Reference 20 Page 1

• 330 North College Avenue

'.·.A ~ [ IDEM Office of Land Qualii)' _ Fileroom Stamp ifldianapolis, Indiana 46202 ·. 7WKE'D A J\ If[' YIW Project Name: fWtxer !Jll&n fJ ,JJ /lJ (317 685-6600 • Fax (317) 68s.6610 • ·· ~Y.L. Wil>#: &z 9j;otJ'! File ·•de: "t'oD 1-800-508-8034

ENVIRONMENT A ,.rf.NC..,ption: emril: keramida@keramida.com ENGINEERING • CONSULTING • R Mio11fi\tfl

1

AIR, LAND, wATER· Volll;;!l~dential? V· ~No w b page: www.keramida.com

•

Deliberat;.,,

..LNo

WASTE CHARACTERIZATION FORMER ALLISON PLANT #10

700 NORTH OLIN AVENUE INDIANAPOLIS, INDIANA

KERAMIDA PROJECT NO. 2829

Submitted To:

INDIANA DEPARTMENT OF ENVIRONMENTAL MANAGEMENT Mr. David Berrey

Industrial Waste Section I 00 North Senate Avenue, Shadeland'Office

P.O. Box 6015 Indianapolis, Indiana 46206-6015

Submitted By:

KERAMIDA ENVIRONMENTAL, INC. 330 North College Avenue Indianapolis, Indiana 46202

317/685-6600

December 6, 2000

Setting The Standard of Excellence

ENGINEERS •'HYDROGEOLOGISTS • SCIENTISTS • INDUSTRIAL HYGIENISTS • TOXICOLOGISTS OFFICES IN: CHICAGO, IL • EVANSVILLE, IN • CINCINNATI, OH ·SACRAMENTO, CA • ATHENS, GREECE

Reference 20 Page 2

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ENVIRONMENTAL, INC. ENGINEERING • CONSULT! NG • REMEDIATION AIR • LAND • WATER • WASTE

December 6, 2000

Mr. David Berrey Indiana Department of Environmental Managemen Industrial Waste Section I 00 North Senate Avenue, Shadeland Office P.O. Box 6015 Indianapolis, Indiana 46206-6015

Re: Waste Characterization Former Allison Plant# I 0 700 North Olin Avenue Indianapolis, Indiana

Dear Mr. Berrey:

330 North College Avenue

Indianapolis, Indiana 46202

(317) 685-6600 • Fax (317) 685-6610 ·

1-800-508-8034

email: keramida@keramida.com

web page: www.keramida.com

Direct No.: 317/685-6606 Direct Voice No.: 65

Direct e-mail: agremos@keramida.com

IDEM Office of L~d Quality - Filer u VRP Prm;~ct Name: tormH !Jib~ ,7 df I o VRP#: /-r99/7JD 'f File' .y<'oo Description: ____ _ Contiaential? __ Y­

Deliberativ

;< X

As per our recent discussions, KERAMIDA Environmental, Inc. (KERAMIDA) on behalf of Genuine Parts Company (Genuine Parts) is providing the following information in request of an agency position regarding whether investigation and/or remediation derived waste generated at the above-referenced site during a voluntary remediation project should be a listed hazardous waste. Provided below are a project background summary and the results of sampling conducted at the site for investigation and waste characterization purposes.

Project Background

The original building was constructed in 1956, and the floor space was doubled in 1970. In 1990, the western portion of the building was enclosed. Prior to that time, the area was a storage pad covered with a metal roof. A map illustrating salient site features is provided as Figure 1 in Attachment 1. BHT Corporation conducted the initial operations at the facility, they remanufactured carburetors and brakes. General Motors Corporation (GMC) purchased the facility in 1973 and used it as a warehouse for obsolete machines, tooling, and fixtures (Plant I 0). Plant 10 was operated as a part of the GMC Speedway Division (Plant 3) until approximately 1984 when it was made a part of the Allison Gas Turbine Division. The subject site subsequently became the property of the Allison Engine Company (AEC) when GMC divested that division. AEC sold the facility to Associated Properties, Inc. in 1998. At that time, Genuine Parts was leasing the property to warehouse automotive parts. The subject site has been vacant since June of2000 .

• Setting The Standard of Excellence

ENGINEERS • HYDROGEOLOGISTS • SCIENTISTS • INDUSTRIAL HYGIENISTS • TOXICOLOGISTS OFFICES IN: CHICAGO, IL • EVANSVILLE, IN • CINCINNATI, OH • SACRAMENTO, CA • ATHENS, GREECE

Reference 20 Page 3

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Ms. David Berrey Indiana Department of Environmental Management Page 2

KERAMIDA is currently working together with Ms. Andrea Robertson of IDEM's Voluntary Remediation Program (VRP) and Genuine Parts to investigate and remediate volatile organic compound (VOC) and metals impacted soil and groundwater at the Site (VRP #6991004). Investigation activities originated in 1993 when GMC conducted due diligence (Phase I and Phase II) assessments of the subject property. Investigation activities have continued since that time on behalf of GMC and more recently Genuine Parts. The project was entered into the VRP in 1999. Genuine Parts is conducting investigation/remedial activities based on their affiliation with the BHT Corporation. Genuine Parts has an access agreement with the current property owner Associated Properties, Inc. to conduct remedial activities. GMC is currently not involved with the VRP project.

Sample Results

Historically, investigation-derived wastes generated at the site have been classified as an F-waste (FOOl, F002, F003), presumably due to the presence of chlorinated volatile organic compounds detected in soil and groundwater samples. The F-listing of the investigation-derived waste began prior to Genuine Part's involvement in the project and may have been a conservative measure taken by GMC to classify the waste in the absence of a known or suspected source (e.g. degreaser). Chlorinated VOC contamination has been detected in soil and groundwater west and southeast of the former facility building. Maps illustrating soil and groundwater VOC concentrations detected on-site during previous investigations are provided as Figures 2 and 3 in Attachment I. As is illustrated by the maps, the contamination does not appear to be related to any particular process-feature such as a degreaser or dip tank. According to the Phase I information Review Report prepared for the site by Parsons Engineering Science, Inc in April 1993, there were no reported releases of chlorinated VOC at the site. Although chlorinated solvents were likely historically used at the facility, there are no available records that would indicate what these solvents were or how they were used .

Toxicity Characteristic Leachate Procedure (TCLP) testing has been performed on materials excavated from the western portion of the site during exploratory trenching and remediation activities. The exploratory trenching was conducted to investigate anomalies detected during a recent geophysical survey. A map illustrating the observed anomalies is provided as Figure 4 in Attachment 1. The exploratory trenching did identify the presence of nearly "disintegrated drums and debris. The drums appear to have contained discarded automotive parts and floor sweepings. There was no apparent indication that the drums once contained liquids or sludges from waste solvents. The TCLP tests have included VOC, semi-volatile organic compounds (SVOC), and the eight Resource Conservation and Recovery Act (RCRA) metals (Metals) analyses. Not all samples were analyzed for all of these parameters. Total VOC and Metals analyses were also run on certain samples. TCLP analytical results are summarized in Tables I and 2 provided in Attachment 2. Totals results are summarized in Tables 3 and 4 (Attachment 2). TCLP SVOC were analyzed for in one sample (A-3 COMP). No detectable concentrations of these compounds were identified in the sample. The geophysical map illustrates the locations of the anomalies where samples were collected (Figure 4, Attachment I). Sample identifications provided in the tables reference the ano.malies. For example, sample "A-3 COMP" is a composite sample collected from Anomaly 3 of the map. Laboratory reports are provided in Attachment 3.

None of the samples analyzed for TCLP organic constituents (VOC and SVOC) contained leachate levels of these compounds greater than their respective regulatory thresholds. In fact, the only detection was 0.064 milligrams per liter oftrichloroethene in one sample (A-2/A-3). Some soils were determined to be a characteristically hazardous waste due to lead and/or cadmium content. These soils were located

Reference 20 Page 4

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Ms. David Berrey Indiana Department of Environmental Management Page3

adjacent to buried debris and deteriorated drums located in the extreme western portion of the Site south of the entrance and in the southwester corner of the Site.

Based on the information provided above, it is believed that investigation/remediation-derived waste generated at the Site should not be classified as F-listed hazardous waste. Waste characterization sampling that has been conducted does indicate that some of the materials are a characteristically hazardous waste attributable to Metals content. These materials will be managed as a hazardous waste. Additional waste will be generated in the future during planned investigation and remediation activities. TCLP sampling will be conducted on new waste streams to investigate the presence of a characteristically hazardous waste.

KERAMIDA respectfully requests that, upon review of this letter, the IDEM respond as to whether it concurs with the generator's position that investigation/remediation-derived wastes generated at the Site during the voluntary remediation project should not be a listed hazardous waste. Approximately 500 tons of soils and debris that do not exhibit a hazardous characteristic but do contain low levels of chlorinated VOC (per totals analysis) have been generated and await final classification prior to disposal. A 30-day extension of the 90-day accumulation period has been granted by the IDEM and, if determined to be a listed hazardous waste, these materials must be taken off-site in January of 200 I. Therefore, an expeditious response is requested to allow time for disposal management of these materials. KERAMIDA appreciates your consideration of this matter. Should you have any questions regarding this correspondence, please contact me at your convenience.

Sincerely, KERAMIDA Environmental, Inc.

~G)~ . Andrew A. Gremos, L.P.G., C.H.M.M. Vice President of Site Investigation and Remediation Services

Enclosures

cc: Robert Lewis, Genuine Parts Company Andrea Robertson, IDEM Voluntary Remediation Program

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Reference 20 P

age 8

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EM31 IN PHASE METAL (parts per thousand) ALLISON ENGINE COMPANY PLANT 10 SITE, HOLT ROAD

INDIANA

MAP SCALE {In feet)

,--40 60 80 100

...

Reference 20 P

age 9

•

TCLP =T~x.icity duoroderistic Izoding: Procedure

VOCo"' Volatile Organic Compound;

mYL"' nlilligntm$ per liter (II Tub!" l • Maximum Concentration afC<>nlamirurnt. f~rtJ,eToxiciry doamcterislic

• Table 1 \Vaste Chaructcril.utinn Sum piing

TCLP VOC Analytical Results (mg/L) in Soils Fonner Allison Plant 10 700 North Olin Avenue lnc.lianapulis, Indiana

•

~

Reference 20 P

age 10

•

TCLP =Toxicity Charncteristic Leading Procedure

mgiL =milligrams per liter

• Table 2 Waste Characterization Sampling

TCLP RCRA Metal Analytical Results (mg/L) in Soils Former Allison Plant 10 700 North Olin Avenue Indianapolis, Indiana

{IJ Table I -Maximum Concentration of Contaminants for the Toxicity Characteristic

"" "' ~ t ..::

<ii

•

Reference 20 P

age 11

•

VOCs "Voh!lit" l.lr!Miic ComJWiln<l:o

Sampl.-s analyud wing EPA S\V-846 Method 8260

uglkg dw = micrograms p;:r kilogram dry weigl1t

NA ~Not Applicable

M Indiana Do!partment ofEnviron.m~ntal MIUt:.lgement Voluntazy

R~m~diation Pn~nm R"'uurce Guid~, Appendi.-..: F Tier U

Cl<anup G<>11ls-Human H,.,Jtli Evaluation by Offioo of

Envirorunental Response, July 1996

(1) Source: EPA Region 3 Risk-Based Conct<ntration Table·

Octob.:i 1998 Update

• Table3 Waste Characterization Sampling

VOC Analytical Results (ugfkg dw) in Soils Former Allison Plant 10 700 North Olin Avenue Indianapolis, Indiana

•

Reference 20 P

age 12

• • Table 3 Waste Characterization Sampling

VOC Analytical Results (uglkg dw) in Soils Former Allison Plant 10 700 North Olin Avenue Indianapolis, Indiana

•

• ~ ~ ::! ..J.. -Ill ..; s:: 2 ~ 41 "';

41 ~ 41 .::: .... ::: "C -

~ g j f !i ~ ~ ~ ~ ;;"' s ;:. .g ~ e ·E41 ·c"' ::::: ..., ~:e ;: ~ "0 ::: ..S H c: f..<::: u "' "ij§ -a z E .E -5 4~~ .t:.~ "E> ]

Sample No. Date Sampled Lab Sample No. :;E :S Z ~ ~ ~ ;= :1 j :::. j ~ X' A-4 COMP 10/1912000 278635 32 <5.6 <5.6 <5.6 <5.6 30 <5.6 <5.6 <II <5.6 A·S COMP !Ofl9!2000 278636 <29 <5.8 <5.8 <5.8 <5.8 83 <5.8 <5.8 <12 <5.8 A·7COMP 10/1912000 278637 30 <5.5 <5.5 <5.5 <5.5 30 <5.5 <5.5 <ll <5.5 A-6 COlv!P I0/19/2000 27&63~ <28 <5.5 <5.5 <5.5 <5.5 9.7 <5.5 <5.5 14 <5.5 A-8 COMP I0/19/2000 278639 47 <5.7 <5.7 <5,7 <5.7 41 <5.7 <5.7 <II <5.7 A-9 COMP 10/1912000 278640 <30 <5.9 <5.9 <5.9 <5.9 6.2 <5.9 <5.9 <12 <5.9 A-3 COMP 10/06/2000 277730 40 IZ 20 <5.0 130 32 160 45 <10 31

A-2/A-3 10/06/2000 277731 <1,900 9,90ft 3,5110 160 <380 9,9110 32,000 12,000 <760 4,9110 /\-1 C01'1.1J) 10/06/2000 277TJ2 MZ <5.U <5.0 <5.0 <5.0 1741 <5.0 <5.0 <l(J <5.0

A-4-9 COMP 10/0612000 277733 <25 <5.0 <5.0 <5.0 <5.0 5.5 <5.0 <5.0 <10 <5.0 :&H!li?:MWWW:W!@@l@t.'Wmf,mf.;t~f:&~ ... £WillWlW:>=~k(iM1MM&~131t~~=*~~**i~~#:t<~MW®.?~d:id!%W@t!~itWtf'~~M~1lt.H!FA'¥BkMWb@:tt:'~·. tmrm~~~Wt'.:M:Wm::¥1f:~ .. -;,;:#t0.1f..tr:brNM::~lM::®dH~~M:#M#?

Tier II Non·Re:>identiat Cleanup Goals Swface Soii{IJ NA 10,000,000 20,000,000(1) I 101,230 I 1,000,000 I 24,790 100,000,000°> 100 000,000(2) I 20 1,000,000

:::M1:i;mHS:ff@H.tW:~m .. ~W:YOC-.f.4Mm:~mtmmmt:m~t·mmt:t<m&Wi.t?~:::::~-::::*~~m:mit6MNHf.if%fft:\~:g;~~tm,:@t:,.i~:W@mMMH::1t<m:~f.?:mblmmmMtt:::=d@W~~?JMWW~L-... ·.:::.~#.iWl'm~mm~H~~~FfWt®~~1@~fi:M~M~m1~::~i%\ TieriiNon-Residenti.llCie:m!!.P...Go.:~lsSubsurfaceSoil< 1 ) I NA 10,000,000 J 20,000,000 ·I 8,010 I 1,000,000 I 25,730 100,000,0001~1 IOOOOO,OOOVI 130 1,000,000

VOC• "' Volatil~ Organic Compounds

Sam pi~ analyud using EPA SW -84 6 M.-thod 8260

uglkg dw" micrograms per kilogram dry weight

NA""' Not Applieab!e

(I) Indiana Department ofEnvirorunental Manascment Vo!untruy

R¢mediation Progrum Resouree Guide, Appcndt"< F Ti~r D

Cleanup GoaJ,..Human H~lth Evaluation by Offic~ of

Enviro1unenta\ Response, July 1996

(I) Sol!ru: EPA Region 3 Risk-Based Concentrntion Table •

October \998 Update

Reference 20 P

age 13

•

Samples analyzed using EPA Method Series 6ooonooo mg!kg"" mit!igrnms per kilogram

• Table 4 Waste Characterization Sampling

Total RCRA Metal Analytical Results (mglkg) in Soils Former Allison Plant 10 700 North Olin Avenue Indianapolis, Indiana

(l) Indiana Department of Environmental Management Voluntary Remediation Program Resource Guide, Appendix F Tier U Cleanup Goals-Human

Health Evaluation by Oflice of Environmental Response, July 1996

(l) Soun:e: James Dragun. Tile Soil Chemistry of Hazardous Materials Table 3.1 Native Soil Concentration ofVarious Elements: p.229, 1988

(J) IDEM VRP Interoftiee Memo dated on January 26, 1998

•