I l-
PERIMFIER OF CITADEL
WATER CISTERNS. ACCESS
c o
¡f.. É|,?eEXTREM ELY LlMlrED.
lo4r.2()
94v*'tø"tt')
AIRS TO
MAIN
AREA
o-
USEABLE
Ct'l4oØftt?'
MAIN CELLBLOCK FOUNDATION
CITADEL LEVEL (MAIN CELLBLOCK AREA ABOVE)
TO
[A-L
\ND
IVER
)0M
TO
FIRST LEVEL OF
HOSPITAL WING.
ITECT IN PLACE.
) NOT USE FOR
ot4
HISTORIC STAIRS TO
FIRST LEVEL OF MAIN
CELLBLOCK AREA.
PROTEÇT IN PL,ACE."
Do NOÏ USE_DURING
CONSTRUCTION.
/'-i\ CITADEL LEVEL REFERENCE PI-AN I | \ -'
\{9/ Ö LEGEND:v
Ëi--'-- = ASBESTOS-CONTAININGMATERIAL(AcM) i-l' = NoN AsBESTos IIATERIAL (NoN'AcM) iinl = TRAcE (<1%) AsBEsros
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,l
@@@llt?
".'.1 o
3? 9??
16 0 16 32
SCALE OF FEÍ
SIAIRS NOÍ
^ USUBLEGr---
NOTES
ALL CONSTRUCTION SHOWN ON
THIS SHEÍ IS EXISTING
M CÍADEL LEVEL MASONRY
/'Î\ CITADEL LEVEL REFERENCE PLAN
LEGEND:
(+) = HUD.DEFINED LEAD-BASED PAINT (LBP)
(-) = LEAD-CONTAINING PAINT (LCP)
APPROXIMATE LOCATION
OF CISERN MNHOLE.y7.-7C) o$-01-t()HISTORIC STA1RS IO
FIRST LEVEL OF MÀN
CELT.BLOCK AREÀ
PROTrcT IN PUCE..
oo rdr use"ounrnö
CONSNUCTION
ako7.l n¡cnr¡ron v¡no -.--\
HoSPITAL WING (BASEMENT LEVEL)
Alcafaz'CellÉouse Citadel Level, Golden Gate National Recreational Area, San Francisco, CA
SCA Proiect No.: 8-9873
Attachment 6
Previous Asbestos Bulk Sampling Results
'|r / 65/'¿ø62 I 4: 54 t{ou O5 02 OS: l7a
/ô /44649ø6 Fl3ÞêsçÞÕh ì
ASBESTECFI
dt25 F¡ir Onts Blvd", Sulrc 103
Carmlchae[ CalifornÍa 9560t Tel.(916) 481-8902 Fax (9)6) 48t-t97s
CAL II.€
316^¡tEr-3975
PAGE ø6 p.2
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Summary Report for Asbestos and Lêad Paint Survey Alcafaz óellhouse Citadel Level, Golden Gate National Recreational Area, Sen Francisco, CA
SCA Proiect No.: 8-9873
Attachment 7
Previous Lead Bulk Sampling Results
L2/II/2øø2 11:34 7ø744649ø6 í cAt. il.c
Dæembcr 71,2002.
Bonita J, Mucller, RA.
Historical Arclitoct sfið, NE Menager N¿tioaal Pa¡t Sc¡'vice . Dsnverr S crvicc Center
72795W, AImú^Parkway ?.O. Box 25287 Drnver, CO 80228
Dea¡ Bonnio Muoller, I havo rocoived the lab…
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