Environmental Site Assessment Ph II
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PHASE n ENVIRONMENTAL
SITE ASSESSMENT
PROPOSED RITE AID PROPERTY, # 97-327
mGHW A Y 507 AND VANCIL ROAD
YELM, WASHINGTON
Copyright 1998 Kleinfelder, Inc.
All Rights Reserved
Unauthorized use or COpVU1g of thiS document IS strictI) prohibited. See "ApplicatlOll
For AuthorizatIOn To Use" located at the end of tlus document If use or copymg IS
desired by anyone other than our clIent and for the project Identified above.
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An emD!m'ee OHT.(-G compJny
January 15, 1998
Klemfelder Project Numbers 60-1742-04
Mr Kenneth Baldndge
Baldndge Development Group, L.L C
c/o Mulvanny Partnershtp Archttects P S
112 Fifth Avenue North
Seattle, Washtngton 98109
SUBJECT. Phase n Environmental Site Assessment
Proposed RIte Aid Property, # 97-327
Highway 507 and Vancil Road
Yelm, Washington
Dear Mr Baldndge
We are pleased to present this report of our Phase II EnVIronmental Site Assessment of the
subject property We trust the mformatlOn presented In thts report meets your needs at thiS time.
We appreciate tlus opporturuty to prOVide our servIces to you. Should you requIre additIonal
mformatIOn or have any questions regarding thts report, please contact us at (425) 562-4200
Smcerely,
KLEINFELDER, INe.
'12? (,--Lb7
Rory L. Galloway, RG
Seruer Project Manager
~ G~I~) ~ (i.~
Kristen L. Burgess
Project GeologIst
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Copyright 1998 Kleinfelder, Inc.
K LEI N F E L D E R 2-105 1-10th Avenue, NE, Suite Al 01, Bellevue, W A 98005 (425) 562-4200 (425) 562-4201 tJX
k.~ KLEINFElDER
A Report Prepared For-
Mr Kenneth Baldndge
Baldndge Development Group, L L C
112 Fifth Avenue North
c/o Mulvanny Partnershtp Archttects P S
Seattle, Waslungton 98109
PHASE IT ENVIRONMENTAL SITE ASSESSIVIENT
PROPOSED RITE AID PROPERTY, # 97-327
mGHW A Y 507 AND V ANC~ ROAD
YELM, WASHINGTON
Klemfelder Project Numbers 60-1742-04
Prepared By'
'fC., '7 L70.-C(-61-<);
Rory L Galloway, RG
Seruor Project Manager
J-~ bA-ft:w7
k~I3
Knsten L. Burgess
Project GeologIst
KLEINFELDER, INe.
2405 140lh Avenue NE
SUIte AlOl
BeIIevue, Washmgton 98005
Phone. (425) 562-4200
January 15, 1998
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TABLE OF CONTENTS
Page
1.0 S UMi\lAR Y ... -............................................................................... ........... ........... ............... ........................... 1
2.0 INTR 0 D U cn 0 N ................................. ...... ................................................................................................... 2
2.1 Purpose.
2.2 SpeCial Terrns and Conditions
2
2
3.0 SITE BACKGROUND AND ADDITIONAL REVIEW............................................................................... 2
4.0 SITE DES CRIPTIO N .................. ............................................................................................................ ..... ~
5.0 PHASE II SITE ASSESSMENT .-\.CTMTIES............................................................................................. 4
5 1 Identlfication of 55-Gallon Drums
5.2 Strataprobe Borings
5 3 Cherrucal Analysis.
4-
5
6
6.0 PHASE II OBSERV A nONS At'iD CHEl\HCAL Al~AL YTICAL RESULTS ..........................................6
6 1 Soil Analytical Results.
Petroleum Hydrocarbons Identlfication (WTPH-HCID)
Petroleum Hydrocarbons wrPH-D Extended
PolycWonnated Blphenols (PCBs) by Method 8080
Semi-Volatile Orgamc Compounds (VOCs) by EPA Method 8260
6.2 Groundwater Samples.
6
7
7
7
7
7
7 0 CON CL US I 0 ~-S ..... ......... ......... .................... ........ ...... ............ ........................................ ......... ...................... 7
8.0 RECOMMENDA nONS
............................................. .................................................... ...... 8
9 0 LlJ\IIT A TI 0 N S ......................... ............... ............. ........................................................ .............. .................. 9
10.0 QUALIFICATIONS OF E~'VIRONMENTAL PROFESSIONALS ...................................................... 10
PLA TES
PLATE 1:
PLATE 2:
SIte LocatIon Map
Site Plan and Bonng LocatIons
TABLES
TABLE 1:
Soil Samples - Cherrucal Analyses
APPENDICES
APPENDIX A
APPENDIX B
APPENDIX C
Site ExploratIon Methods and Quality Assurance! Quality Control
Analytical Results, Chromatographs, and Cham-of-Custody Forms
ApplicatIon for AuthonzatlOn to Use
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1.0 SUMMARY
At the request of Baldndge Development Group, L.L C (Baldndge), the RIte AId CorporatIon
(RIte Aid), and Mulvanny PartnershIp, Klemfelder has completed a Phase II EnvIronmental
SIte Assessment (ESA) for the subject property, located at the mtersectIon of Highway 507 and
Vancil Road m Yelm, Washmgton The SIte consIsts of three parcels and IS currently OCCUpIed
by a resIdence, church, a former antIque-dealer bUlldmg and several other structures
Klemfelder's Phase I ESA Idenufied several enVironmental concerns WhIch could have resulted
m the contammatIOn of subsurface SOlis and/or groundwater at the subJect property
Klemfelder IdentIfied one WashIngton Confirmed & Suspected Contanunated (C&SCS) SIte
wIthm 1 0 mIle of the subJect property We also identIfied possible hazardous matenal use,
storage, and handlmg on the subject property, Includmg the storage of numerous unlabeled
drums and cont:alners Furthermore, dunng our Phase II exploratIon, Klemfelder 1dentlfied the
two-story resIdence located on the south-end of the property IS a lIcensed auto repaIr shop
ThIS shop contalns an oil-water separator and other related contamInant sources GIven the
findmgs of the Phase I ESA and addItIOnal mtervIews dunng the Phase II exploratlon,
Klemfelder and subcontract personnel completed SIX Strataprobe bonngs on the subject
property on December 19, 1997 m the area of the repaIr shop
ChemIcal analytIcal results of SOlI samples collected from bonngs located to the south of the
auto repaIr shop revealed the presence of petroleum-related hydrocarbons m the subsurface
SOlIs, whIch exceeded the Washmgton State Department of Ecology's (Ecology) Model TOXICS
Control Act (MTCA) cleanup levels Chemical analytical results of analyzed soIl samples
collected from bonngs located m the VICInity of the drums dId not reveal the presence of
petroleum-related hydrocarbons, semI-volatIle organIC compounds, or polychlonnated
bIphenols (PCBs) exceedIng Ecology's MTCA cleanup levels Groundwater was not
encountered 10 any of the bonngs completed dunng our Phase II exploratIon
Kle10felder recommends the contamInated SOlI assOCIated WIth the auto rep31r shop be
excavated and properly dIsposed of 10 accordance WIth State regulatIOns Klemfelder also
recommends that the drums on the property be properly removed/dISposed, that the oll-water
separator be decommISSIOned, and any subsurface contammatlOn related to the auto repaIr shop
be addressed. ConSIderatIon also should be gIven to the decommiSSIOning of the Identified
septiC systems on the site. Klemfelder recommends thIS work scope be prepared WIth the
assistance of Baldndge and RIte AId upon completion of reVIew of thIS report. Klemfelder can
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prepare a specIfic scope of work at that tIme. Furthermore, as wIth the development of any
site, If a prevlously-umdentIfied environmental condltlon IS encountered dunng sIte work,
these envIronmental issues should be evaluated at that tlme.
2.0 INTRODUCTION
Klemfelder's Phase II work summanzed m thIS report was mtended to explore for the possible
presence SOlI and/or groundwater contammation resultmg from on-sIte and possibly off-SIte
practIces Identlfied m our Phase I EnvIronmental SIte Assessment (ESA) as detaIled m SectIon
3 0 of thIS report. The results of our SIte exploratIOn are presented m thIS report and are
subject to the hmItatlons presented m SectIOn 9 0
2.1 Purpose
Klemfelder understands that Baldndge and Rite AId are Interested m obtaImng data regardIng
subsurface condItIOns at the SIte, as well as Klemfelder's conclusIOns and recommendatIOns
regardmg subsurface contammatlOn, If any ThIS report describes Klemfelder's assessment
procedures and the mformatlOn IdentIfied Fmdmgs, concluSIOns, and recommendatIOns
concermng potentJ.al SOlI and/or groundwater contammatIOn are presented In SectIOns 7 0 and
8 0 of thIS report.
2.2 Special Terms and Conditions
ThIS report IS mtended for use by Baldndge and Rite AId Any party other than Baldndge or
Rite Aid who WIshes to use thIS report to Identify recogmzed enVIronmental condItIOns In the
process of makmg appropnate mqUIry Into the SIte or surroundmg propertIes shall notIfy
Klemfelder by executlng the "ApphcatJ.on for Authonzatlon to Use" whIch follows thIS
document. Based on the mtended use of the report, Klemfelder may reqUIre that addItJ.onal
work be performed and that an updated report be ISSUed. Non-complIance WIth any of these
requirements will release KleInfelder from any lIab1hty resultmg from the use of thIS report by
any unauthonzed party
3 0 SITE BACKGROUND AND ADDITIONAL REVIE\V
Klemfelder completed a Phase I ESA for the subject property on October 9, 1997 Our
assessment revealed several envIronmental concerns, whIch could have resulted In the
contanunatlon of subsurface soils and/or groundwater at the subJect property Possible
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hazardous matenal use, storage, and handlmg on the subject property were IdentIfied dunng
Klemfelder's assessment. ThIS mcluded storage of both empty drums and containers, as well as
drums and contaIners wIth unknown contents Our record reVIew revealed one potentIal
enVIronmental concern resultmg from an off-site c&SCS sIte withm the ASTM-reqUlred
search dIstance
To determme the possible Impacts from the storage of umdent1fied 55-gallon drums and other
containers, a representatIve from Klemfelder conducted several mtervIews WIth current
property owners as well as current and prevIOUS tenants of the subject property Accordmg to
Mr Lyod RIchel, the current owner of the antIque store and the two-story resIdence, no
hazardous matenals have been generated or stored on the subJect property We mtervIewed
Ms SteffanIe Ray, the prevIous tenant and operator of the antIque-dealer shop Accordmg to
Ms Ray, the five plastIC drums located to the south-west of the shop are filled WIth water or
chIcken feed Mr RIchel and Ms Ray stated that these drums have not been used for the
storage of any hazardous substances Ms Ray also stated that they dId not recondItIOn,
refirush, or stnp (remove pamt or surface finshes) any of the antIques sold on the property
Ms Ray explaIned that she bought and sold a small volume of antIques at the subject property
for approxImately five years before she closed the bUSiness
We also mtervIewed Mr Bruce Thomas, the current tenant and owner of a lIcensed auto repaIr
shop located m the garage of the two-story home at the south-end of the subject property
Accordmg to Mr Thomas, the Department of Health mandated that the part-tIme auto repau
bUSIness (WhICh operated In the garage) be lIcensed, and the work space be brought up to code
ThIS entaIled pounng a reinforced concrete floor within the garage and InstallIng an oil-water
separator at the entrance of the garage The waste water from the auto shop flows to the east
VIa concrete pIpes and collects m the oil-water separator The water reportedly IS dIscharged
mto the soil to the south of the OIl-water separator vIa a 30 foot concrete pIpe Mr Thomas
stated that he has operated thIS shop for the past five to ten years on a part-tIme baSIS, and that
he Just performs tune-ups Mr Thomas does perform 011 changes for hIS own vehIcles on the
subject property and stores the resultmg waste-oil In a steel 55-gallon drum located outSIde at
the west-end of the shop Mr Thomas stated that the full drums are taken to a local servIce
statIon for dISposal and not dISpOSed on the property
Mr Thomas pomted out two areas of enVIronmental concern where auto fuels or lubncants
were accidentally released mto the soils. A hydraulIc oil spIll had occurred along the south
SIde of the garage (plate 2) Mr Thomas IdentIfied another spill that had occurred in the
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vIcmity of the stored waste-OIl drums along the west sIde of the auto reparr shop approxImately
one year ago (plate 2) Accordmg to Mr Thomas, a small drum of engme-cleamng solvents
had spIlled onto the SOlis m thIS area. Mr Thomas proceeded to clean the saturated soils by
excavatlng them WIth a shovel and placmg the SOlI in a 55-gallon drum The 55-gallon drum
contalmng the contammated soil IS located along the west-end of the shop behmd a storage
shed.
Based on the findmgs of our Phase I ESA and the results of the addItlonal Phase II mtervIews,
Klemfelder performed a subsurface exploratlOn program to explore whether SOlis and/or
groundwater at the subject property have been Impacted by the on-SIte practlces m the
Identlfied areas of concern
4.0 SITE DESCRIPTION
The subject property IS located at the southwest comer of the mtersectlOn of State HIghway
507 (Bald Hill Road SE) and SE Vancil Road (plate 1) The sIte conSIsts of three parcels and
IS currently OCCUpIed by a reSIdence, church, a former antIque-dealer bUIldmg and several
small storage sheds (plate 2) The SIte IS bounded to the north by State Highway 507, to the
east by SE Vancil Road, to the south an west by pnvate reSIdences
The local topography IS charactenzed by generally flat-Iymg valley alluvlUm (Quaternary non-
glaCIal secilments) Groundwater IS expected to be w1thm 20 feet of the ground surface and
lIkely flows approxImately north to north-east, toward the Nisqually River
5.0 PHASE n SITE ASSESSMENT ACTIVITIES
ThIS sectlOn discusses site exploratlOn work performed at thiS sIte. An explanatIOn of field
sampling methods IS presented m AppendiX A QUalIty assurance and qualIty control methods
are also mcluded m AppendiX A Plate 2 presents a schematIC site plan and Strataprobe bonng
locatlons
5.1 Identification of 55-Gallon Drums
Twenty five 55-gallon steel drums were stockpIled on the south SIde of the auto repaIr shop.
Each drum was opened by a Klemfelder geolOgISt. All twenty five drums were empty at the
tIme of our mspectlOn, Based on the labehng and odors from the drums, each drum contalned
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a specIfic flavored essentIal oil such as cmnamon, peppermmt, wmtergreen, amse, and
spearmint. The drums were collected from I P call1son m chehalIs, Washmgton The drums
are cleaned out and sold by Mr Thomas as water storage One 55-gallon drum stored along
the west SIde of the auto repaJr shop contamed contammated SOlI, and one 55-gallon drum
contained waste-oil from auto-OIl changes as described in Sectlon 3 0 of thIS report. A small
drum of auto engme cleamng-solvent was also located along the west SIde of the auto repaJr
shop
Five 55-gallon plastIC drums were stored along the south SIde of the shed assocIated WIth the
antlque dealer store Each drum was opened and as reported by Ms Ray, each drum eIther
contamed chIcken feed or water The drums were resealed and left on SIte The addItIOnal
plastlc drums Identlfied m our Phase I assessment located along the west Side of the antIque
dealer shop were not present dunng our Phase II exploratIOn, and could not be found
elsewhere on the SIte The area where the drums had been stored dId not show eVIdence of
dIstressed vegetatlon or ObVIOUS SIgns of SOlI staJ.mng The 5-gallon buckets and other
contaJ.ners IdentIfied In our Phase I assessment were not present on the subject property at the
tlme of our Phase II exploratIon No other drums than those descnbed were Inspected dunng
our Phase II exploratIon
5.2 Strataprobe Borings
In accordance WIth the reVIsed scope of work requested by our clIent, SIX Strataprobe bonngs
were completed on the subJect property on December 19, 1997 Bonng locatIOns were ad] usted
from those ongmally proposed, based on representatIons by SIte tenants that hazardous
matenal had not been used 10 the area of the antIque store, but were present m the auto repaIr
area. GIven the cl1ent-authonzed scope of work, the bonngs were placed m the area Identified
to have the hIghest potentIal SubstantIve soil contammatIOn whIch IS the auto repaJr operatIon
Three bonngs (B-1 through B-3) wereJocated m the vIcm1ty of the oil-water separator at the
entrance of the auto repaJr garage One bonng (B-4) was located m the VICInIty of an 011 spIll
south of the auto repaJr shop as IdentIfied by Mr Bruce Thomas Two bonngs (B-5 and B-6)
were located m the VICInIty of the stockpiled 55-gallon drums to the south of the auto repaIr
shop Due to the presence of a septIc tank and asSOCIated dram field, a bonng could not be
located m the vIc1mty of the engme-cleanmg solvent spill IdentIfied by Mr Thomas (dnvmg
the drillIng ng over the dram field would have caused damage to the buned draIn hnes )
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5.3 Chemical Analysis
DUTIng the Strataprobe work, soil samples were collected at three-foot mtervals for sod
identIficahon and possible chemIcal analYSIS Samples were collected dIrectly from the
Strataprobe split spoon sampler and screened for volatIle organIC compounds (VOCs) usmg a
photOlomzatIOn detector (PID) A total of nIne SOli samples collected from the bOTIngs (B-1
through B-6) were submItted to the analytIcal laboratory for chemIcal analYSIS unIque to each
bonng, mcludmg hydrocarbon IdentIficatIOn analysIs usmg the Ecology speCIfied Method
WTPH-HcID, dIesel-range hydrocarbons by Ecology speCIfied Method WTPH-D and WTPH-
D extended, PolychloTInated BIphenols (PCBs) by Ecology SpeCIfied Method 8080, VolatIle
OrganIC Compounds (VQCs) by the EnVIronmental ProtectIOn Agency (EPA) specIfied
Method 8260 The results of these analyses are presented m SectIon 6 1 of thIS report.
6.0 PHASE II OBSERVATIONS Al'll) CHEI\HCAL ANALYTICAL RESULTS
Based on the SIX bOTIngs, geology at the SIte IS charactenzed by five to SIX feet of lIght brown
Silty fine sand WIth gravel. ThIS sand IS underlaIn by four to five feet of broWnIsh-grey fine to
medIUm sand WIth silt and gravel Groundwater was not encountered In the Strataprobe bonngs
(explored to a maximum depth of 17 feet below ground surface) dUTIng our Phase II
exploratIOn
Klemfelder VIsually observed the SOlI samples collected at the SIte for any obVIOUS SIgns of
petroleum-related contammatIon Based on our field screenmg results, representatIve soIl
samples were selected from each bOTIng for chemIcal analysIs SOlI stammg and elevated prD
reading were recorded from bonng B-4 Elevated PID readmgs detected dunng the course of
our work md1cated the presence of volatIle organic compounds m the VICInIty of an IdentIfied
oil spill on the south SIde of the reSIdence Strataprobe bOTIng locatIons are presented on Plate
2
6.1 Soil Anal)tical Results
Klemfelder submItted SOlI samples from each of the bOTIngs to a Washmgton State CertIfied
Laboratory, Fnedman and Bruya. The analytIcal laboratory reports and chromatographs for the
analyzed soil samples are attached as AppendIX B of thIS report. ChaIn-of custody forms are
also included In AppendIX B. Table 1 presents the results of the chemIcal analyses for the
submItted soil samples
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The results of the nine analyzed soil samples are summanzed as follows
Petroleum Hydrocarbons Identification (WTPH-HCID):
Klemfelder submItted the followmg SOlI samples for hydrocarbon idenb.ficatlOn analYSIS, (B-l-
2, B-2-2, B-3-3, B-5-3) Petroleum-related hydrocarbons were not detected m any of the SOlI
samples analyzed by thIS method
Petroleum Hydrocarbons WTPH-D Extended
Four SOli samples (B-4-1, B-4-4, B-6-2, and B-6-3) were sub nutted for-hydrocarbon analYSIS
quanufied as diesel DIesel-range hydrocarbons were detected In SOlI sample B-4-1 (depth of 3
feet) at a concentratIon of 14,000 mg/kg, exceedmg MTCA cleanup levels of 200 mg/kg
Diesel-range hydrocarbons were detected In soil sample B-4-4 (depth of 12 feet) at a
concentrauon of 90 mg/kg, below the MTcA cleanup levels Delsel-range hydrocarbons were
not detected In sou samples B-6-2 and B-6-3
Polychlorinated Biphenols (PCBs) by Method 8080
One soil sample (B-4-1) was sub mI tted for PCB analysis PCBs were not detected In 5011
sample B-4-1
Semi- Volatile Organic Compounds (Yoes) by EPA Method 8260
Two SOlI samples (B-1-2 and B-3-2) were submItted for VOc analysIs VOCs were not
detected m either of the SOli samples submItted
6.2 Groundwater Samples
Groundwater was not encountered In the SOli bonng completed dunng our Phase II
mvesb.gatIOn, therefore, Klelnfelder did not submit groundwater samples for chemIcal analysIs
7.0 CONCLUSIONS
The followmg conclUSIOns are based on Klemfelder's knowledge of the subJect property from
our Site observatlons, InformatIOn gathered dunng our reVIew, and sample analyses. These
conclUSIOns are subject to the hmltatIons presented at the end of thIS report, and may change If
additIonal mformatIon becomes aVaIlable.
. Our Phase II findmgs, indicate that petroleum-related soil contanunatlon IS present
at thts site due to the on-site actIVIties assOCiated WIth the lIcensed auto repair shop
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operated by a current tenant. In the one bOrIng location (B-4-1), contarrunatlOn
was found at a depth of 3 feet below ground surf~ce and may extend to a depth as
great as 10 feet below the ground surface
· The stockpiled 55-gallon drums located to the south of the auto repair shop, once
contamed essentIal oils such as spearmlnt and peppermmt. The drums are now
empty and do not represent an environmental concern to the subject property
However, two 55-gallon drums and one smaller drum do eXIst along the west Side
of the auto repair shop, whIch contaIn contamInated soils and waste-Oil.
· An oil-water separator eXIsts to the east of the auto repair shop and emptIes
directly mto the subsurface soils 30 feet to the south of the auto repair shop Soil
bonngs located m these areas did not reveal soil contarrunat10n, however, It IS
possible that some related contamInatIOn eXIsts due to the operatIOn of the oil-
water separator and dramfield.
· Soil contammatlOn may be present beneath the concrete slab of the garage/auto
repair shop, smce the facilIty was m operatIOn for several years pnor to pounng
the concrete slab
· The plastiC 55-gallon drums located m a shed to the south-west of the antique
dealer shop are filled WIth anImal feed and do not represent an environmental
concern to the subject property However, several drums that were Identified m
our Phase I ESA were removed from the sIte pnor to our site VISIt. We were,
therefore, unable to ascertaIn the contents of these drums
· A soil bonng was not completed In the VICInity of the antique dealer shop SInce the
owner of the shop, Mr RIchel and Ms Ray stated that they did not refimsh,
repamt, or stnp furruture m aSSOCiatIOn With the sellIng of antiques Furthermore,
we did not observe any IndicatIOns that these hazardous-matenal actiVities took
place on site m thts area of the property
8.0 RECOMNIENDA TIONS
Based on Klemfelder's current understanding of site condItIOns, the follOWing activItIes are
recommended
· Klemfelder recommends the petroleum-related contarrunated soil to the south of
the auto repair shop be properly excavated and removed from the site In
accordance With State regulatIOns pnor to site development.
· The 55-gallon drums filled WIth waste-oIl and contarrunated soils and the smaller
auto engine-solvent drum as well as any other contaIners w1thtn the auto repair
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shop must be removed from the site and properly disposed pnor to any site
development.
o Klemfelder also recommends that the od-water separator be properly
deconurusslOned and any associated contamInated soils be disposed of accordmg
to State regulatIons.
o A bonng should be located m the area Identified as the auto engIne-clearung
solvent spill, and soil samples should be collected to confirm the absence or
presence of contarrunants In thiS area.
· The concrete slab m the auto repair shop should be removed and the soIls beneath
the slab tested for petroleum and other possible subsurface contarrunatIOn.
o Pnor to site development, the eXlstmg septic tanks and dram fields assocIated With
the auto repair shop and the antique dealership should be removed and soil samples
collected to confirm the absence or presence contarrunants whtch may have been
released m the sub-surface soils.
· Klemfelder recommends, as With the development of any Site, If a prevlOusly-
urudent1fied environmental condition IS encountered dunng site work, these
enVIfonmental1ssues should be evaluated and addressed at that time
· Klemfelder recommends a site-remediatIOn work scope be prepared With the
assistance of Baldndge and Rlte A1d upon completIOn of review of thts report
Klemfelder can prepare a speCific scope of work at that time
9.0 LThUTATIONS
Phase II enVIronmental SIte assessments are non-comprehensIve by nature and are unlIkely to
IdentIfy all enVIronmental problems or elImmate all nsk. The attached report IS a qualitatIve
assessment. Klemfelder offers a range of investigative and engmeenng servIces to SUIt the
needs of our clIents, IncludIng more quantitatIve InvestigatIons. Although nsk can never be
el1minated, more detailed and extenSIve investigatIOns YIeld more mformatIon, whIch may help
you understand and better manage your nsks. Since such detaIled services Involve greater
expense, we ask our clIents to partICipate In IdentIfymg the level of service that Will proVide
them WIth an acceptable level of nsk. Please contact the sIgnatones of thIS report If you would
like to dISCUSS thIS Issue of nsk further
The scope of work on thIS project was presented In our Identified proposal and subsequently
approved by you as our clIent. Please be aware our scope of work was lImited to those Items
60-174204/6018ROO8
Copyright 1998 Kleinreld~r. Inc.
9 of 10
prinl~d. 01/15/98
III KlEINFElDER
specIfically Identlfied in the proposal. Environmental Issues not specIfically addressed m the
proposal or thIS report were beyond the scope of our work and not mcluded m our evaluatlon
Land use, site conditIons (both on-site and off-sIte) and other factors will change over tIme.
Smce SIte actIv1tles and regulatIons beyond our control could change at any tIme after the
completIon of thIs report, our observatIons, find10gs and opmIOns can be considered valId only
as of the date of the Site VISIt.
The property owner IS solely responsible for notIfY1Og all governmental agencIes, and the
publIc at large, of the eXistence, release, treatment or disposal of any hazardous matenals
observed at the proJect Site. Klemfelder assumes no responsibilIty or lIabilIty whatsoever for
any claIm, loss of property value, damage, or 10Jury WhiCh results from pre-exIstmg hazardous
matenals bemg encountered or present on the proJect Site, or from the dIscovery of such
hazardous matenals
Any party other than our clIent who would lIke to use thIS report shall notIfy Kle10felder of
such mtended use by executIng the" ApplIcatIOn for AuthonzatIon to Use" contamed 10 thIS
document. Based on the 10tended use of the report, Kle10felder may require that additIOnal
work be performed and that an updated report be Issued. Non-complIance With any of these
reqUIrements by our chent or anyone else will release Kle10felder from any hab1lIty result10g
from the use of thIs report by any unauthonzed party
No warranty, eIther express or ImplIed IS made
10.0 QUALIFICATIONS OF ENVIRONMENTAL PROFESSIONALS
Resumes of enVlfonmental professIOnals conduct1Og thIS environmental SIte assessment are on
file at the Klemfelder office and are aVaIlable upon request.
60-174204/6018ROO8
Copyright 1998 Kleinfelder, Inc.
10 of 10
printed: 01/15/98
Reference: USGS 15 mmute topographic quadrangle, Yelm. WA. 1959
HI---i
O'
t--1
4000'
'1t
-.-
APPROXIMATE SCALE
PROIECf NO 60-1766-04
Januarv 1998
SITE LOCATION l'v1AP
State Highway 507
& Vancil Road
Yelm, Washington
PLATE
KLEINFELDER
1
X
!
x
x
P.A. VED
LEGEND
~ DRUM STORAGE AREA
'-'-)<-'->("-"7<--' EXISTING FENCE
-+ SOIL BORING LOCATION
NOT TO SCALE
'>>Q
~4-
-<1)-
So
:>
PAVED
x
x
STORM
SEWER
/ ~
x
x
x
x
~ GRAVEL
x
PAVED"
x
x
x
x
ISHEDI
....15:1
X
REPORTED SOLVENT
SPILL AREA
ISHED I
x
POSSIBLE DRYWELL - 0
x
Cl
<:
o
0:::
PRESENT
OIL-WATER
EPARATOR
nd DRAINlINE
17.(2.P<4
~r
Planned Rite IUd store
VaneD Road 4: state HIghway 507
Velm, Wa&hlngtan
Project: 60-1742-01 1-14-98
SOIL BORING
LOCATIONS
GJ
TABLE 1
Soil Analytical Results
Date of Sample Collection: December 19, 1997
Proposed Rite Aid Site, Yclm, Washington
Sample Number 11-1-2 11-2-2 11-]-2 11-]-3 11-4-1 11-4-4 11-5-3 1l-6-2 1l-6-3 ;::.1]11
SalnD1e l)eolh (reel) 6 6 6 9 3 12 9 9 9
---~..TTT""'''''
==~,-~""'~~~
TPII C ::::::::::::::,::::::;::::.,:::,::::::::,::::::
........................
-I I ID ,:,:"/,:,:'":,:::;:::;:;::::,:",:":,,,,,,
..........".. .......
~~,,~JL ~~ ~~ ~~ ~_. ~~jL~",,~L,~,,=,,4\liI
ALL ANAL TIES NA NA NA NA ND NA NA NA NA if\::::,))!:::::.}:,
...........................,........'.......................'................................... ,...................... ........,.,...........................,...................... ..................................,.........,................................ ...... ............,............................... ......................... ..............
VOLATILE OHGANICS (8260)
ALL AN AL YTES
NO
NA
NO
NA
NA
NA
NA
NA
NA
NOTES
(1)
Refer to site diagram for sampling locations.
Method' A' Soil Cleanup Levels, MTCA, Amended Janunry 1996 Excecdances of thcse Icvels do not Ilccessnrily trigger
requirements for cleanup action under MTCA.
Concentration less than the Inboratory method detection limit
Not analyzed
NO
NA
6O-174204/6018nJ08
Copyright 1998 Klcinfclder Inc
Prinl<d: II U198
APPENDIX A
SITE EXPLORATION METHODS
Quality Assurance Quality Control
Qualtty Assurance/Quahty Control (QAlQc) for the presented scope of work mcluded generally
accepted procedures for sample collectIon, storage, trackmg, and documentatIOn. All sampling
eqUIpment was washed wIth a detergent wash and tap water nnse pnor to the collectIon of the
samples All samples were labeled wIth a sample number, date, ttme, and sampler name, and were
stored 10 an Ice chest contam1Og frozen "blue Ice" Appropnate cham-of-custody documentatIOn
was completed.
General
Klemfelder developed a health and safety plan for thts project pnor to the start of field work. The
health and safety plan mcluded speCificatIOns for steel toe boots, hard hats, safety glasses, and
protective clothtng. For the protectIOn of the crew, a photolOruzat10n detector (PID) was used to
screen for the presence of volatile orgaruc concentratIOns m the breathmg zone dUrIng the dnllmg
of the bonngs. The Pro was a Thermo EnVironmental Model 580B OVM, or eqUIvalent, WIth a
105 ev lamp The mstrument was calibrated to 100 parts per milhon by volume (ppmv) WIth an
1sobutylene gas standard. The Pro measures volatile orgaruc compounds (VOcs) 10 the aIr m
ppmv
Strataprobe Borings
Soil bonngs were drilled usmg a truck-mounted Strataprobe drillIng ng, provIded by our dnllmg
subcontractor A Klemfelder employee was present dunng the drilling and aSSisted 10 obtammg
samples of the subsurface matenals, mamtamed a log of the bonngs, made detailed observatIons
of sIte conditIOns, and provIded technIcal aSSistance, as reqUIred.
All drilling and samplmg eqUIpment was steam cleaned pnor to mobilIzatIOn and between bOrIngs
to reduce the potential for cross contarrunatlOn. In additIon, the samplmg eqUIpment was steam
cleaned between each sampltng mterval pnor to the collectIOn of the next sample
Strataprobe Soil Sampling
A strataprobe subcontractor will perform the "drillIng" at thts site The strataprobe used for thiS
work will conSISt of al 5-mch stamless steel sampler (sealed pIston sampler) Discrete or
contmuous soil samples will be obtamed by dnvmg thts sampler to depth, then operung to obtam a
soil core of 1 125 10ches diameter WIth an attempted soil recovery of 18 to 24 mches m length
Collected soil samples were evaluated for eVIdence of contarrunatlOn by VIsible discoloration of
the soil sample or VOCs detected by the Pro A portion of each soil sample was placed mto a
plastiC ZIp-lock bag, and the vapors were drawn through the Pro for qualItative screenmg of
VOCs. The vapor readmgs were documented as the field screerung results. A new plastIC bag
was used each ttme a sample was screened.
60-174204/60 18ROO8
Copyright 1998 K1~infelder. Ine.
A-I
printed: 01/15/98
Sample cores were labeled WIth a sample number, date, tIme, and sampler's name and stored m an
Ice chest contammg frozen "blue Ice." cham-of-custody procedures were followed to document
sample handlmg.
Upon collectIOn of the soil cores, the probe was extracted. The resultmg hole was closed
(matenals IdentIfied on the attached bonng logs) The extracted strataprobe rod was washed
between bonng locatIOns and new liners were be used between sampling locatIOns.
60-174204/6018ROOS
Copyright 1998 Kleinfe1der, Inc.
A-2
printed 01/15/98
FRIEDMAN & BRUY A, INC.
ENVIRONMENTAL CHEMISTS
James E. Bruya. Ph.D
Charlene Jensen, M.S.
Bradley T Benson, B.S
Kun Johnson, B.S.
3012 16th Avenue West
Seattle. WA 98119-2029
TEL. (206) 285-8282
FAX. (206) 283-5044
e-mail.fbi@isomedia.com
January 7, 1998
Knsten Burgess, Project Manager
Klemfelder, Inc.
2405 140th Avenue NE, SUlte A10 1
Bellevue,VVA 98005
Dear Ms Burgess
Included are the results from the testmg of matenal submItted on December 22,
1997 from your Yelm-fute AId proJect. Any samples that may remaln are currently
scheduled for chsposal ill 30 days If you would hke us to return your samples or
arrange for long term storage at our offices, please contact us as soon as possible
VV e appreCIate thIS opportumty to be of servIce to you and hope you will call If you
should have any questlOns.
Smcerely,
FRIED11AN & BRUYA, INC
==-~
Chenust
Enclosures
FAX: (425) 562-4201
KLE010'iR.DOC
FRIEDMAN & BRUY A, INC.
ENVIRONMENTAL CHEMISTS
Date of Report: 01/07/98
Date ReceIved.. 12/22/97
ProJect. Yelm-RIte AId
Date Extracted.. 12/23/97
Date Analyzed: 12/23/97
RESULTS FROM THE ANALYSIS OF SOIL SAMPLES
FOR GASOLINE, DIESEL AND HEAVY OIL BY \VTPH-HCID
Results Reported as Not Detected (ND) or Detected (D)
THE DATA PROVIDED BELOW WAS PERFORMED PER THE GUIDELINES ESTABLISHED BY
THE WASHINGTON DEPARTMENT OF ECOLOGY AND WERE NOT DESIGNED TO
PROVIDE INFORMATION WITH REGARDS TO THE ACTUAL IDENTIFICATION
OF Ml' MATERIAL PRESENT
Sample ill Gasohne DIesel Heavy Oil Surrogate
Laboratory ID (% Recovery)
B-1-2 ND ND ND 87
712092.01
B-2-2 ND ND ND 85
712092.03
B-3-3 ND ND ND 86
712092-05
B-5-3 ND ND ND 86
712092-12
Method Blank ND ND ND 100
ND - Matenal.not detected at or above 20 mg/kg gas, 50 mg/kg chesel and 100 mg/kg
heavy oil.
FRIEDMAN & BRUY A, INC.
ENVIRON11ENT AL CHEMISTS
AnalYS1S For Volatile Compounds By EP A Method 8260
Chent Sample ID B-1.2 Chent: Klemfelder
Date ReceIved. 12/22/97 ProJect: Yelm.RIte Ald
Date Extracted. 12124/97 Lab ID 712092.01
Date Analyzed. 12124/97 Data FIle. 122416.D
MatrL"( Soil Instrument: GCMS 1
Umts ug/g (ppm) Operator' YA
Lower Upper
Surrogates % Recovery LImIt Lmnt
Dibromofluoromethane 96 54 118
1,2- DIchloroethane-d4 95 62 119
Toluene-d8 72 61 120
4-Bromofluorobenzene 74 59 124
ConcentratIOn ConcentratIOn
Compounds. ug/g (ppm) Compounds ug/g (ppm)
DIchlorochfl uoromethane <004 Tetrachloroethene <004
Chloromethane <0.04 DIbromochloromethane <0.04
Vinyl chlorIde <0.04 1,2-Dibromoethane (EDB) <004
Bromomethane <0.04 Chloroben zen e <004
Chloroethane <0.04 Ethylbenzene <004
TnchloroD uorom ethan e <0.04 1,1,1,2.Tetrachloroethane <004
Acetone <0.4 m.p-Xylene <0.04
1,1-DIchloroethene <0.04 o-Xylene <004
Methylene chlonde <0.2 Styrene <0.04
trans-1 ,2- Dichloroethene <0.04 Isopropylbenzene <004
1,1-DIchloroethane <004 Bromoform <004
2,2- DIchloropropane <0.04 n.Propylbenzene <0.04
cIS-1,2-Dlchloroethene <0.04 Bromobenzene <004
Chloroform <0.04 1,3,5-Tnmethylbenzene <004
2-Butanone (1:fEK) <0.4 1,I,2,2-Tetrachloroethane <004
1,2-DIchloroethane (EDC) <0.04 1 ,2,a- Tnchloropropane <004
1,1, I-TrIchloroethane <0.04 2-Chlorotoluene <004
1.1-DIchloropropene <0.04 4-Chlorotoluene <004
Carbon Tetrachlonde <0.04 tert-Butylbenzene <004
Benzene <0.04 1,2,4-Tnmethylbenzene <004
Tnchloroethene <0.04 sec- Buty lbenzene <004
1,2.DlChloropropane <0.04 p-Isopropyltoluene <004
Bromod1chloromethane <0.04 1,.3-Dlchlorobenzene <004
Dibromomethane <0.04 1,4- DIchlorobenzene <004
4-Methyl-2-pentanone <0.4 1,2.Dlchlorobenzene <004
cIS-1,:3-Dlchloropropene <0.04 1,2- Dibromo-:3-chloropropane <004
Toluene <0.04 1,2,4- Tnchlorobenzene <004
trans-1,3-Dlchloropropene <0.04 Hexachlorobu tad1ene <0.04
1,1.2-TrIchloroethane <0.04 Naphthalene <004
2-Hexanone <0.4 1,2,:3- Tnchlorobenzene <004
1,3-DlChloropropane <0.04
4
FRIEDMAN & BRUY A, INC.
ENVIRONMENTAL CHEMISTS
Analysis For Volatile Compounds By EPA Method 8260
Client Sample ID
Date ReceIved.
Date Extracted.
Date Analyzed.
MatTLx:
Umts.
Method Blank
12/22/97
12/24/97
12/24/97
Soil
ug/g (ppm)
Surrogates.
Dibromofluoromethane
1,2- DIchloroethane-d4
Toluene-dS
4-Bromofluorobenzene
Compounds
DIchlorochfluoromethane
Chloromethane
Vinyl chlonde
Bromomethane
Chloroethane
Tnchlorofluoromethane
Acetone
1,1- DIchloroethene
Methylene chloride
trans-l ,2- DIchloroethene
1,1- DIchloroethane
2,2-Dichloropropane
clS-l ,2- DIchloroethene
Chloroform
2-Butanone (MEh.l
1,2-DlChloroethane (EDC)
1,1,1- TrIchloroethane
1,I-DIchloropropene
Carbon Tetrachlonde
Benzene
Trichloroethene
1,2- DIchloropropane
Bromoruchloromethane
Dibromomethane
4-Methyl-2-pentanone
cIs-I, '3- DIchloropropene
Toluene
trans-l,3-DIchloropropene
1,1,2-TrIchloroethane
2-Hexanone
1,3- Dichloropropane
% Recovery
105
101
71
S2
ConcentratIOn
ug/g (ppm)
<004
<004
<004
<004
<004
<004
<04
<004
<02
<004
<004
<004
<004
<004
<04
<004
<004
<004
<004
<004
<004
<004
<004
<004
<04
<004
<004
<0.04
<004
<04
<004
Chen t.
ProJect.
Lab ID'
Data File:
Instrument:
Operator'
Lower
LImIt
54
62
61
59
Klemfelder
Yelm-RIte AId
ME 07-742
122415 D
GCMS 1
YA
Upper
LImit
lIS
119
120
124
ConcentratIOn
ug/g (ppm)
<004
<004
<004
<004
<004
<004
<004
<004
<004
<004
<004
<0.04
<004
<004
<004
<004
<004
<004
<004
<004
<0.04
<004
<004
<004
<004
<004
<0.04
<004
<004
<004
CompouncLs.
Tetrachloroethene
Dibromochloromethane
1.2-Dibromoethane (EDB)
Chlorobenzene
Ethylbenzene
1 1,1,2-Tetrachloroethane
m p-Xylene
o-Xylene
Styrene
I sop ropy Ibenzene
Bromoform
n-Propylbenzene
Bromobenzene
1,,3,5- Tnmethylbenzene
1, 1 ,2,2- Tetrachloroe than e
1,2.:3-Tnchloropropane
2-Chlorotoluene
4-Chlorotoluene
tert-Butylbenzene
1,2,4-Tnmethylbenzene
sec-Butylbenzene
p-Isopropyltoluene
1, '3-DIchlorobenzene
1,4- DIchlorobenzene
1,2-Dtchlorobenzene
1 ,~. Dibromo-,3-chloropropane
1,2,4- Tnchlorobenzene
Hexachlorobutamene
Naphthalene
1,2,:3-Tnchlorobenzene
4
Date of Report: 01/07/98
Date ReceIved. 12/22/97
ProJect. Yelm-R1te AId
FRIEDMAN & BRUY A, INC.
ENVIRON1vIENT AL CHE:rvIISTS
QUALITY ASSURANCE RESULTS FOR THE ANALYSIS OF SOIL SAMPLES
FOR POLYCHLORINATED BIPHENYLS AS AROCHLOR 1254 BY GC/ECD
Laboratory Code. 712092-06 (DuplIcate)
Analvte
Arochlor 1254
Reportmg
Umts
lJ,g/g (ppm)
Sample
Result
<1
RelatIVe
Percen t
Dliference
nm
Acceptance
Cntena
0-20
DuplIcate
Result
<1
Laboratory Code 712092-06 (Nlatm;: Spike)
Analvte
Arochlor 1254
Reportmg
Umts
lJ,g/g (ppm)
Spike
Level
0.7
Sample
Result
<1
% Recovery
MS
107
Acceptance
Cntena
fiO-150
Laboratory Code Laboratory Control Sample
Analvte
Arochlor 12,54
Reporting
Units
Ilg/g (ppm)
Spike
Level
0.7
RelatIve
Percent
Dliference
6
% Recovery
LCS
10.3
% Recovery
LCSD
109
Accep tance
Cntena
G5-1 :35
nm - The analyte was not detected m one or more of the dupllcate analyses. Therefore, calculatIOn of
the RPD IS not appllcable.
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23 Dec 97 07:00 PM Instrument Method:
07 Jan 98 08:05 AM Analysis Method :
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Send l1u.."> To
KLEINFELOEA
1200 112TH AVENUE NE
SUITE C226
nELLEVUE WA nf\on.'
("01;) 451 2877
~!" fl;)17
k-q KlEINFElDER
APPLICATION FOR AUTHORIZATION TO USE
PHASE II ENVIRONMENTAL SITE ASSESSMENT
PROPOSED RITE AID PROPERTY, #97-138
BUCKLIN Hll.-L ROAD AND SaVERDALE WAY
SIL VERDALE, WASHINGTON
KLEINFELDER PROJECT NUMBER 60-1756-04
DATED
January 15, 1998
TO Klemfelder, Inc
2405 140th Avenue NE
SUite AlOl
Bellevue, Washtngton 98005
FROM.
Applicant
[State here the use(s) contemplated}
hereby appltes for penmsslon to
for the purpose(s) of
[SUte here ....-by yOU wish to do whatlS contemplated as set forth above}
ApplIcant understands and agrees that the above IdentIfied report prepared by K1emfelder, Ine. 15
the copynght owner and that unauthonzed use or copymg of the above IdentIfied report IS strictly
prohibited WIthout the express wntten permiSSIon of Klemfelder, Inc and K1emfelder' 5 clIent
Applicant understands that Klemfelder, Inc and/or Klemfelder's client, may Withhold such
pernusslOn at Its sole dIscretIOn, or grant such perrrusslOn upon such terms and conditions as It
deems acceptable.
Dated
Applicant
by
ItS
60-174204/6018ROO8
Copyright 1998 Kleinfelder, Inc.
C-1
printed. 01/1519&