APPENDIX F DATA OBTAINED FROM PREVIOUS SITE
DRAFTAPPENDIX FDATA OBTAINED FROM PREVIOUS SITE INVESTIGATIONS(SECTION 6.0 OF NUS WORK PLANPREVIOUSLY SUBMITTED IN NOVEMBER 1983)
6.0ENVIRONMENTAL CONCENTRATIONS6.1AirAn air sampling program was conducted at the site on November 16 and 17, 1982 bythe Environmental Response Team (ERT) from ERA Region III. Ten onsitelocations and two background locations were sampled using calibrated portable airpumps with different capturing media for various chemical groups. These mediawere analyzed for total organics, organic solvents, aromatic amines, inorganicacids, RGBs, and metal particulates. No airborne vapor/gas contaminants werepresent above the detection limits.Air samples were collected in the crawl spaces of houses adjacent to the landfillusing similar collection equipment as the onsite air survey. Grab samples werecollected and analyzed using a Photovac 1QA10 portable gas chromatograph (GC).The samples that gave a response were sampled with the pumping system for alonger period of time. Table 6-1 presents the analytical results, which indicatethat some form of hydrocarbons were present in all samples. Since there werecompounds present at or slightly above the GC's detection limit, but not insufficient concentration to be identified on a GC/MS, all compounds' detected in asample were totalled and reported as total hydrocarbons (as if it were toluene).The offsite sampling did not show the presence of compounds in sufficientconcentrations to be identified on a GC/MS with the exception of carbontetrachloride in one sample ( 20 ug) in a 600 mg charcoal tube (ERT, 1983b).6.2SoilTable 6-2 lists the locations and descriptions of soil samples collected at or nearthe site by various agencies. PADER collected three soil samples from on site andfour samples from adjacent, offsite property. ERT collected soil samples from 23locations on site, some of which were sampled at various depths. ERT samplinglocations are shown on Figure 6-1. The analytical results are presented inTables 6-3, 6-4, 6-5, and 6-6.AROODSlii*6-1
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TABLE 6-2MILLCREEK SITESOIL SAMPLE LOCATIONSSampleCodeSample Locationor NumberDescriptionSMC01Middle of siteOily wasteSMC02DateSampler3/23/82PADERComposite of site7/28/82PADERSMC0350 yd south-Well 1 Sample at 6-in intervals(18 in. to 24 in.)7/29/82PADERSMC04Sample #1Samples at surface, 1 ft, 4 ft11/82ERTSMC05Sample #2Samples at surface, 1 ft, 4 ft11/82ERTSMC06Sample #3Surface - saturated silt muck1 ft - saturated gray clay muck4 ft - saturated gray clay, sand11/82ERTSMC07Sample #4Surface - black loam1 ft - black silt fill4 ft - black silt fill11/82ERTSMC08Sample #5Surface - black silt fill1 ft - black silt fill11/82ERTSMC09Sample #6Surface - black muck1 ft - light brown clay, silt4 ft - saturated fine brown sand11/82ERTSMC10Sample #7Surface - black clay, silt1 ft - brown clay, silt4 ft - saturated sand11/82ERTSMC11Sample #8Surface - black muck1 ft - clay4 ft - brown sand11/82ERTSMC12Sample #9Surface - black muck, peat1 ft - brown clay, silt11/82ERT4 ft - saturated brown muckSMC13Sample #10Surface - black clay3 ft - brown saturated6 ft - brown sand, loam11/82ERTSMC14Sample #11Surface - black clay, sand1 ft - saturated brown sand4 ft - brown gravel, loam11/82ERT6-3uu
TABLE 6-2MILLCREEK SITESOIL SAMPLE LOCATIONSPAGE TWOSampleCodeSample Locationor NumberSMC15fy. y-' -',DescriptionDateSamplerSample #12Surface - saturated black sand1 ft - saturated brown clay4 ft - gray sand, silt11/82ERTSMC16Sample #13Surface - saturated brown sand, silt3 ft - saturated brown clay, sand6 ft - saturated gray gravel, sand11/82ERTSMC17Sample #14Surface - brown silt loam11/82ERT3 ft - light brown clay6 ft - saturated brown claySMC18Sample #15Surface - brown loam1 ft - saturated black muck4 ft - saturated gray gravel, sand11/82ERTSMC19Sample #16Surface - black loam6 ft - saturated brown sand, silt11/82ERTSMC20Soil Sample #17Surface - brown loam6 ft - saturated gray sand, clay11/82ERTSMC21Soil Sample #18Surface - black fill, sand, gravel11/82ERTSMC22Sample #19Surface - black loam11/82ERTSMC23Sample #20Surface - black fill11/82ERTSMC24Sample #21Surface - black fill11/82ERTSMC25Sample #22Surface - black fill11/82ERTSMC26Sample #23Surface - black loam11/82ERTSMC27Oros backyardComposite10/26/82 PADERSMC28George backyardComposite10/26/82 PADERSMC29Hetrick backyardComposite10/26/82 PADERSMC30Front yardsComposite10/26/82 PADERSources:PADER, March 23, 1982; PADER, July 28, 1982; PADER, July 29, 1982;PADER, October 26, 1982; ERT, April 1983.ERT:PADER:Environmental Response TeamPennsylvania Department of Environmental Resources6-4
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TABLE 6-3MILLCREEK SITESOIL ANALYSES - METALS, INORGANICSSample kq)0.2668.035,712OilpH——Total Organic CarbonChemical Oxygen DemandCyanide (total)Cyanide (free)PhenolsAmmonia (as N)ArsenicCadmium -—8— 5 0.1 0.3— 0.1— ———————: :mg/kg:8211,9441,331103956 0.246,6396224,7770.66Not analyzedLess thanmilligrams per kilogramTable 6-2 and Figure 6-1 for sample locationsSources: PADER, March 23, 1982; PADER, July 28, 1982; PADER, July6-6——
TABLE 6-4MILLCREEK SITESOIL ANALYSES - EP TOXICITY RESULTSSample Number hromiumCopper——2.8103——13—62 0.010.02 82—11,944Lead1400.07 1,331 mg/l:mg/kg: :—:EP Leachate(mg/l)—————Soil(mg/kg)0.0050.056 0.01 0.018.22103 0.002956 0.02 0.2 0.014 0.016,63912.73milligrams per litermilligrams per kilogramLess thanNot analyzedTable 6-2 and Figure 6-T for sample locationsSources: PADER, March 23, 1982; PADER, July 28, 19826-7EP Leachate(mg/l)
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Of the three onsite samples collected by PADER, SMC01 and SMC02 wereanalyzed for metals and were leached using the RCRA extraction procedure andanalyzed. SMCO2 was also analyzed for other inorganic compounds. SMC03 wasanalyzed for oil and PCS. SMCO1 and SMC02 contained metals at variousconcentrations. SMC03 contained 12 ug/kg of PCS (as Aroclor 1248) and 35,712mg/kg of oil.The samples that PADER collected off site (SMC 27 through SMC 30) wereanalyzed by GC/MS for priority pollutant organics. No acid extractables, volatiles,PCBs, or pesticides were detected in the four samples. All four samples containednumerous base/neutral extractables. The concentrations ranged from 1 ug/kg foracenaphtylene to 680 yg/kg for di-n-butyl phthalate.Samples SMC04 through SMC08, collected by ERT, had water extracts from themanalyzed using the Microtox System. The Microtox is intended for use indetermining the acute toxicity of aqueous samples. The system uses a specialstrain of bioluminescent bacteria. A photomultiplier tube measures the relativelight output of these organisms before and after exposure to serial dilutions of asample. Toxicity is indicated by a percent decrease in light output. The resultsfrom duplicate samples are averaged to calculate a normalized percent lightdecrease (NPLD) corresponding to each dilution. Marginal toxicity is sometimesindicated by an increase in light output due to biostimulation of the bacteria (ERT,1983b). The results of the Microtox System analysis are shown in Table 6-7.Samples SMCO9 through SMC26, collected by ERT, were analyzed for organicpriority pollutants. Base/neutral extractable compounds were detected in SMC09and SMC20 through SMC26. Volatile organics were detected in SMC13, SMC16,SMC17, and SMC26. PC8 was detected in SMC21, SMC23, and SMC26. Thevolatile organics appeared to penetrate further into the ground and to accumulatein the saturated zone, in contrast to the base/neutral extractable compounds.Especially evident were 1,2-trans-dichloroethylene and trichloroethylene, whichappeared in deeper soils while absent from the surface soils. The base/neutralextractable compounds were generally confined to the top foot of soil.6-11
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6.3GroundwaterTable 6-8 lists the locations of groundwater samples collected by various agencies.PADER collected 14 groundwater samples at or near the Miilcreek Site, ERT andTAT collected 12 onsite groundwater samples, and a Technical Advisory Team(TAT) collected 3 groundwater samples off the site.Analytical results arepresented in Tables 6-9, 6-10 and 6-11.Miilcreek Township had installed 5 monitoring wells on its portion of the site. Nineadditional wells were installed around the site for the ERT investigation. Threepublic drinking water wells (Yoder Wells) and two private wells were also sampled.PADER sampled the township monitoring wells in July 1982. These samples(GWMC01, GWMC03, GWMC04, GWMC08, and GWMC09) were analyzed for ailpriority pollutants and other inorganic parameters. Some metals and volatileorganics were detected in the five wells at varying concentrations. PADERresampled two of the wells (GWMC04 and GWMC07) in January 1983. Metals andvolatile organics were detected again, in addition to low concentrations (23 ug/l) ofisophorone and bis(2-ethylhexyl)phthalate, base/neutral extractables, in GWMC04.PADER sampled all five township monitoring wells (GWMC26 through GWMC30) inApril 1983 and analyzed them for gross alpha and gross beta radioactivity. Thevery low levels measured were below drinking water standards and do not indicatea radioactivity hazard.ERT and TAT sampled three of the five wells installed by the township and the nineadditional onsite wells (No. 6-14) in December 1982. These samples (GWMC02,GWMC06, and GWMC10 through GWMC19) were analyzed for metals, volatileorganics, and poiynuclear aromatic hydrocarbons (PAH's).No PAH's weredetected. Volatile organics were detected in GWMC02, GWMC06, and GWMC11through GWMC16. Metals were detected in every sample.TAT sampled the Yoder public drinking water supply wells in February 1983. Thesesamples (GWMC20 through GWMC22) were analyzed for priority pollutant organic6-13
TABLE 6-8MILLCREEK SITEGROUNDWATER SAMPLE LOCATIONSSampleCodeSample Locationor NumberGWMC01Twp.Well #1GWMC02Twp. Well #1GWMC03Twp. Well #2GWMC04Twp. Well #2DescriptionBlack iron casingBlack iron casingBlack iron casingBlack iron ERT, TATPADERPADER(not purged)GWMC05GWMC06GWMC07GWMC08GWMC09GWMC10Twp. Well #3Twp. Well #3Twp. Well #3Twp. Well #4Twp. Well #5Twp. Well #5Black iron casingBlack iron casingBlack iron casingBlack iron casingBlack iron casingBlack iron DERERT, TATPADERPADERPADERERT, TATGWMC11Well #6PVC12/5/82ERT, TATGWMC12Well #7PVC12/5/82ERT, TATGWMC13Well #8PVC12/5/82ERT, TATGWMC14GWMC15Well #9Well #10PVCPVC12/5/8212/5/82ERT, TATERT, TATGWMC16Well #11PVC12/5/82ERT, TATGWMC17GWMC18Well #12Well #13PVCPVC12/5/8212/5/82ERT, TATERT, TATGWMC19Well #14PVC12/5/82ERT, TATGWMC20GWMC21GWMC22GWMC23Yoder Well #1Yoder Well #2Yoder Well #3KnostPublic water supplyPublic water supplyPublic water supplyPrivate well2/83TAT2/83 TAT2/83 TAT12/14/82PADER3133 W. 12thStreet6-14
i JTABLE 6-8MILLCREEK SITEGROUNDWATER SAMPLE LOCATIONSPAGE TWOSampleCodeSample Locationor aschneskeKraschneskeTwp. Well #1Twp. Well #2Twp. Well #3Twp. Well #4Twp. Well #5PADER:ECHO:TAT:ERT:DescriptionKitchen faucetPrivate wellBlack iron casingBlack iron casingBlack iron casingBlack iron casingBlack iron Pennsylvania Department of Environmental ResourcesErie County Health DepartmentTechnical Advisory TeamEnvironmental Response TeamSources: Vrenna, C., January 12, 1981; PADER, July 1, 1982; PADER, July 21,1982; PADER, December 14, 1982; PADER, January 12, 1983; Dreisch,R., February 1, 1983; Austin, J., February 2, 1983; Kayser, S., February16, 1983; Sammons, B., February 18, 1983;ERT, April 1983; PADER,April 11, 1983.6-15
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compounds and some metals. Barium was detected in all three samples. Mercurywas detected near the detection limit in GWMC21. No organics were detected inGWMC20. Trichlorofluoromethane was detected in GWMC21 at a concentrationbetween 1 ug/l and 10 ug/l. 1,1,1-Trichloroethane was estimated at a concentrationof 0.2 ug/l in GWMC22.PADER sampled private wells owned by Knost (GWMC23) in December 1982 andKraschneske (GWMC24) in July 1982. The Kraschneske well (GWMC25) wassampled by Erie County in November 1980. GWMC23 was analyzed for inorganicsand priority pollutants. No organics were detected. GWMC24 was analyzed fororganic priority pollutants; the results were negative. GWMC25 was analyzed onlyfor inorganics.6.4Surface WatersTable 6-12 lists locations where surface water and sediment samples werecollected by various agencies. PADER collected six surface water samples at ornear the site. The EPA collected two surface water samples on site, while Ecologyand Environment, Inc. (E & E) collected two sediment samples. The ERT and TATcollected four surface water samples. The Erie County Health Department (ECHO)collected six samples from Marshalls Run and one sample from the swamp. Theanalytical results from all samplings are presented in Table 6-13 through 6-16.The onsite pond was sampled once by PADER (SWMC01) and once by EPA(SWMC02). SWMC01 was analyzed for inorganics and priority pollutants whileSWMC02 was analyzed for priority pollutants. Small quantities of various metalswere detected in both samples. Trace quantities of organics were detected in bothsamples.The drainage ditch (SWMC03) north of the site was sampled by ERT and TAT andanalyzed for metals, volatile organics, and polynuclear aromatic hydrocarbons(PAHs). All of the PAHs tested for were base/neutral extractable compounds. Novolatiles or PAHs were detected, but some metals were.6-22
I ITABLE 6-12MILLCREEK SITESURFACE WATER AND SEDIMENT SAMPLE rSWMC01Pond7/21/82SWMC02SWMC03On-site pondDitch-north60 ft west of well #128/82 EPA12/5/82ERT, TATSWMC04Ditch15 ft west of well C11SWMC12SWMC13SWMC14SWMC15SWMC16SWMC17South swampSouth swampSouth swampSouth swampStreamMarshalls RunMarshalls RunMarshalls RunMarshalls RunMarshalls RunMarshalls RunCreekMarshalls allsMarshallsRunRunRunRunSediment sampleNext to slag drumsNorth edgeSediment sampleUpstreamDownstreamUpstreamUpstream, 15th St. Ext.DownstreamDownstreamBelow drum siteBelow railroad tracks,south of siteAbove Michigan AvenueBelow storm drainBelow cemeteryNear Lake EriePADERPADER8/82 EPA8/26/82E&E8/25/80ECHO12/5/82ERT, TAT8/26/82E&E10/26/82PADER10/26/82PADER% 7/21/82PADER12/5/82ERT, TAT7/21/82PADER12/5/82ERT, HOECHOECHOECHOSources: PADER, August 25, 1980; PADER, July 21, 1982; Wellington, R.,September 1, 1982; Jerpe, J., September 8, 1982; Preston, H., September10, 1982; Austin, J., September 11, 1982; Dreisch, September 14, 1982;Princeton Testing Laboratory, October 25, 1982; PADER, October 26,1982; PADER, December 14, 1982; ERT, April 1983.HR0005666-23
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TABLE 6-15MILLCREEK SITESURFACE WATER/SEDIMENT ANALYSES - BASE/NEUTRAL EXTRACTABLE ORGANICSSample Number1Parameter SWMC09(uq/kg)190260160250— l phthalateDi-n-octyl 1,2,3-cd)pyreneNapthalenePyrene210—290160740940 :SWMC10(ug/l)0.5690less thanlag/kg: micrograms per kilogramyg/l:micrograms per liter1See Table 6-12 for sample locations.—:Not detected, detection limit unknown.Sources: Princeton Testing Laboratory, October 25, 1982; PADER, October 26,1982.6-28
TABLE 6-16MILLCREEK SITESURFACE WATER/SEDIMENT ANALYSESPCBs, PESTICIDES. ACID EXTRACTABLE AND VOLATILE ORGANICSSample Number"1SWMC04 sulfan-alphaNANANA 10 500—Heptachlor chloroethane ichloroethylene1,1,1-TrichloroethaneVinyl ——5———SWMC09 SWMC12 �———149311SWMC14(ug/l)187, 1782Ug/l:micrograms per liter*:estimated See Table 6-12 for sample locationsNA:Not Analyzed.Not detected, detection limit unknown.ug/kg: micrograms per kilogramSources: PADER, July 21, 1982; Princeton Testing Laboratory, October 25, 1982; PADER,December 14, 1982; ERT, April 1983.AB0005726-29
The drainage ditch (SWMC04) separating the Halmi and Riehl properties wassampled once by PADER and analyzed for inorganics and priority pollutants.Phenol (1.4 ug/l) and pentachlorophenol (0.3 ug/l) were detected along with metalsand other inorganics.Water from the south swamp was sampled once by EPA (SWMC05), once by ECHO(SWMC07), and once by ERT and TAT (SWMC08). The swamp sediment wassampled once by E & E (SWMC06). SWMC05 and 06 were analyzed for prioritypollutants. SWMC08 was analyzed for metals, volatile organics, and PAHs.SWMC07 was analyzed for pH, oil, and metals. Metals were detected in allsamples. SWMCOS contained phenol (220ug/kg) and tetrachloroethylene (5 ug/kg).No volatiles or PAHs were detected in SWMCOS. No organics were detected inSWMCOS.PADER collected.two water samples from Marshalls Run, one upstream (SWMC1.0)and one downstream (SWMC11) of the Miilcreek Township portion of the site. E 8tE collected a stream sediment sample from Marshalls Run (SWMC09). The aqueoussamples were analyzed for organic priority pollutants. Diethyl phthalate (0.5 ug/l)was detected in SWMC10. SWMC09 was analyzed for priority pollutants. Novolatiles were detected. Numerous metals and base/neutral extractables weredetected along with lesser numbers of PCS, pesticides, and phenol.Marshalls Run, upstream of the site, was sampled once by PADER (SWMC12) andonce by ERT aad TAT (SWMC13). Both samples were analyzed for prioritypollutants while more inorganics were analyzed for in SWMC12. Some metals andvolatile organics were detected in both samples.Marshalls Run, downstream of the 'site
1 ft - saturated brown clay 4 ft - gray sand, silt SMC16 Sample #13 Surface - saturated brown sand, silt 11/82 ERT 3 ft - saturated brown clay, sand 6 ft - saturated gray gravel, sand SMC17 Sample #14 Surface - brown silt loam 11/82 ERT 3 ft - light brown clay 6 ft - saturated brown clay SMC18
Issue of orders 69 : Publication of misleading information 69 : Attending Committees, etc. 69 : Responsibility 69-71 : APPENDICES : Appendix I : 72-74 Appendix II : 75 Appendix III : 76 Appendix IV-A : 77-78 Appendix IV-B : 79 Appendix VI : 79-80 Appendix VII : 80 Appendix VIII-A : 80-81 Appendix VIII-B : 81-82 Appendix IX : 82-83 Appendix X .
Appendix G Children's Response Log 45 Appendix H Teacher's Journal 46 Appendix I Thought Tree 47 Appendix J Venn Diagram 48 Appendix K Mind Map 49. Appendix L WEB. 50. Appendix M Time Line. 51. Appendix N KWL. 52. Appendix 0 Life Cycle. 53. Appendix P Parent Social Studies Survey (Form B) 54
Appendix H Forklift Operator Daily Checklist Appendix I Office Safety Inspection Appendix J Refusal of Workers Compensation Appendix K Warehouse/Yard Inspection Checklist Appendix L Incident Investigation Report Appendix M Incident Investigation Tips Appendix N Employee Disciplinary Warning Notice Appendix O Hazardous Substance List
The Need for Adult High School Programs 1 G.E.D.: The High School Equivalency Alternative 9 An Emerging Alternative: The Adult High School Ciploma 12 Conclusion 23 Appendix A -- Virginia 25 Appendix B -- North Carolina 35 Appendix C -- Texas 42 Appendix 0 -- Kansas 45 Appendix E -- Wyoming 48 Appendix F -- Idaho 56 Appendix G -- New Hampshire .
Appendix 4 . Clarification of MRSA-Specific Antibiotic Therapy . 43 Appendix 5 . MRSA SSI . 44 Appendix 6 . VRE SSI . 62 Appendix 7 . SABSI related to SSI . 74 Appendix 8 . CLABSI – Definition of a Bloodstream Infection . 86 Appendix 9 . CLABSI – Definition of a MBI -related BSI . 89 Appendix 10 . Examples relating to definition of .
Appendix E: DD Form 577 for Appointing a Certifying Officer 57 Appendix F: Sample GPC Appointment Letters 58 Appendix G: Formal Reporting Requirements 66 Appendix H: Semi-Annual Surveillance Report Template 70 Appendix I: GPC Thresholds 73 Appendix J: Glossary – Sections I and II 75 Chapter 1: The Government Purchase Card Program 1-1. Purpose a.
Appendix D: Active Voice vs Passive Voice . Appendix E: Examples, Use of D0000 . Appendix F: Additional Examples for Principles 2-6 . Appendix G: Examples, Use of D8100 . Appendix H: Examples, Lack of Documentation . Appendix I: Examples, DPS Does Not Match Findings . Appendix J: Examples, Repeating Regulations in the DPS
Appendix D, Prescribed Form for Bidder's Profile 35 12. Appendix E, Letter of Authorized Person in Charge 36 13. Appendix F, Undertaking 37 14. Appendix G, Form of Technical Proposal 38 15. Appendix H, Form of Financial Proposal 39 16. Appendix I, Form of Performance Security 40 17. Appendix J, Bank Guarantee for Advance Payment 41
