- r -

] ( 3 QuaJuy Assunnce ProjtCt Plan for Pictllo Fum

July ]I 1990 Revbion No 2

Paae I of 33

10 TltlePogo

aullty Auunce Project Plan

~

Work 11ten Dille

Wor1 IJA -ltd

C0nnct Numblf

Doll ol lnl11o11on

_ Agency

Connctcw

RlyenriiCLambe

Rtmtdial PlanninJ Activities at the PictUo Farm Site Coventry cr June 26 1990

July II 1990

63-W80120 Work AniJnment No 01 -ILOI April 19 1990 -n US Environmental Protection Apncy ReJion I = Arthur D linle Inc = U

~ - __ Date

Arthur D Litde Project Manaer

4pound~ Date Arthur D Urde Quality Assurance Qualiry Coonrol Oflicer

US Envitonmentll Pr01ecrion Aaency Date

ArtlurD Little

r

Qualuy As unncc ProjtCI Plan for PlctUo farm July 9 1990

Revision No I PaJC 2 o( J3

11 foreword

This Quality Assurance Project Plan it spectncally prepared for the Remedial lnvettiJationFcastbllity Study Phase lA at the Picillo Farm she The Arthur 0 Little ARCS Pfopam Manaaement Plan (PMP) April 3 1989 submitted 10 the Environmenlll Protectkgtn Aaency (EPA) Refon I by Anhur D Uttlt Incbull Havens and Emerson Inc and Remediation Technoloaies Inc containt two sections that provide aencraJ cover~ae of a broad ranp or quality assurance iUIJCI These two teetions n the Qualt ry Assurance Prolflm Plan (QAPP) Section 70 and the Ocneric QuaJiry Auurtnce Project Plan (QAPjP) Att~ehmcnt C The PMP wu approved by US EPA Recbullon I on April II 1989 This siaemiddotspcciftc QAPjP will cover lhotc henu which are unique to the tile and necessary for staff to have onshytland to ensure the work for this project is of adequate and known qualiry General henu covered in the QA PP and QAPjP in the PMP will be referenced in this document and noc repeated

Artlur D Little

I r I

Qualuy As ura nct ProjtCI Pan (Of P1c1Uo Farm July 9 1990

Revision No I Paae 3 of 33

20 Tlble of Contntt

10 Title Paae

11 Foreword

20 Table or Concencs

JO Project Description

31 Project Objective and Scope Statment 32 Dall Qualicy Objectives 33 MonhorinJ Network Deslan Rationale and Parametcn

40 Projecc Oraaniza1ion and Responsibility 16

50 Data Quali ty Objectives for Critical Measu~ments in Tcnru of Precision Accur~ey Completeness Representativeness and Comparability II

51 Summary 18 52 Re~sentativencss middotmiddotbullmiddotmiddotmiddotmiddotmiddotmiddotmiddot 1853 Comparability bull bull bull bull bull bull bull bull 18

60 SamplinJ Procedures 21

61 SamplinJ Location and Frequency 21 62 SamplinJ Procedures 21

70 Sample ClisOdy 21

80 Calibnrion Procedures 22

90 Analytical Procedures bullbull bull 24

100 Data Reduction Validuion and Rcponina 24

101 Data Reduction 24 102 Data Validarion 26 103 Aow and Reponina of Data and Responsible Staff for Data 26

11 0 Internal Quality Control Checks 28

111 Blank Samples bull bull 28 11 2 Replicate Samples 30 113 Spiked Samples bull ll 11 4 Standards ll

Artlur D Little

-n = = c-

- r I

RtviSion No I Paae 4 of 33

Quauy Anurpoundnce Project Plan for Plclllo Fann July 9 1990

Pogo

12 0 Pcrfomance and Systems Audus 31

130 Prtventative Mamtenance 32

140 Specific Rouune Procedures Uitd to Assess Data Precis1on Accuracy and Completeneu 32

UO Corrective Actions 32

160 Quality Auurance Repons to Mana1ement 32

Uat Of uret

3middot1 Project Schedule 7 4middot1 Project Oraanizanonal Structure 17 101 Aow From Colleclion of Raw Data Throuah Storaae 21

3middot 1 Parame1en to be Tested II

3middot3 Taract Compound List for Volatile Oraanics in Monitorinamp Wells

3middot4 Soil Gas Survey Analysis I

14-1 Quality Conttol Samples Analyzed to Prod uce Re sults for

3-2 Volatile Oraanics for Anal ysis in Private Wells Usina Method j242 12

Usina a RAS Method 14

1 -1 Data Qualiry Objectives for Critica l Measuremems 19 8middot 1 Calibration Procedures and Frequency 23 9middot 1 Labontory and Field Analyrical Procedures 25

Statistical Calculations 33

Artlur Ill Little

- r -

Qualuy Assu rance ProJeCt Plan for Plctllo fum July 9 1990

Remion No I Papl of JJ

30 oiect DeltCrlptlon

31 Protect Objective and Seope Stlltmtnt

A description of the Picbullllo Fum ue and bteklound information about the st te is Jiven in Section 10 of the F1cld SamplinJ Plan (June 22 1990) A more complete descriplion of the prOJCCI ObJCCUoC IS Jiven Ln the final Work Plan IUIFS PiciUo Fum S11e Town of Co cntty Rhode Island ~ January 1990 prepared for EPA ReJion I by Ebasco Scrvtces Inc (Th1s document w11l be rcfemd to u the Ebasco Wort Plan throuahout thiS QAPjP)

This PicUio Farm site has an emiddotdendtd hmory of prior invcstiaations ~ctcd 11 dileftte eltmenu of site remediation This RlFS is desianed to provide the basis fot complete remediation of any resbulldual onsile or related offsite contamination pruenrina risk to pubhc health or the environment To meet this ovell project objective the Ebasco Work Plan div1ded the first pan of the field invesliaadon Into rwo subphases (lA and 18) A Phue n proJTim will be desianed and lmplcmenled u necessary llus QAPjP addrtues only Phase lA The project scheclule is shown in Fiaure 3- I

The specific Phase IA tasks are

Task 1 -- Project Plannina

11 -- Work Plan 12 -- Field Operations Plln 13 -- Project Meerinas 14 middotmiddot Site Visit

Task 2 -- Community Relations

Task 3 -- Field lnvesriaarion

31 bullbull Mobiliution 32 -- Private Well Inventory and Samplina 33 -- Monitorina (EIIisrinamp) Well Inventory Development and Samplinamp 34 -- Field Reconnaissance 31 bullbull Macnetorneter Survey 36 -- Seismic Survey 37 -- Soil Gas Screenina 38 --Elevation Survey 310 middotmiddot Biota Survey 311 bullbull Monthly Water Level Measurements

Tuk 4 -- Sample AnalysisValidation

Tuk I -middot Data EvaluationPreparation of Technical Directive Memorandum

Artlur D Little

I r I

Quahty Assurance Projtct Plan fOt Plc1llo Farm July 9 1990

Revis1on No I Paae 6 of 33

Specitk project objecuves for the aboe tasks are Jlvtn in the Anhur D Ltttle Interim Work Pan This QAPJP IS plaquoLfically concerned With ICUVUICJ In suppon of Tasks 3 and 4 and pro bulldes the necessary detuled procedures for 1mplemenrinJ Phase lA tO meet the project obJtclives

1lle overaU project objtcnvc for Phase lA is to provbullde a prcliminuy assessment of the cumnt conditions at the sue and to provuJe surtcicnt 1nfonnalion tO expand or modify u necessary Phase 18 as awen in the Ebuco Work Plan A Phase U may be necessary dtprndina on whether Phase lA and 18 rcsulu indicale a ~ed for further data aatherinJ and evaluauon The ovcrampJI objtcdvc combination of these pflascs n to provide a surricLent database for environmenlll chUICteriurion risk assessment and source control and manaJement of micrauon nmedial ahemarives evaluation

Artlur D LJttJe 62J1AJIC1lll

r -middot-

bull

111 1middotmiddot1middot

lt

~

bull

bull u

-

bull

ArtJurD

Little

I r I

Qulluy Assurance ProJeCt Plan for Piclilo Fann July 9 1990

Revision No I Pace I of 33

U Dolo Ollf Otgtjecllvoo (DOOt)

A detailed discusuon is Jiven 1n the Ebasco Wort Plan of the data Jlps prKhKlinJ complcrion of the fctiSlbLiuy study and data quality objecdvcs related to the data needed 10 fill those aaps A brief summary of 0Q0s in support of Task l Field lnvcuiaarion activ111es 11 presented here

Activity 0111 Ou1llty Objective

32 Private Well lnvcnrory NA (field)

Private Well SamplinampAnalysis Level V (SAS) of Method 524 VOAs pH Level n (field pH temp cond) Temp Cond

33 Monitorina Well lnvcn10ry NA ~

Monltorin1 Well Samplinampf Level IV (RAS) Analysis of TCL VOAs plus I 0 Level n (field pH temp cond) n-TICs pH Temp Cond = 34 Field Reconnaissance NA (field) =

3 Maanetometcr Survey NA (field) 36 Stismic Survey NA (field)

37 Soil Gas ScrecninJ Level n (field) of toluene m-xylene (or accwne) methylene chloride 111 -trichlorethane trichloroethylene

38 EleVation Survey NA (tield)

310 Biota Survey NA (fie ld)

Health and Safe[) Suppon Levell (field)

HNu PID Draeaer 1ubts Explosivity Radiarion

r

)

Qualuy Assurance ProJeCt Plan for Ptctlo Fum Jul y 9 1990

Re vbullsbullon No I Paac 9 of J3

33 Monttortng Network Dtslgn AIIIOMII and Parameters

A discussion of the Phase lA monuonnc netork lllld the rationaJe behind tluu net work is Jlven tn Secuon a 3 I and 2 3 3 of the Ebasco Work Plan 11d bnd ly summan zed below SamphnJ tocauons and frequency an Jiven in Section 3 0 of the Field SamplinJ Plan The paraflltters to be tested (and corru pondinJ (teld and field QC samples) for subtaslu 3 2 bull Pnvate Wells 33 bullbull Monilorina Wells and 37 bullbull SoH Gas Surveys ~ summ1nzcd to Tables 3-1 lhrouamph 3middot4

SUbtak 32 PriVIIe Wells Thirteen private wells wtll be sampled and mnalyzed for the volarilc oraanics Ji ven in Table 3-2 plus ten temamely tdcnnficd compounds (TICs) by Method j 242 in Methods for the Os tennjnauon of Ornmc ComooundJ jn Drinkjna Wttcr EPA4-881039 to assess tf com~mmauon t )(ists Wells will be selected based on their susetptibility 10 comaminanon and avaJhtbJiity usinamp the private well inventory and if ava1lable RI OEM data The analyses are ~stricted to volatiles since past efforts indicated that these contaminants were at levels Jrtater than 1 m~ 1M limitation of resmcuna the analyses to volatiles is that acidbaseneutral semivolalile oraamcs pe nicides and inoraanic1 may aavel throuah lhe aquifer differenliy than the volatiles these will not be found since they ampR not beina analyzed fOf

SubteM 33 Monitoring Wtlll Thirty-seven uistina wells will be s~tmpled and anal yzed for volatiles on the TamprJet Compound List (TCL Table 3middot3) plus ten tentatively identified compoundJ (TICs) by the US EPA Contrlct Laboratory ProJram (ClP) routine anaJytical services (RAS ) volatiles method Th1s is beina done to assess cuntnt contamination Well s will be selected based on their serviceabi lity detcnnined durinJ the inventory As noted above for the private wells the study is limited 10 volatiles

Sublbullk 34 llld Rtconnbulllaunct This study will cover approx imately two square mile s centered on the oriainal disposal site at Picillo Farm and will also include assessment of existina information 1M tield portion of this work is directed towards aeoloampical field mappina and localina surface water samples These effons are directed towards rttinina Phase 18 activities includi namp the location of surface water samples and detenninina the inn uence of bedrock structure on around water movement The two squ~ miles encompasses the entire site and in combination with existinamp infonnation such as the EPIC air photoampraphs aeoloaicaJ maps tOpoJTlphic maps and aeoloaical repons sufficiently cover the site to locate geolopcal and surface water features that may be suscepuble to contamination on the site

Subtask 35 aonetomettr Survey The maanetometer surve y w11l be conducted over the emire project area to seanh for buried steel drums tanks or other ferrous debris that could indicate additional wute burial sites nm discovered during previous remedial invesriJations Eiaht areu were identified as potential waste burial sites from EPIC air photos by Ebasco These mas will be surveyed usinamp the fo llowina arid spacinas 40 feet

Artlur D Little 6Z3SlARCOll

I r I

Qualuy As ura nct ProjtCI Pan (Of P1c1Uo Farm July 9 1990

Revision No I Paae 3 of 33

20 Tlble of Contntt

10 Title Paae

11 Foreword

20 Table or Concencs

JO Project Description

31 Project Objective and Scope Statment 32 Dall Qualicy Objectives 33 MonhorinJ Network Deslan Rationale and Parametcn

40 Projecc Oraaniza1ion and Responsibility 16

50 Data Quali ty Objectives for Critical Measu~ments in Tcnru of Precision Accur~ey Completeness Representativeness and Comparability II

51 Summary 18 52 Re~sentativencss middotmiddotbullmiddotmiddotmiddotmiddotmiddotmiddotmiddot 1853 Comparability bull bull bull bull bull bull bull bull 18

60 SamplinJ Procedures 21

61 SamplinJ Location and Frequency 21 62 SamplinJ Procedures 21

70 Sample ClisOdy 21

80 Calibnrion Procedures 22

90 Analytical Procedures bullbull bull 24

100 Data Reduction Validuion and Rcponina 24

101 Data Reduction 24 102 Data Validarion 26 103 Aow and Reponina of Data and Responsible Staff for Data 26

11 0 Internal Quality Control Checks 28

111 Blank Samples bull bull 28 11 2 Replicate Samples 30 113 Spiked Samples bull ll 11 4 Standards ll

Artlur D Little

-n = = c-

- r I

RtviSion No I Paae 4 of 33

Quauy Anurpoundnce Project Plan for Plclllo Fann July 9 1990

Pogo

12 0 Pcrfomance and Systems Audus 31

130 Prtventative Mamtenance 32

140 Specific Rouune Procedures Uitd to Assess Data Precis1on Accuracy and Completeneu 32

UO Corrective Actions 32

160 Quality Auurance Repons to Mana1ement 32

Uat Of uret

3middot1 Project Schedule 7 4middot1 Project Oraanizanonal Structure 17 101 Aow From Colleclion of Raw Data Throuah Storaae 21

3middot 1 Parame1en to be Tested II

3middot3 Taract Compound List for Volatile Oraanics in Monitorinamp Wells

3middot4 Soil Gas Survey Analysis I

14-1 Quality Conttol Samples Analyzed to Prod uce Re sults for

3-2 Volatile Oraanics for Anal ysis in Private Wells Usina Method j242 12

Usina a RAS Method 14

1 -1 Data Qualiry Objectives for Critica l Measuremems 19 8middot 1 Calibration Procedures and Frequency 23 9middot 1 Labontory and Field Analyrical Procedures 25

Statistical Calculations 33

Artlur Ill Little

- r -

Qualuy Assu rance ProJeCt Plan for Plctllo fum July 9 1990

Remion No I Papl of JJ

30 oiect DeltCrlptlon

31 Protect Objective and Seope Stlltmtnt

A description of the Picbullllo Fum ue and bteklound information about the st te is Jiven in Section 10 of the F1cld SamplinJ Plan (June 22 1990) A more complete descriplion of the prOJCCI ObJCCUoC IS Jiven Ln the final Work Plan IUIFS PiciUo Fum S11e Town of Co cntty Rhode Island ~ January 1990 prepared for EPA ReJion I by Ebasco Scrvtces Inc (Th1s document w11l be rcfemd to u the Ebasco Wort Plan throuahout thiS QAPjP)

This PicUio Farm site has an emiddotdendtd hmory of prior invcstiaations ~ctcd 11 dileftte eltmenu of site remediation This RlFS is desianed to provide the basis fot complete remediation of any resbulldual onsile or related offsite contamination pruenrina risk to pubhc health or the environment To meet this ovell project objective the Ebasco Work Plan div1ded the first pan of the field invesliaadon Into rwo subphases (lA and 18) A Phue n proJTim will be desianed and lmplcmenled u necessary llus QAPjP addrtues only Phase lA The project scheclule is shown in Fiaure 3- I

The specific Phase IA tasks are

Task 1 -- Project Plannina

11 -- Work Plan 12 -- Field Operations Plln 13 -- Project Meerinas 14 middotmiddot Site Visit

Task 2 -- Community Relations

Task 3 -- Field lnvesriaarion

31 bullbull Mobiliution 32 -- Private Well Inventory and Samplina 33 -- Monitorina (EIIisrinamp) Well Inventory Development and Samplinamp 34 -- Field Reconnaissance 31 bullbull Macnetorneter Survey 36 -- Seismic Survey 37 -- Soil Gas Screenina 38 --Elevation Survey 310 middotmiddot Biota Survey 311 bullbull Monthly Water Level Measurements

Tuk 4 -- Sample AnalysisValidation

Tuk I -middot Data EvaluationPreparation of Technical Directive Memorandum

Artlur D Little

I r I

Quahty Assurance Projtct Plan fOt Plc1llo Farm July 9 1990

Revis1on No I Paae 6 of 33

Specitk project objecuves for the aboe tasks are Jlvtn in the Anhur D Ltttle Interim Work Pan This QAPJP IS plaquoLfically concerned With ICUVUICJ In suppon of Tasks 3 and 4 and pro bulldes the necessary detuled procedures for 1mplemenrinJ Phase lA tO meet the project obJtclives

1lle overaU project objtcnvc for Phase lA is to provbullde a prcliminuy assessment of the cumnt conditions at the sue and to provuJe surtcicnt 1nfonnalion tO expand or modify u necessary Phase 18 as awen in the Ebuco Work Plan A Phase U may be necessary dtprndina on whether Phase lA and 18 rcsulu indicale a ~ed for further data aatherinJ and evaluauon The ovcrampJI objtcdvc combination of these pflascs n to provide a surricLent database for environmenlll chUICteriurion risk assessment and source control and manaJement of micrauon nmedial ahemarives evaluation

Artlur D LJttJe 62J1AJIC1lll

r -middot-

bull

111 1middotmiddot1middot

lt

~

bull

bull u

-

bull

ArtJurD

Little

I r I

Qulluy Assurance ProJeCt Plan for Piclilo Fann July 9 1990

Revision No I Pace I of 33

U Dolo Ollf Otgtjecllvoo (DOOt)

A detailed discusuon is Jiven 1n the Ebasco Wort Plan of the data Jlps prKhKlinJ complcrion of the fctiSlbLiuy study and data quality objecdvcs related to the data needed 10 fill those aaps A brief summary of 0Q0s in support of Task l Field lnvcuiaarion activ111es 11 presented here

Activity 0111 Ou1llty Objective

32 Private Well lnvcnrory NA (field)

Private Well SamplinampAnalysis Level V (SAS) of Method 524 VOAs pH Level n (field pH temp cond) Temp Cond

33 Monitorina Well lnvcn10ry NA ~

Monltorin1 Well Samplinampf Level IV (RAS) Analysis of TCL VOAs plus I 0 Level n (field pH temp cond) n-TICs pH Temp Cond = 34 Field Reconnaissance NA (field) =

3 Maanetometcr Survey NA (field) 36 Stismic Survey NA (field)

37 Soil Gas ScrecninJ Level n (field) of toluene m-xylene (or accwne) methylene chloride 111 -trichlorethane trichloroethylene

38 EleVation Survey NA (tield)

310 Biota Survey NA (fie ld)

Health and Safe[) Suppon Levell (field)

HNu PID Draeaer 1ubts Explosivity Radiarion

r

)

Qualuy Assurance ProJeCt Plan for Ptctlo Fum Jul y 9 1990

Re vbullsbullon No I Paac 9 of J3

33 Monttortng Network Dtslgn AIIIOMII and Parameters

A discussion of the Phase lA monuonnc netork lllld the rationaJe behind tluu net work is Jlven tn Secuon a 3 I and 2 3 3 of the Ebasco Work Plan 11d bnd ly summan zed below SamphnJ tocauons and frequency an Jiven in Section 3 0 of the Field SamplinJ Plan The paraflltters to be tested (and corru pondinJ (teld and field QC samples) for subtaslu 3 2 bull Pnvate Wells 33 bullbull Monilorina Wells and 37 bullbull SoH Gas Surveys ~ summ1nzcd to Tables 3-1 lhrouamph 3middot4

SUbtak 32 PriVIIe Wells Thirteen private wells wtll be sampled and mnalyzed for the volarilc oraanics Ji ven in Table 3-2 plus ten temamely tdcnnficd compounds (TICs) by Method j 242 in Methods for the Os tennjnauon of Ornmc ComooundJ jn Drinkjna Wttcr EPA4-881039 to assess tf com~mmauon t )(ists Wells will be selected based on their susetptibility 10 comaminanon and avaJhtbJiity usinamp the private well inventory and if ava1lable RI OEM data The analyses are ~stricted to volatiles since past efforts indicated that these contaminants were at levels Jrtater than 1 m~ 1M limitation of resmcuna the analyses to volatiles is that acidbaseneutral semivolalile oraamcs pe nicides and inoraanic1 may aavel throuah lhe aquifer differenliy than the volatiles these will not be found since they ampR not beina analyzed fOf

SubteM 33 Monitoring Wtlll Thirty-seven uistina wells will be s~tmpled and anal yzed for volatiles on the TamprJet Compound List (TCL Table 3middot3) plus ten tentatively identified compoundJ (TICs) by the US EPA Contrlct Laboratory ProJram (ClP) routine anaJytical services (RAS ) volatiles method Th1s is beina done to assess cuntnt contamination Well s will be selected based on their serviceabi lity detcnnined durinJ the inventory As noted above for the private wells the study is limited 10 volatiles

Sublbullk 34 llld Rtconnbulllaunct This study will cover approx imately two square mile s centered on the oriainal disposal site at Picillo Farm and will also include assessment of existina information 1M tield portion of this work is directed towards aeoloampical field mappina and localina surface water samples These effons are directed towards rttinina Phase 18 activities includi namp the location of surface water samples and detenninina the inn uence of bedrock structure on around water movement The two squ~ miles encompasses the entire site and in combination with existinamp infonnation such as the EPIC air photoampraphs aeoloaicaJ maps tOpoJTlphic maps and aeoloaical repons sufficiently cover the site to locate geolopcal and surface water features that may be suscepuble to contamination on the site

Subtask 35 aonetomettr Survey The maanetometer surve y w11l be conducted over the emire project area to seanh for buried steel drums tanks or other ferrous debris that could indicate additional wute burial sites nm discovered during previous remedial invesriJations Eiaht areu were identified as potential waste burial sites from EPIC air photos by Ebasco These mas will be surveyed usinamp the fo llowina arid spacinas 40 feet

Artlur D Little 6Z3SlARCOll

- r I

RtviSion No I Paae 4 of 33

Quauy Anurpoundnce Project Plan for Plclllo Fann July 9 1990

Pogo

12 0 Pcrfomance and Systems Audus 31

130 Prtventative Mamtenance 32

140 Specific Rouune Procedures Uitd to Assess Data Precis1on Accuracy and Completeneu 32

UO Corrective Actions 32

160 Quality Auurance Repons to Mana1ement 32

Uat Of uret

3middot1 Project Schedule 7 4middot1 Project Oraanizanonal Structure 17 101 Aow From Colleclion of Raw Data Throuah Storaae 21

3middot 1 Parame1en to be Tested II

3middot3 Taract Compound List for Volatile Oraanics in Monitorinamp Wells

3middot4 Soil Gas Survey Analysis I

14-1 Quality Conttol Samples Analyzed to Prod uce Re sults for

3-2 Volatile Oraanics for Anal ysis in Private Wells Usina Method j242 12

Usina a RAS Method 14

1 -1 Data Qualiry Objectives for Critica l Measuremems 19 8middot 1 Calibration Procedures and Frequency 23 9middot 1 Labontory and Field Analyrical Procedures 25

Statistical Calculations 33

Artlur Ill Little

- r -

Qualuy Assu rance ProJeCt Plan for Plctllo fum July 9 1990

Remion No I Papl of JJ

30 oiect DeltCrlptlon

31 Protect Objective and Seope Stlltmtnt

A description of the Picbullllo Fum ue and bteklound information about the st te is Jiven in Section 10 of the F1cld SamplinJ Plan (June 22 1990) A more complete descriplion of the prOJCCI ObJCCUoC IS Jiven Ln the final Work Plan IUIFS PiciUo Fum S11e Town of Co cntty Rhode Island ~ January 1990 prepared for EPA ReJion I by Ebasco Scrvtces Inc (Th1s document w11l be rcfemd to u the Ebasco Wort Plan throuahout thiS QAPjP)

This PicUio Farm site has an emiddotdendtd hmory of prior invcstiaations ~ctcd 11 dileftte eltmenu of site remediation This RlFS is desianed to provide the basis fot complete remediation of any resbulldual onsile or related offsite contamination pruenrina risk to pubhc health or the environment To meet this ovell project objective the Ebasco Work Plan div1ded the first pan of the field invesliaadon Into rwo subphases (lA and 18) A Phue n proJTim will be desianed and lmplcmenled u necessary llus QAPjP addrtues only Phase lA The project scheclule is shown in Fiaure 3- I

The specific Phase IA tasks are

Task 1 -- Project Plannina

11 -- Work Plan 12 -- Field Operations Plln 13 -- Project Meerinas 14 middotmiddot Site Visit

Task 2 -- Community Relations

Task 3 -- Field lnvesriaarion

31 bullbull Mobiliution 32 -- Private Well Inventory and Samplina 33 -- Monitorina (EIIisrinamp) Well Inventory Development and Samplinamp 34 -- Field Reconnaissance 31 bullbull Macnetorneter Survey 36 -- Seismic Survey 37 -- Soil Gas Screenina 38 --Elevation Survey 310 middotmiddot Biota Survey 311 bullbull Monthly Water Level Measurements

Tuk 4 -- Sample AnalysisValidation

Tuk I -middot Data EvaluationPreparation of Technical Directive Memorandum

Artlur D Little

I r I

Quahty Assurance Projtct Plan fOt Plc1llo Farm July 9 1990

Revis1on No I Paae 6 of 33

Specitk project objecuves for the aboe tasks are Jlvtn in the Anhur D Ltttle Interim Work Pan This QAPJP IS plaquoLfically concerned With ICUVUICJ In suppon of Tasks 3 and 4 and pro bulldes the necessary detuled procedures for 1mplemenrinJ Phase lA tO meet the project obJtclives

1lle overaU project objtcnvc for Phase lA is to provbullde a prcliminuy assessment of the cumnt conditions at the sue and to provuJe surtcicnt 1nfonnalion tO expand or modify u necessary Phase 18 as awen in the Ebuco Work Plan A Phase U may be necessary dtprndina on whether Phase lA and 18 rcsulu indicale a ~ed for further data aatherinJ and evaluauon The ovcrampJI objtcdvc combination of these pflascs n to provide a surricLent database for environmenlll chUICteriurion risk assessment and source control and manaJement of micrauon nmedial ahemarives evaluation

Artlur D LJttJe 62J1AJIC1lll

r -middot-

bull

111 1middotmiddot1middot

lt

~

bull

bull u

-

bull

ArtJurD

Little

I r I

Qulluy Assurance ProJeCt Plan for Piclilo Fann July 9 1990

Revision No I Pace I of 33

U Dolo Ollf Otgtjecllvoo (DOOt)

A detailed discusuon is Jiven 1n the Ebasco Wort Plan of the data Jlps prKhKlinJ complcrion of the fctiSlbLiuy study and data quality objecdvcs related to the data needed 10 fill those aaps A brief summary of 0Q0s in support of Task l Field lnvcuiaarion activ111es 11 presented here

Activity 0111 Ou1llty Objective

32 Private Well lnvcnrory NA (field)

Private Well SamplinampAnalysis Level V (SAS) of Method 524 VOAs pH Level n (field pH temp cond) Temp Cond

33 Monitorina Well lnvcn10ry NA ~

Monltorin1 Well Samplinampf Level IV (RAS) Analysis of TCL VOAs plus I 0 Level n (field pH temp cond) n-TICs pH Temp Cond = 34 Field Reconnaissance NA (field) =

3 Maanetometcr Survey NA (field) 36 Stismic Survey NA (field)

37 Soil Gas ScrecninJ Level n (field) of toluene m-xylene (or accwne) methylene chloride 111 -trichlorethane trichloroethylene

38 EleVation Survey NA (tield)

310 Biota Survey NA (fie ld)

Health and Safe[) Suppon Levell (field)

HNu PID Draeaer 1ubts Explosivity Radiarion

r

)

Qualuy Assurance ProJeCt Plan for Ptctlo Fum Jul y 9 1990

Re vbullsbullon No I Paac 9 of J3

33 Monttortng Network Dtslgn AIIIOMII and Parameters

A discussion of the Phase lA monuonnc netork lllld the rationaJe behind tluu net work is Jlven tn Secuon a 3 I and 2 3 3 of the Ebasco Work Plan 11d bnd ly summan zed below SamphnJ tocauons and frequency an Jiven in Section 3 0 of the Field SamplinJ Plan The paraflltters to be tested (and corru pondinJ (teld and field QC samples) for subtaslu 3 2 bull Pnvate Wells 33 bullbull Monilorina Wells and 37 bullbull SoH Gas Surveys ~ summ1nzcd to Tables 3-1 lhrouamph 3middot4

SUbtak 32 PriVIIe Wells Thirteen private wells wtll be sampled and mnalyzed for the volarilc oraanics Ji ven in Table 3-2 plus ten temamely tdcnnficd compounds (TICs) by Method j 242 in Methods for the Os tennjnauon of Ornmc ComooundJ jn Drinkjna Wttcr EPA4-881039 to assess tf com~mmauon t )(ists Wells will be selected based on their susetptibility 10 comaminanon and avaJhtbJiity usinamp the private well inventory and if ava1lable RI OEM data The analyses are ~stricted to volatiles since past efforts indicated that these contaminants were at levels Jrtater than 1 m~ 1M limitation of resmcuna the analyses to volatiles is that acidbaseneutral semivolalile oraamcs pe nicides and inoraanic1 may aavel throuah lhe aquifer differenliy than the volatiles these will not be found since they ampR not beina analyzed fOf

SubteM 33 Monitoring Wtlll Thirty-seven uistina wells will be s~tmpled and anal yzed for volatiles on the TamprJet Compound List (TCL Table 3middot3) plus ten tentatively identified compoundJ (TICs) by the US EPA Contrlct Laboratory ProJram (ClP) routine anaJytical services (RAS ) volatiles method Th1s is beina done to assess cuntnt contamination Well s will be selected based on their serviceabi lity detcnnined durinJ the inventory As noted above for the private wells the study is limited 10 volatiles

Sublbullk 34 llld Rtconnbulllaunct This study will cover approx imately two square mile s centered on the oriainal disposal site at Picillo Farm and will also include assessment of existina information 1M tield portion of this work is directed towards aeoloampical field mappina and localina surface water samples These effons are directed towards rttinina Phase 18 activities includi namp the location of surface water samples and detenninina the inn uence of bedrock structure on around water movement The two squ~ miles encompasses the entire site and in combination with existinamp infonnation such as the EPIC air photoampraphs aeoloaicaJ maps tOpoJTlphic maps and aeoloaical repons sufficiently cover the site to locate geolopcal and surface water features that may be suscepuble to contamination on the site

Subtask 35 aonetomettr Survey The maanetometer surve y w11l be conducted over the emire project area to seanh for buried steel drums tanks or other ferrous debris that could indicate additional wute burial sites nm discovered during previous remedial invesriJations Eiaht areu were identified as potential waste burial sites from EPIC air photos by Ebasco These mas will be surveyed usinamp the fo llowina arid spacinas 40 feet

Artlur D Little 6Z3SlARCOll

- r -

Qualuy Assu rance ProJeCt Plan for Plctllo fum July 9 1990

Remion No I Papl of JJ

30 oiect DeltCrlptlon

31 Protect Objective and Seope Stlltmtnt

A description of the Picbullllo Fum ue and bteklound information about the st te is Jiven in Section 10 of the F1cld SamplinJ Plan (June 22 1990) A more complete descriplion of the prOJCCI ObJCCUoC IS Jiven Ln the final Work Plan IUIFS PiciUo Fum S11e Town of Co cntty Rhode Island ~ January 1990 prepared for EPA ReJion I by Ebasco Scrvtces Inc (Th1s document w11l be rcfemd to u the Ebasco Wort Plan throuahout thiS QAPjP)

This PicUio Farm site has an emiddotdendtd hmory of prior invcstiaations ~ctcd 11 dileftte eltmenu of site remediation This RlFS is desianed to provide the basis fot complete remediation of any resbulldual onsile or related offsite contamination pruenrina risk to pubhc health or the environment To meet this ovell project objective the Ebasco Work Plan div1ded the first pan of the field invesliaadon Into rwo subphases (lA and 18) A Phue n proJTim will be desianed and lmplcmenled u necessary llus QAPjP addrtues only Phase lA The project scheclule is shown in Fiaure 3- I

The specific Phase IA tasks are

Task 1 -- Project Plannina

11 -- Work Plan 12 -- Field Operations Plln 13 -- Project Meerinas 14 middotmiddot Site Visit

Task 2 -- Community Relations

Task 3 -- Field lnvesriaarion

31 bullbull Mobiliution 32 -- Private Well Inventory and Samplina 33 -- Monitorina (EIIisrinamp) Well Inventory Development and Samplinamp 34 -- Field Reconnaissance 31 bullbull Macnetorneter Survey 36 -- Seismic Survey 37 -- Soil Gas Screenina 38 --Elevation Survey 310 middotmiddot Biota Survey 311 bullbull Monthly Water Level Measurements

Tuk 4 -- Sample AnalysisValidation

Tuk I -middot Data EvaluationPreparation of Technical Directive Memorandum

Artlur D Little

I r I

Quahty Assurance Projtct Plan fOt Plc1llo Farm July 9 1990

Revis1on No I Paae 6 of 33

Specitk project objecuves for the aboe tasks are Jlvtn in the Anhur D Ltttle Interim Work Pan This QAPJP IS plaquoLfically concerned With ICUVUICJ In suppon of Tasks 3 and 4 and pro bulldes the necessary detuled procedures for 1mplemenrinJ Phase lA tO meet the project obJtclives

1lle overaU project objtcnvc for Phase lA is to provbullde a prcliminuy assessment of the cumnt conditions at the sue and to provuJe surtcicnt 1nfonnalion tO expand or modify u necessary Phase 18 as awen in the Ebuco Work Plan A Phase U may be necessary dtprndina on whether Phase lA and 18 rcsulu indicale a ~ed for further data aatherinJ and evaluauon The ovcrampJI objtcdvc combination of these pflascs n to provide a surricLent database for environmenlll chUICteriurion risk assessment and source control and manaJement of micrauon nmedial ahemarives evaluation

Artlur D LJttJe 62J1AJIC1lll

r -middot-

bull

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lt

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bull

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bull

ArtJurD

Little

I r I

Qulluy Assurance ProJeCt Plan for Piclilo Fann July 9 1990

Revision No I Pace I of 33

U Dolo Ollf Otgtjecllvoo (DOOt)

A detailed discusuon is Jiven 1n the Ebasco Wort Plan of the data Jlps prKhKlinJ complcrion of the fctiSlbLiuy study and data quality objecdvcs related to the data needed 10 fill those aaps A brief summary of 0Q0s in support of Task l Field lnvcuiaarion activ111es 11 presented here

Activity 0111 Ou1llty Objective

32 Private Well lnvcnrory NA (field)

Private Well SamplinampAnalysis Level V (SAS) of Method 524 VOAs pH Level n (field pH temp cond) Temp Cond

33 Monitorina Well lnvcn10ry NA ~

Monltorin1 Well Samplinampf Level IV (RAS) Analysis of TCL VOAs plus I 0 Level n (field pH temp cond) n-TICs pH Temp Cond = 34 Field Reconnaissance NA (field) =

3 Maanetometcr Survey NA (field) 36 Stismic Survey NA (field)

37 Soil Gas ScrecninJ Level n (field) of toluene m-xylene (or accwne) methylene chloride 111 -trichlorethane trichloroethylene

38 EleVation Survey NA (tield)

310 Biota Survey NA (fie ld)

Health and Safe[) Suppon Levell (field)

HNu PID Draeaer 1ubts Explosivity Radiarion

r

)

Qualuy Assurance ProJeCt Plan for Ptctlo Fum Jul y 9 1990

Re vbullsbullon No I Paac 9 of J3

33 Monttortng Network Dtslgn AIIIOMII and Parameters

A discussion of the Phase lA monuonnc netork lllld the rationaJe behind tluu net work is Jlven tn Secuon a 3 I and 2 3 3 of the Ebasco Work Plan 11d bnd ly summan zed below SamphnJ tocauons and frequency an Jiven in Section 3 0 of the Field SamplinJ Plan The paraflltters to be tested (and corru pondinJ (teld and field QC samples) for subtaslu 3 2 bull Pnvate Wells 33 bullbull Monilorina Wells and 37 bullbull SoH Gas Surveys ~ summ1nzcd to Tables 3-1 lhrouamph 3middot4

SUbtak 32 PriVIIe Wells Thirteen private wells wtll be sampled and mnalyzed for the volarilc oraanics Ji ven in Table 3-2 plus ten temamely tdcnnficd compounds (TICs) by Method j 242 in Methods for the Os tennjnauon of Ornmc ComooundJ jn Drinkjna Wttcr EPA4-881039 to assess tf com~mmauon t )(ists Wells will be selected based on their susetptibility 10 comaminanon and avaJhtbJiity usinamp the private well inventory and if ava1lable RI OEM data The analyses are ~stricted to volatiles since past efforts indicated that these contaminants were at levels Jrtater than 1 m~ 1M limitation of resmcuna the analyses to volatiles is that acidbaseneutral semivolalile oraamcs pe nicides and inoraanic1 may aavel throuah lhe aquifer differenliy than the volatiles these will not be found since they ampR not beina analyzed fOf

SubteM 33 Monitoring Wtlll Thirty-seven uistina wells will be s~tmpled and anal yzed for volatiles on the TamprJet Compound List (TCL Table 3middot3) plus ten tentatively identified compoundJ (TICs) by the US EPA Contrlct Laboratory ProJram (ClP) routine anaJytical services (RAS ) volatiles method Th1s is beina done to assess cuntnt contamination Well s will be selected based on their serviceabi lity detcnnined durinJ the inventory As noted above for the private wells the study is limited 10 volatiles

Sublbullk 34 llld Rtconnbulllaunct This study will cover approx imately two square mile s centered on the oriainal disposal site at Picillo Farm and will also include assessment of existina information 1M tield portion of this work is directed towards aeoloampical field mappina and localina surface water samples These effons are directed towards rttinina Phase 18 activities includi namp the location of surface water samples and detenninina the inn uence of bedrock structure on around water movement The two squ~ miles encompasses the entire site and in combination with existinamp infonnation such as the EPIC air photoampraphs aeoloaicaJ maps tOpoJTlphic maps and aeoloaical repons sufficiently cover the site to locate geolopcal and surface water features that may be suscepuble to contamination on the site

Subtask 35 aonetomettr Survey The maanetometer surve y w11l be conducted over the emire project area to seanh for buried steel drums tanks or other ferrous debris that could indicate additional wute burial sites nm discovered during previous remedial invesriJations Eiaht areu were identified as potential waste burial sites from EPIC air photos by Ebasco These mas will be surveyed usinamp the fo llowina arid spacinas 40 feet

Artlur D Little 6Z3SlARCOll

I r I

Quahty Assurance Projtct Plan fOt Plc1llo Farm July 9 1990

Revis1on No I Paae 6 of 33

Specitk project objecuves for the aboe tasks are Jlvtn in the Anhur D Ltttle Interim Work Pan This QAPJP IS plaquoLfically concerned With ICUVUICJ In suppon of Tasks 3 and 4 and pro bulldes the necessary detuled procedures for 1mplemenrinJ Phase lA tO meet the project obJtclives

1lle overaU project objtcnvc for Phase lA is to provbullde a prcliminuy assessment of the cumnt conditions at the sue and to provuJe surtcicnt 1nfonnalion tO expand or modify u necessary Phase 18 as awen in the Ebuco Work Plan A Phase U may be necessary dtprndina on whether Phase lA and 18 rcsulu indicale a ~ed for further data aatherinJ and evaluauon The ovcrampJI objtcdvc combination of these pflascs n to provide a surricLent database for environmenlll chUICteriurion risk assessment and source control and manaJement of micrauon nmedial ahemarives evaluation

Artlur D LJttJe 62J1AJIC1lll

r -middot-

bull

111 1middotmiddot1middot

lt

~

bull

bull u

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bull

ArtJurD

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I r I

Qulluy Assurance ProJeCt Plan for Piclilo Fann July 9 1990

Revision No I Pace I of 33

U Dolo Ollf Otgtjecllvoo (DOOt)

A detailed discusuon is Jiven 1n the Ebasco Wort Plan of the data Jlps prKhKlinJ complcrion of the fctiSlbLiuy study and data quality objecdvcs related to the data needed 10 fill those aaps A brief summary of 0Q0s in support of Task l Field lnvcuiaarion activ111es 11 presented here

Activity 0111 Ou1llty Objective

32 Private Well lnvcnrory NA (field)

Private Well SamplinampAnalysis Level V (SAS) of Method 524 VOAs pH Level n (field pH temp cond) Temp Cond

33 Monitorina Well lnvcn10ry NA ~

Monltorin1 Well Samplinampf Level IV (RAS) Analysis of TCL VOAs plus I 0 Level n (field pH temp cond) n-TICs pH Temp Cond = 34 Field Reconnaissance NA (field) =

3 Maanetometcr Survey NA (field) 36 Stismic Survey NA (field)

37 Soil Gas ScrecninJ Level n (field) of toluene m-xylene (or accwne) methylene chloride 111 -trichlorethane trichloroethylene

38 EleVation Survey NA (tield)

310 Biota Survey NA (fie ld)

Health and Safe[) Suppon Levell (field)

HNu PID Draeaer 1ubts Explosivity Radiarion

r

)

Qualuy Assurance ProJeCt Plan for Ptctlo Fum Jul y 9 1990

Re vbullsbullon No I Paac 9 of J3

33 Monttortng Network Dtslgn AIIIOMII and Parameters

A discussion of the Phase lA monuonnc netork lllld the rationaJe behind tluu net work is Jlven tn Secuon a 3 I and 2 3 3 of the Ebasco Work Plan 11d bnd ly summan zed below SamphnJ tocauons and frequency an Jiven in Section 3 0 of the Field SamplinJ Plan The paraflltters to be tested (and corru pondinJ (teld and field QC samples) for subtaslu 3 2 bull Pnvate Wells 33 bullbull Monilorina Wells and 37 bullbull SoH Gas Surveys ~ summ1nzcd to Tables 3-1 lhrouamph 3middot4

SUbtak 32 PriVIIe Wells Thirteen private wells wtll be sampled and mnalyzed for the volarilc oraanics Ji ven in Table 3-2 plus ten temamely tdcnnficd compounds (TICs) by Method j 242 in Methods for the Os tennjnauon of Ornmc ComooundJ jn Drinkjna Wttcr EPA4-881039 to assess tf com~mmauon t )(ists Wells will be selected based on their susetptibility 10 comaminanon and avaJhtbJiity usinamp the private well inventory and if ava1lable RI OEM data The analyses are ~stricted to volatiles since past efforts indicated that these contaminants were at levels Jrtater than 1 m~ 1M limitation of resmcuna the analyses to volatiles is that acidbaseneutral semivolalile oraamcs pe nicides and inoraanic1 may aavel throuah lhe aquifer differenliy than the volatiles these will not be found since they ampR not beina analyzed fOf

SubteM 33 Monitoring Wtlll Thirty-seven uistina wells will be s~tmpled and anal yzed for volatiles on the TamprJet Compound List (TCL Table 3middot3) plus ten tentatively identified compoundJ (TICs) by the US EPA Contrlct Laboratory ProJram (ClP) routine anaJytical services (RAS ) volatiles method Th1s is beina done to assess cuntnt contamination Well s will be selected based on their serviceabi lity detcnnined durinJ the inventory As noted above for the private wells the study is limited 10 volatiles

Sublbullk 34 llld Rtconnbulllaunct This study will cover approx imately two square mile s centered on the oriainal disposal site at Picillo Farm and will also include assessment of existina information 1M tield portion of this work is directed towards aeoloampical field mappina and localina surface water samples These effons are directed towards rttinina Phase 18 activities includi namp the location of surface water samples and detenninina the inn uence of bedrock structure on around water movement The two squ~ miles encompasses the entire site and in combination with existinamp infonnation such as the EPIC air photoampraphs aeoloaicaJ maps tOpoJTlphic maps and aeoloaical repons sufficiently cover the site to locate geolopcal and surface water features that may be suscepuble to contamination on the site

Subtask 35 aonetomettr Survey The maanetometer surve y w11l be conducted over the emire project area to seanh for buried steel drums tanks or other ferrous debris that could indicate additional wute burial sites nm discovered during previous remedial invesriJations Eiaht areu were identified as potential waste burial sites from EPIC air photos by Ebasco These mas will be surveyed usinamp the fo llowina arid spacinas 40 feet

Artlur D Little 6Z3SlARCOll

r -middot-

bull

111 1middotmiddot1middot

lt

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bull

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-

bull

ArtJurD

Little

I r I

Qulluy Assurance ProJeCt Plan for Piclilo Fann July 9 1990

Revision No I Pace I of 33

U Dolo Ollf Otgtjecllvoo (DOOt)

A detailed discusuon is Jiven 1n the Ebasco Wort Plan of the data Jlps prKhKlinJ complcrion of the fctiSlbLiuy study and data quality objecdvcs related to the data needed 10 fill those aaps A brief summary of 0Q0s in support of Task l Field lnvcuiaarion activ111es 11 presented here

Activity 0111 Ou1llty Objective

32 Private Well lnvcnrory NA (field)

Private Well SamplinampAnalysis Level V (SAS) of Method 524 VOAs pH Level n (field pH temp cond) Temp Cond

33 Monitorina Well lnvcn10ry NA ~

Monltorin1 Well Samplinampf Level IV (RAS) Analysis of TCL VOAs plus I 0 Level n (field pH temp cond) n-TICs pH Temp Cond = 34 Field Reconnaissance NA (field) =

3 Maanetometcr Survey NA (field) 36 Stismic Survey NA (field)

37 Soil Gas ScrecninJ Level n (field) of toluene m-xylene (or accwne) methylene chloride 111 -trichlorethane trichloroethylene

38 EleVation Survey NA (tield)

310 Biota Survey NA (fie ld)

Health and Safe[) Suppon Levell (field)

HNu PID Draeaer 1ubts Explosivity Radiarion

r

)

Qualuy Assurance ProJeCt Plan for Ptctlo Fum Jul y 9 1990

Re vbullsbullon No I Paac 9 of J3

33 Monttortng Network Dtslgn AIIIOMII and Parameters

A discussion of the Phase lA monuonnc netork lllld the rationaJe behind tluu net work is Jlven tn Secuon a 3 I and 2 3 3 of the Ebasco Work Plan 11d bnd ly summan zed below SamphnJ tocauons and frequency an Jiven in Section 3 0 of the Field SamplinJ Plan The paraflltters to be tested (and corru pondinJ (teld and field QC samples) for subtaslu 3 2 bull Pnvate Wells 33 bullbull Monilorina Wells and 37 bullbull SoH Gas Surveys ~ summ1nzcd to Tables 3-1 lhrouamph 3middot4

SUbtak 32 PriVIIe Wells Thirteen private wells wtll be sampled and mnalyzed for the volarilc oraanics Ji ven in Table 3-2 plus ten temamely tdcnnficd compounds (TICs) by Method j 242 in Methods for the Os tennjnauon of Ornmc ComooundJ jn Drinkjna Wttcr EPA4-881039 to assess tf com~mmauon t )(ists Wells will be selected based on their susetptibility 10 comaminanon and avaJhtbJiity usinamp the private well inventory and if ava1lable RI OEM data The analyses are ~stricted to volatiles since past efforts indicated that these contaminants were at levels Jrtater than 1 m~ 1M limitation of resmcuna the analyses to volatiles is that acidbaseneutral semivolalile oraamcs pe nicides and inoraanic1 may aavel throuah lhe aquifer differenliy than the volatiles these will not be found since they ampR not beina analyzed fOf

SubteM 33 Monitoring Wtlll Thirty-seven uistina wells will be s~tmpled and anal yzed for volatiles on the TamprJet Compound List (TCL Table 3middot3) plus ten tentatively identified compoundJ (TICs) by the US EPA Contrlct Laboratory ProJram (ClP) routine anaJytical services (RAS ) volatiles method Th1s is beina done to assess cuntnt contamination Well s will be selected based on their serviceabi lity detcnnined durinJ the inventory As noted above for the private wells the study is limited 10 volatiles

Sublbullk 34 llld Rtconnbulllaunct This study will cover approx imately two square mile s centered on the oriainal disposal site at Picillo Farm and will also include assessment of existina information 1M tield portion of this work is directed towards aeoloampical field mappina and localina surface water samples These effons are directed towards rttinina Phase 18 activities includi namp the location of surface water samples and detenninina the inn uence of bedrock structure on around water movement The two squ~ miles encompasses the entire site and in combination with existinamp infonnation such as the EPIC air photoampraphs aeoloaicaJ maps tOpoJTlphic maps and aeoloaical repons sufficiently cover the site to locate geolopcal and surface water features that may be suscepuble to contamination on the site

Subtask 35 aonetomettr Survey The maanetometer surve y w11l be conducted over the emire project area to seanh for buried steel drums tanks or other ferrous debris that could indicate additional wute burial sites nm discovered during previous remedial invesriJations Eiaht areu were identified as potential waste burial sites from EPIC air photos by Ebasco These mas will be surveyed usinamp the fo llowina arid spacinas 40 feet

Artlur D Little 6Z3SlARCOll

I r I

Qulluy Assurance ProJeCt Plan for Piclilo Fann July 9 1990

Revision No I Pace I of 33

U Dolo Ollf Otgtjecllvoo (DOOt)

A detailed discusuon is Jiven 1n the Ebasco Wort Plan of the data Jlps prKhKlinJ complcrion of the fctiSlbLiuy study and data quality objecdvcs related to the data needed 10 fill those aaps A brief summary of 0Q0s in support of Task l Field lnvcuiaarion activ111es 11 presented here

Activity 0111 Ou1llty Objective

32 Private Well lnvcnrory NA (field)

Private Well SamplinampAnalysis Level V (SAS) of Method 524 VOAs pH Level n (field pH temp cond) Temp Cond

33 Monitorina Well lnvcn10ry NA ~

Monltorin1 Well Samplinampf Level IV (RAS) Analysis of TCL VOAs plus I 0 Level n (field pH temp cond) n-TICs pH Temp Cond = 34 Field Reconnaissance NA (field) =

3 Maanetometcr Survey NA (field) 36 Stismic Survey NA (field)

37 Soil Gas ScrecninJ Level n (field) of toluene m-xylene (or accwne) methylene chloride 111 -trichlorethane trichloroethylene

38 EleVation Survey NA (tield)

310 Biota Survey NA (fie ld)

Health and Safe[) Suppon Levell (field)

HNu PID Draeaer 1ubts Explosivity Radiarion

r

)

Qualuy Assurance ProJeCt Plan for Ptctlo Fum Jul y 9 1990

Re vbullsbullon No I Paac 9 of J3

33 Monttortng Network Dtslgn AIIIOMII and Parameters

A discussion of the Phase lA monuonnc netork lllld the rationaJe behind tluu net work is Jlven tn Secuon a 3 I and 2 3 3 of the Ebasco Work Plan 11d bnd ly summan zed below SamphnJ tocauons and frequency an Jiven in Section 3 0 of the Field SamplinJ Plan The paraflltters to be tested (and corru pondinJ (teld and field QC samples) for subtaslu 3 2 bull Pnvate Wells 33 bullbull Monilorina Wells and 37 bullbull SoH Gas Surveys ~ summ1nzcd to Tables 3-1 lhrouamph 3middot4

SUbtak 32 PriVIIe Wells Thirteen private wells wtll be sampled and mnalyzed for the volarilc oraanics Ji ven in Table 3-2 plus ten temamely tdcnnficd compounds (TICs) by Method j 242 in Methods for the Os tennjnauon of Ornmc ComooundJ jn Drinkjna Wttcr EPA4-881039 to assess tf com~mmauon t )(ists Wells will be selected based on their susetptibility 10 comaminanon and avaJhtbJiity usinamp the private well inventory and if ava1lable RI OEM data The analyses are ~stricted to volatiles since past efforts indicated that these contaminants were at levels Jrtater than 1 m~ 1M limitation of resmcuna the analyses to volatiles is that acidbaseneutral semivolalile oraamcs pe nicides and inoraanic1 may aavel throuah lhe aquifer differenliy than the volatiles these will not be found since they ampR not beina analyzed fOf

SubteM 33 Monitoring Wtlll Thirty-seven uistina wells will be s~tmpled and anal yzed for volatiles on the TamprJet Compound List (TCL Table 3middot3) plus ten tentatively identified compoundJ (TICs) by the US EPA Contrlct Laboratory ProJram (ClP) routine anaJytical services (RAS ) volatiles method Th1s is beina done to assess cuntnt contamination Well s will be selected based on their serviceabi lity detcnnined durinJ the inventory As noted above for the private wells the study is limited 10 volatiles

Sublbullk 34 llld Rtconnbulllaunct This study will cover approx imately two square mile s centered on the oriainal disposal site at Picillo Farm and will also include assessment of existina information 1M tield portion of this work is directed towards aeoloampical field mappina and localina surface water samples These effons are directed towards rttinina Phase 18 activities includi namp the location of surface water samples and detenninina the inn uence of bedrock structure on around water movement The two squ~ miles encompasses the entire site and in combination with existinamp infonnation such as the EPIC air photoampraphs aeoloaicaJ maps tOpoJTlphic maps and aeoloaical repons sufficiently cover the site to locate geolopcal and surface water features that may be suscepuble to contamination on the site

Subtask 35 aonetomettr Survey The maanetometer surve y w11l be conducted over the emire project area to seanh for buried steel drums tanks or other ferrous debris that could indicate additional wute burial sites nm discovered during previous remedial invesriJations Eiaht areu were identified as potential waste burial sites from EPIC air photos by Ebasco These mas will be surveyed usinamp the fo llowina arid spacinas 40 feet

Artlur D Little 6Z3SlARCOll

r

)

Qualuy Assurance ProJeCt Plan for Ptctlo Fum Jul y 9 1990

Re vbullsbullon No I Paac 9 of J3

33 Monttortng Network Dtslgn AIIIOMII and Parameters

A discussion of the Phase lA monuonnc netork lllld the rationaJe behind tluu net work is Jlven tn Secuon a 3 I and 2 3 3 of the Ebasco Work Plan 11d bnd ly summan zed below SamphnJ tocauons and frequency an Jiven in Section 3 0 of the Field SamplinJ Plan The paraflltters to be tested (and corru pondinJ (teld and field QC samples) for subtaslu 3 2 bull Pnvate Wells 33 bullbull Monilorina Wells and 37 bullbull SoH Gas Surveys ~ summ1nzcd to Tables 3-1 lhrouamph 3middot4

SUbtak 32 PriVIIe Wells Thirteen private wells wtll be sampled and mnalyzed for the volarilc oraanics Ji ven in Table 3-2 plus ten temamely tdcnnficd compounds (TICs) by Method j 242 in Methods for the Os tennjnauon of Ornmc ComooundJ jn Drinkjna Wttcr EPA4-881039 to assess tf com~mmauon t )(ists Wells will be selected based on their susetptibility 10 comaminanon and avaJhtbJiity usinamp the private well inventory and if ava1lable RI OEM data The analyses are ~stricted to volatiles since past efforts indicated that these contaminants were at levels Jrtater than 1 m~ 1M limitation of resmcuna the analyses to volatiles is that acidbaseneutral semivolalile oraamcs pe nicides and inoraanic1 may aavel throuah lhe aquifer differenliy than the volatiles these will not be found since they ampR not beina analyzed fOf

SubteM 33 Monitoring Wtlll Thirty-seven uistina wells will be s~tmpled and anal yzed for volatiles on the TamprJet Compound List (TCL Table 3middot3) plus ten tentatively identified compoundJ (TICs) by the US EPA Contrlct Laboratory ProJram (ClP) routine anaJytical services (RAS ) volatiles method Th1s is beina done to assess cuntnt contamination Well s will be selected based on their serviceabi lity detcnnined durinJ the inventory As noted above for the private wells the study is limited 10 volatiles

Sublbullk 34 llld Rtconnbulllaunct This study will cover approx imately two square mile s centered on the oriainal disposal site at Picillo Farm and will also include assessment of existina information 1M tield portion of this work is directed towards aeoloampical field mappina and localina surface water samples These effons are directed towards rttinina Phase 18 activities includi namp the location of surface water samples and detenninina the inn uence of bedrock structure on around water movement The two squ~ miles encompasses the entire site and in combination with existinamp infonnation such as the EPIC air photoampraphs aeoloaicaJ maps tOpoJTlphic maps and aeoloaical repons sufficiently cover the site to locate geolopcal and surface water features that may be suscepuble to contamination on the site

Subtask 35 aonetomettr Survey The maanetometer surve y w11l be conducted over the emire project area to seanh for buried steel drums tanks or other ferrous debris that could indicate additional wute burial sites nm discovered during previous remedial invesriJations Eiaht areu were identified as potential waste burial sites from EPIC air photos by Ebasco These mas will be surveyed usinamp the fo llowina arid spacinas 40 feet

Artlur D Little 6Z3SlARCOll

r

Quahty Auuf3nce ProJtCI Plan for Plcllo Farm July 9 1990

Rev1saon No I ~gtabull 10 o1 n

(Attu Ia the wcsttm tield mnd the fie ld surroundinJ the duJ pond nur the two residences) and 20 feet (Arus I b 2 l 4 and )

Subtuk SI Slamlc Refraction Survey Two lines or Hismic reftacuon wLII be conducttd over the wetlands at the northern portion of the project area to venfy the poaenual presence of a 111mflcant bedtoclt shear zone in this area owh tch may effect the movement of around water and conwninanu The loe~uons of the prelttous rcfracoon lines and the new proposed linet arc shown in the Ebasco Work Plan (Fiaure 4-4 paae 131 ) The seismic survey will employ 24-channel dJil31 record101 Jnsttumentatlon usinJ a 10-foot eophone spcinJ Previoosly collected st1smic data indicl)ted that this area in the wetlands required funher study

Subtelk 37 SOli Gat Survey The soil 111 survey will encompm nch of the eleven suspected dumpin1 shes idenlifted in the EPIC air phoiOcraphic murpretadon (Ebuco Work P1an FiJure 4shy3 pap 126) A 0-f()()( JOd spacinJ will be used for each of the shes Volatile orJampnics found at hJh levels 1n the round water durinamp previous studies will be analyzed (Table 3-4) These will serve u indicators of contamination in the suspect areu

lubt8lk 31 Ebullvbulltlon Survey A location and elevation survey of cenain lcey points in the project site will be conducted Durinamp an initial phase prior 10 developina Jrids for Subtasks 3 Maanetometu Survey 36 Seismic Survey and 37 Soil Gas Survey the locations IQd elevations of 20 key amprid points throuahout the project area will be established Subsequently these points will be used to establish the Jrids for the three subwlcs Durinamp the second phase the location and elevation o( each of the monitorinJ wells sampled and surface water samplinJ points to be sampled in Phuc 18 will be determined Horizontal locations will be to wilhi n I foot and venical elevations to within Oot feet All of the points will be tied to the State Planar Coonlinate System Therefore the localion of samplina effons will be accurtely known

Subtelk 310 Blote Survey This survey will provide a preliminary overview of the tc~strial and wetland biota and ecosystems occurrinc throuahout the site lnilially site toporraphic sites National Wetlands Inventory (NW I) maps and Rhode Island Natural Heritaae Propvns (RINHP) element occurrence lists and associated habitat maps will be reviewed to focus the subsequent two day site visit The combined information will provide sufficient coverage for a preliminary overview

HMith lnd Safety Support A radiation screen of the emire site will be undenaken prior to any field efforu to uscss whether special precaunons wtll need to be taken durina field activities

) Durinamp aU field surveys except the private well survey an HNu photoionization meter wiU be used to screen for volatile orc anic compounds An explosivity meter will also be used to monitor wells for an explosive atmosphere when opened

ArtlurD Little 6lJS1ARCOII

-n = =

- r 1

-

--32

] ]

]7

=amp PrtvbullWdlt

Pleld -middot-Trlpllri FlcldlluplicMe MalriJ SpibDup

wu-middotshy _TO I- w~middot- SoWOup

oil 0 Sy ~(sy-)

-()middotshy-()middotshy~ oliO Field ~

ow w w w

ow w

ow w w

ow w so A

A

so so

TOCII ~r or Samples

Qualify Au unncc Pmject Pan for Pcillo Farm

owhrUm VOAe + YOAI + 10

(T- 21 (T-W)

13 I I I I I

20

37 I 9 10 2 I

61

July ) I 1990 Revision No 2 Pap II of l l

til OCindle pH co YOAa T- IT- HI

I]

37

)(B

30

All

lO m

bull bull Tbr eua rNmbcr or QC samples may chanampc due 10 Rdd conditions OW-OIOUndwlter W bull ltcafeN IJade warcr so - SoU bullbull

) A - Ambicnc Air

ArtlurD Little 6llSlAJCOII~

- r 1

-

--32

] ]

]7

=amp PrtvbullWdlt

Pleld -middot-Trlpllri FlcldlluplicMe MalriJ SpibDup

wu-middotshy _TO I- w~middot- SoWOup

oil 0 Sy ~(sy-)

-()middotshy-()middotshy~ oliO Field ~

ow w w w

ow w

ow w w

ow w so A

A

so so

TOCII ~r or Samples

Qualify Au unncc Pmject Pan for Pcillo Farm

owhrUm VOAe + YOAI + 10

(T- 21 (T-W)

13 I I I I I

20

37 I 9 10 2 I

61

July ) I 1990 Revision No 2 Pap II of l l

til OCindle pH co YOAa T- IT- HI

I]

37

)(B

30

All

lO m

bull bull Tbr eua rNmbcr or QC samples may chanampc due 10 Rdd conditions OW-OIOUndwlter W bull ltcafeN IJade warcr so - SoU bullbull

) A - Ambicnc Air

ArtlurD Little 6llSlAJCOII~

I r I

-

TtMe 3-2 Vot11Ue Org~nlct ror (-1012)

Compound

Benzene Bromobenzenc Bromochloromelhane Bromodichloromethanc Bromoform Bromomethane n-Butylbenzenc sec-Butylbenzcne tcn-Butylbenzene Carbon tcrrchloride Chklrobenzcnc OloroethlllC Cblorolonn OklromethlllC 2-Cbkwololucnc 4-0iorocolucnc Dibromochloromethane 12-Dibrorno-3-chloropropane 12-Dibromocthane DibromomethlllC 12-Dichlorobenzene 13-Dichlorobcnzene 14-Dichlorobenzene DichlorodiOuoromethane 1 1-DichloroethlllC 12-DichiOIOIthane l l middotDichlorocthene cii-12-Dichloroethene trans-llmiddotDichlorocthene 12-DichloroproplllC 13-Dichloropropane 22-Dichloropropane 11-Dichloropropene cis-1 2-Dichloropropene trans-12-Dichloropropene Ethylbenzene He~tachlorobutadiene

Quahry Auunnct Project Plan for Pc 1Uo flnll July 9 1990

Revision No I p 12 olll

Analysts In Privett Wtlla Utlng MttttOd 5242

Detection Umll (ugL)

004 00) 004 008 012 011 011 013 014 021 004 010 003 013 004 006 001 026 006 024 OoJ 012 003 010 004 006 012 012 006 004 004 OJl 010

006 011

ArtlurD Little 6l3SlARCOI

r

Qllhry Anunnce Project Plan for Picbullllo Farm

)

T- 3-2 (continued page 2 of 2)

Compound

Isopropylbenzene 4-UopropyiiOIIJCne Methylene chloride Nopllthllcne n-Propylbenzene S~ynne 1112middot Tetnchloroethane 11 22middot Tccnchloroethane Tctr~ehlorocthenc ToiLMne 123middotTrichlorobenzene 124-Trichlorobenzene 111-Trichlorocdtanc 112middot Trichloroethane Trichloroelhene Trichlorofluoromethane 123middotTrichloropropane 124middot Trimethylbenzenc 13 middotTrimethylbenzenc Vinyl chloride ~rXylene m-Xylene p-Xylcne

Additional Taracted Compounds

MethyUsobutyiKetone (4-methyl-2-pencanone) Acetone (2- propanone) Methyl Ethyl Ketone (2-Buranone)

Plus Ten (10) Tentatively ldcn dficd Compounds

July 9 1990 Re vition No I Paae 13 of 33

Otttcllon Limit (ugtl)

0 1~ 012 Oo3 004 004 004 00~ 004 014 011 Oo3 004 008 010 019 008 032 013 Ool 017 011 00~ 013

100 100 100

Method 242 in Methods for rhc Oerermjnarjon of Ornnic Comoounds jn Drinkinr Water EPA6004-881039

ArtJur IJIIittle

r

)

Qu~hty Assu nnce ProJect Plan for Ptctllo Fum July 9 1990

Re vision No I Pase 14 of 33

TIIM )3 Target Compound List (TCL) for Volltllt Org1nlc1 In Monitoring Wtllt utlng AA S Method

Ouantltatlon Limit Water

VcMatUte (Ugl)

Chloromtthane 10 Brornomethanc 10 Vinyl Chlonde 10 Chloroethanc 10 Methylene Chloride l Acetone 10 Carbon Disulnde l 11-Dichloroethcne l 11-Dichloroethane l 12-0ichloroethene Iota) l Chloroform l 12-0 ichloroethane l 2-Butanone 10 11 1-Trichloroethane l Carbon Tetrachloride l Vinyl AcetaiC 10 Bromodichloromethane l 12-Dichloropropane l I2-Dichloropropane l cis-13-Dic h)oropropene l Trichlorocthene l Dibromochloromethane l 11 2middot Trichloroethane l Benzene l transmiddot13-Dichloropropene l Bromofonn l 4-Mcthyl-2-pcntanone 10 2-Hcunone 10 Te01Chloroethcne l Toluene l 1122-Tett1chloroethane l Chlorobenzene l Ethyl Benzene l Styrene l Xylenes (toul) l

Plus Ten (10) Tentative ly Identified Compounds

QP Statement of Work (February 1988) RAS methods

ArtJur D Little 62lSlARCltIII

- r I

QuaHy Auunnce ProjtCI Plan for Ptc1ilo Fann July 9 1990

Revtston No I pbullbull ll ol JJ

Otttctton Limit V~IUie Organic Compound ugl Soli G11

lll-Trkhloltoellane ITCAJ 0000

Trkhloroelllene (TCEJ 00001

Me1hylcne Chloride 0002

Toluene 002

002

~-n = =U

bull Acetone may be subsntuted for ylcnes dependent on initial results

AltlurD Little

- r -

QuJiuy Anur1ncc ProJtCI Plan for Plc111o Farm July 9 1990

ReviSIOn No I p 16 ol ))

0 Protect Orgenlutlon and Anponsfblllty

See PMP QAPP Secuon 7 a for funher tllplanauon of quahty assurance responsibilhies and projtct oraaniuuon and PMP Section 2 0 for overall proaram responsibiliues )

llclllo bull lroject Sttt

Pmjec1 Manaaer Roben Lambc

Health and Safc ry Project Manaacrmiddot Davtd lscnberJ

lrogrem ~ent Office Staff

Deputy Proampnm Manaacr David Lanascth

Qualily Assurance Officer Richard Waterman (responsibili ties include project speciftc performancesys te ms audits)

Lead Chemis1 Roben O Nc1l

Health and Safety Officer Corey Bnus

The project oraanization and re sponsibilities are shown in Fiaure 4-1

ArtlurD Little

--

-(_

Figure 4-l Proect OJgMizat- Slruct

L EPA~~ J [)ane Kelley r --- --

I

~ IL J I

David Langseth L J I Ii

l

__J I

l ADL EPA- Jl I PrcgtJoc~ David Isenbergl J L J JRobert Lambe Anna Ktasko

_l c-- l I DIU Subcont-ctors~

Kristen Steck Scot Foster Kalhy Thrun Phil Aury - -RolgtertONei Tony IAajahad (To be selected]

Task2 Tasks 35 Tasks 135 Tasks 35

Task4

1 Task3

JeH Fonnermiddot Kevin KuecNer

Kevin Cahil

Tasks 35 middoton site tleallh and Sakgtty COOidmaKw

middot middotmiddotmiddot r~~ middot~ OliOOJll IAUVlUSUrrl-0yen IUtbull ft30P Mil 10 bulln-bull M(l

WVVJ OTl~ 01 -middot bull1 n qtoN bull1-1111 bullbull1111iOOJid bullbullap nat bullbullbullbull1pabull os M~bull 11 3lUOM

r -

-QuJILy -uurJnce Pro)laquot Plan for P1c111o Farm

July 9 1990 Revision No I Pa1e 11 of 33

SO Data Oulllty Ob)eetlvll for Critical Meaturernentt In Terma of ~recllion Accuracy Complett nllt Rtprtllntlt lveneaa and ComparebiiUy

(See PMP QAPP Section 7 9 and Genenc QAPJP Secnon $0 for funher u planauona)

51 Summary

D1t1 Quality Objectives for cnucal musuremen11 durinamp the private well monitorin1 well and soil ampas surveys are summariud in Table $-1

52 AepreMntetlveneu

(See PMO Generic QAPJP Secuon $6 for a furthe r explanarion)

Representati veness is defined in QAMSmiddot00$80 as an expression of the dcaree to which the data accurately and precisely represe ntS a characteristic of a population parameter variations at a samplina point a process condition or an environmental condition The objectives for repre sentativeness are described in the Field Samplin1 Plan Section 20 and this Quality Auunnce Project Plltl Section 30 These objectives will be met throu1h the proper implementation of the Field Samplin1 Plan and the Quali ty Assurance Projcct Plan Each of the surveys wert detiJIICd usin1 infonnat ion obtained durinamp pre vious Sludies and are therefore fcxussed on detectinamp areas of potentiJl contamination and assessin1 current levels of contamination at sites found previously to be contaminated

Compuability is defmed in QAMS-00$80 as an expression of the confidence with which one data set can be compared to another

Data units will be expressed unifonnly for each s~cific site

MNeurement

Concentrltion (aqueous) Concentration (soil aas) Concentration (air) Concentrltion (HNu air) Temperature Distance Conducli vi1y pH radioactivity Maampnetic fie ld Seismic Velocity

Artlur D Little

Units

ugL ugL ugL ppmbullc feelt umhoscmJ pH uni1s pCilamp uCicm aam mas ~secm msecm

~Rihr mRhr

- r -

J

Quahty AlSUIInce Prottct Plan for Plctllo Farm Ju ly 9 1990

Re visaon No I Paac 19 of JJ

0111 Outllly Objectives for Critic Mtesurtmtnls Precision Accurecy 1nd Compltttntll (page 1 or 2)

Levtl ot Anllysbull Mltrlbull

Anllyall P1rameter

EltlmiK Accurtcy

Eltlmlltd P-clskJn Completeness

Laboratory Mtuurtmenu Private WcUt (Sublask 32)

v ow 1242 CLP RAS J CLP RAS Volaules

Monltorina Wdls (Subcask 13)

IV ow CLP RAS CL P RAS CLP RAS TCL VOAs

Field Mcuurtmcnts Soil Gu Survey Subtask 17)

so Volatiles Rttovcry RPO 1011-I IOtt SOO

Privaee and Monitarinl Wells Monthly W3ter Level Mcasuremcms (SubtaskJ 32 13 311 )

ow pH +02 pH un its bull 02 pH units 900 ow Tcmperuure bulllmiddot lmiddotc c ow Conducti vity +middot2111 scal e +middot lloscale

or 10 umhos shyow Depth Hclahl +middot(gt0111 OQI n shy

Health W Safety Support -HNu PID +middot2lo scale bullmiddotI scale

or I ppm ExpiOS1vhy shyRadiation tlllO tlllO 1000

(GciJer Counter)

Maancrometcr Survey (Subtask 3Ji)

NA NA Field Intensity tl aamma tl aamma -6llUAJICOIIArtlurD Little

I

I r I

Quaht) Auurance Proect Plan fot Pic1llo Farm July 9 1990

Revisbullon No 1 Paac 20 ot JJ

Tlble 5-1 (continued page 2 of 2)

~ Of Anltytlt htimlttd AMtrM Mllrlx P1rameter Accuracy

Seink Sutty (Subcask 3 6)

NA NA Wave Velouy 12 btt ttsoluttOn from

2msecto~clsample -ElcVItlon Survey (Subtask 3 8)

NA NA Dm~nce tl fi tl fooc 10010 NA NA Elevauon tOOl ft plusmn001 ft 10010

Maub ow bull Ground Waur sa SOli Gas A bull Ambient AirI

bull aPmiddotRAS bull Objectives for these meuun=ments will be taken from the US EPA Reaion I Ouidme for Vllidltbullna Ora11mc and lnoraanic Data

NA bull Noc AppUcabk

62JS1Aitcltltl

r

Qualuy Assurance Project Plan for PICtllo Farm July 9 1990

ReY tS IOfl No I Pace 21 of Jl

DuMJ the evaluation of the data rtsuluna from thts sue the variabtluy usoctalfd with the data in terms of prectslon accunCy and representameness wtll abo be UJeSsed and tncludcd 10 the diSCUSS IOn of tht datL

10 Swnpllng Procedurtl

f1 Sampling Locltlon tnd Frequency

The samplina locauons and frtquency of samplina for the surveys is Jiven in the Field Samplina Plan Sccuon 30

12 Sampling Proctdurta

Standard OpendnJ ProcedurtJ SOPs) for each of the samplinc openrions and r~ld te ninJ procedures that wtll be undertaken are attached to the Field Samplinc Plan A summary of each of these procedures alon J with a reference to the appropriate SOP is ampiven in Seclion ~ 0 of the Field SamplinJ Plan

eon ivn 1nd Holding nmn These items arc civen in the Field Samplin1 Plan Section 60

Pletd OrtconWmlneUOn ProcKurtl Field decontamination procedures are riven in the followinJ SOPs Field Decoruaminadon of Metal Samplina Equipment SOP No ADL-1009 and Field Dccoruaminarion of Tenon or Glass SamplinJ Equipment SOP No ADL-1008

d Oocumenlallon Procedurn Field documenwion procedu~s art summarized in the PMP Generic QA PjP Section 67 and the followina SOPs Standard OperatinJ Procedures SOP) for Schedulina ARCS Analylical Services SOP No ARC-20 Geotechnical Documentalion SOP No ADLmiddot4014 and Sample Cunody SOP No EPAmiddot IOOI

70 smp Cuetody

Sample custody procedures arc summarized in the PMP Generic QAPjP Section 70 and detai led in Sample Custody SOP No EPA-1001

I

J 6lllARaltlArthwD Little

r

Qu~hty Auunnce ProJeCt Plan for Plclllo Farm July 9 1990

Ruuion No I Po1e ll of ll

10 Clbrltlon Proetdurts

Generll proccdurts for calibrmlion are JIVtn 1n the PMO Generic QAP]P Secrion 10 Calibrttion procedures for the analysiS of volaule oraanics in the private well water an Jiven in Me1hod j242 Methoda for the Oetcnnjnarion olt Orllnki Compoonda jn Drinlqnr WIC[ EPA60014-88039 and ror he analysis of volaule oraanks In the monuonna well ampfOUnd water in US EPA Concrct Laboratory Propam (aP Statement of Work for the Analysts of Volanle Oraanics February 1988

Calibnrion procedures and frequency for other critical measuremenu 13 summarized in Table 8middot 1 wuh the appropriate references

ArtlurD Little

r

Qllhry Anunnce Project Plan for Picbullllo Farm

)

T- 3-2 (continued page 2 of 2)

Compound

Isopropylbenzene 4-UopropyiiOIIJCne Methylene chloride Nopllthllcne n-Propylbenzene S~ynne 1112middot Tetnchloroethane 11 22middot Tccnchloroethane Tctr~ehlorocthenc ToiLMne 123middotTrichlorobenzene 124-Trichlorobenzene 111-Trichlorocdtanc 112middot Trichloroethane Trichloroelhene Trichlorofluoromethane 123middotTrichloropropane 124middot Trimethylbenzenc 13 middotTrimethylbenzenc Vinyl chloride ~rXylene m-Xylene p-Xylcne

Additional Taracted Compounds

MethyUsobutyiKetone (4-methyl-2-pencanone) Acetone (2- propanone) Methyl Ethyl Ketone (2-Buranone)

Plus Ten (10) Tentatively ldcn dficd Compounds

July 9 1990 Re vition No I Paae 13 of 33

Otttcllon Limit (ugtl)

0 1~ 012 Oo3 004 004 004 00~ 004 014 011 Oo3 004 008 010 019 008 032 013 Ool 017 011 00~ 013

100 100 100

Method 242 in Methods for rhc Oerermjnarjon of Ornnic Comoounds jn Drinkinr Water EPA6004-881039

ArtJur IJIIittle

r

)

Qu~hty Assu nnce ProJect Plan for Ptctllo Fum July 9 1990

Re vision No I Pase 14 of 33

TIIM )3 Target Compound List (TCL) for Volltllt Org1nlc1 In Monitoring Wtllt utlng AA S Method

Ouantltatlon Limit Water

VcMatUte (Ugl)

Chloromtthane 10 Brornomethanc 10 Vinyl Chlonde 10 Chloroethanc 10 Methylene Chloride l Acetone 10 Carbon Disulnde l 11-Dichloroethcne l 11-Dichloroethane l 12-0ichloroethene Iota) l Chloroform l 12-0 ichloroethane l 2-Butanone 10 11 1-Trichloroethane l Carbon Tetrachloride l Vinyl AcetaiC 10 Bromodichloromethane l 12-Dichloropropane l I2-Dichloropropane l cis-13-Dic h)oropropene l Trichlorocthene l Dibromochloromethane l 11 2middot Trichloroethane l Benzene l transmiddot13-Dichloropropene l Bromofonn l 4-Mcthyl-2-pcntanone 10 2-Hcunone 10 Te01Chloroethcne l Toluene l 1122-Tett1chloroethane l Chlorobenzene l Ethyl Benzene l Styrene l Xylenes (toul) l

Plus Ten (10) Tentative ly Identified Compounds

QP Statement of Work (February 1988) RAS methods

ArtJur D Little 62lSlARCltIII

- r I

QuaHy Auunnce ProjtCI Plan for Ptc1ilo Fann July 9 1990

Revtston No I pbullbull ll ol JJ

Otttctton Limit V~IUie Organic Compound ugl Soli G11

lll-Trkhloltoellane ITCAJ 0000

Trkhloroelllene (TCEJ 00001

Me1hylcne Chloride 0002

Toluene 002

002

~-n = =U

bull Acetone may be subsntuted for ylcnes dependent on initial results

AltlurD Little

- r -

QuJiuy Anur1ncc ProJtCI Plan for Plc111o Farm July 9 1990

ReviSIOn No I p 16 ol ))

0 Protect Orgenlutlon and Anponsfblllty

See PMP QAPP Secuon 7 a for funher tllplanauon of quahty assurance responsibilhies and projtct oraaniuuon and PMP Section 2 0 for overall proaram responsibiliues )

llclllo bull lroject Sttt

Pmjec1 Manaaer Roben Lambc

Health and Safc ry Project Manaacrmiddot Davtd lscnberJ

lrogrem ~ent Office Staff

Deputy Proampnm Manaacr David Lanascth

Qualily Assurance Officer Richard Waterman (responsibili ties include project speciftc performancesys te ms audits)

Lead Chemis1 Roben O Nc1l

Health and Safety Officer Corey Bnus

The project oraanization and re sponsibilities are shown in Fiaure 4-1

ArtlurD Little

--

-(_

Figure 4-l Proect OJgMizat- Slruct

L EPA~~ J [)ane Kelley r --- --

I

~ IL J I

David Langseth L J I Ii

l

__J I

l ADL EPA- Jl I PrcgtJoc~ David Isenbergl J L J JRobert Lambe Anna Ktasko

_l c-- l I DIU Subcont-ctors~

Kristen Steck Scot Foster Kalhy Thrun Phil Aury - -RolgtertONei Tony IAajahad (To be selected]

Task2 Tasks 35 Tasks 135 Tasks 35

Task4

1 Task3

JeH Fonnermiddot Kevin KuecNer

Kevin Cahil

Tasks 35 middoton site tleallh and Sakgtty COOidmaKw

middot middotmiddotmiddot r~~ middot~ OliOOJll IAUVlUSUrrl-0yen IUtbull ft30P Mil 10 bulln-bull M(l

WVVJ OTl~ 01 -middot bull1 n qtoN bull1-1111 bullbull1111iOOJid bullbullap nat bullbullbullbull1pabull os M~bull 11 3lUOM

r -

-QuJILy -uurJnce Pro)laquot Plan for P1c111o Farm

July 9 1990 Revision No I Pa1e 11 of 33

SO Data Oulllty Ob)eetlvll for Critical Meaturernentt In Terma of ~recllion Accuracy Complett nllt Rtprtllntlt lveneaa and ComparebiiUy

(See PMP QAPP Section 7 9 and Genenc QAPJP Secnon $0 for funher u planauona)

51 Summary

D1t1 Quality Objectives for cnucal musuremen11 durinamp the private well monitorin1 well and soil ampas surveys are summariud in Table $-1

52 AepreMntetlveneu

(See PMO Generic QAPJP Secuon $6 for a furthe r explanarion)

Representati veness is defined in QAMSmiddot00$80 as an expression of the dcaree to which the data accurately and precisely represe ntS a characteristic of a population parameter variations at a samplina point a process condition or an environmental condition The objectives for repre sentativeness are described in the Field Samplin1 Plan Section 20 and this Quality Auunnce Project Plltl Section 30 These objectives will be met throu1h the proper implementation of the Field Samplin1 Plan and the Quali ty Assurance Projcct Plan Each of the surveys wert detiJIICd usin1 infonnat ion obtained durinamp pre vious Sludies and are therefore fcxussed on detectinamp areas of potentiJl contamination and assessin1 current levels of contamination at sites found previously to be contaminated

Compuability is defmed in QAMS-00$80 as an expression of the confidence with which one data set can be compared to another

Data units will be expressed unifonnly for each s~cific site

MNeurement

Concentrltion (aqueous) Concentration (soil aas) Concentration (air) Concentrltion (HNu air) Temperature Distance Conducli vi1y pH radioactivity Maampnetic fie ld Seismic Velocity

Artlur D Little

Units

ugL ugL ugL ppmbullc feelt umhoscmJ pH uni1s pCilamp uCicm aam mas ~secm msecm

~Rihr mRhr

- r -

J

Quahty AlSUIInce Prottct Plan for Plctllo Farm Ju ly 9 1990

Re visaon No I Paac 19 of JJ

0111 Outllly Objectives for Critic Mtesurtmtnls Precision Accurecy 1nd Compltttntll (page 1 or 2)

Levtl ot Anllysbull Mltrlbull

Anllyall P1rameter

EltlmiK Accurtcy

Eltlmlltd P-clskJn Completeness

Laboratory Mtuurtmenu Private WcUt (Sublask 32)

v ow 1242 CLP RAS J CLP RAS Volaules

Monltorina Wdls (Subcask 13)

IV ow CLP RAS CL P RAS CLP RAS TCL VOAs

Field Mcuurtmcnts Soil Gu Survey Subtask 17)

so Volatiles Rttovcry RPO 1011-I IOtt SOO

Privaee and Monitarinl Wells Monthly W3ter Level Mcasuremcms (SubtaskJ 32 13 311 )

ow pH +02 pH un its bull 02 pH units 900 ow Tcmperuure bulllmiddot lmiddotc c ow Conducti vity +middot2111 scal e +middot lloscale

or 10 umhos shyow Depth Hclahl +middot(gt0111 OQI n shy

Health W Safety Support -HNu PID +middot2lo scale bullmiddotI scale

or I ppm ExpiOS1vhy shyRadiation tlllO tlllO 1000

(GciJer Counter)

Maancrometcr Survey (Subtask 3Ji)

NA NA Field Intensity tl aamma tl aamma -6llUAJICOIIArtlurD Little

I

I r I

Quaht) Auurance Proect Plan fot Pic1llo Farm July 9 1990

Revisbullon No 1 Paac 20 ot JJ

Tlble 5-1 (continued page 2 of 2)

~ Of Anltytlt htimlttd AMtrM Mllrlx P1rameter Accuracy

Seink Sutty (Subcask 3 6)

NA NA Wave Velouy 12 btt ttsoluttOn from

2msecto~clsample -ElcVItlon Survey (Subtask 3 8)

NA NA Dm~nce tl fi tl fooc 10010 NA NA Elevauon tOOl ft plusmn001 ft 10010

Maub ow bull Ground Waur sa SOli Gas A bull Ambient AirI

bull aPmiddotRAS bull Objectives for these meuun=ments will be taken from the US EPA Reaion I Ouidme for Vllidltbullna Ora11mc and lnoraanic Data

NA bull Noc AppUcabk

62JS1Aitcltltl

r

Qualuy Assurance Project Plan for PICtllo Farm July 9 1990

ReY tS IOfl No I Pace 21 of Jl

DuMJ the evaluation of the data rtsuluna from thts sue the variabtluy usoctalfd with the data in terms of prectslon accunCy and representameness wtll abo be UJeSsed and tncludcd 10 the diSCUSS IOn of tht datL

10 Swnpllng Procedurtl

f1 Sampling Locltlon tnd Frequency

The samplina locauons and frtquency of samplina for the surveys is Jiven in the Field Samplina Plan Sccuon 30

12 Sampling Proctdurta

Standard OpendnJ ProcedurtJ SOPs) for each of the samplinc openrions and r~ld te ninJ procedures that wtll be undertaken are attached to the Field Samplinc Plan A summary of each of these procedures alon J with a reference to the appropriate SOP is ampiven in Seclion ~ 0 of the Field SamplinJ Plan

eon ivn 1nd Holding nmn These items arc civen in the Field Samplin1 Plan Section 60

Pletd OrtconWmlneUOn ProcKurtl Field decontamination procedures are riven in the followinJ SOPs Field Decoruaminadon of Metal Samplina Equipment SOP No ADL-1009 and Field Dccoruaminarion of Tenon or Glass SamplinJ Equipment SOP No ADL-1008

d Oocumenlallon Procedurn Field documenwion procedu~s art summarized in the PMP Generic QA PjP Section 67 and the followina SOPs Standard OperatinJ Procedures SOP) for Schedulina ARCS Analylical Services SOP No ARC-20 Geotechnical Documentalion SOP No ADLmiddot4014 and Sample Cunody SOP No EPAmiddot IOOI

70 smp Cuetody

Sample custody procedures arc summarized in the PMP Generic QAPjP Section 70 and detai led in Sample Custody SOP No EPA-1001

I

J 6lllARaltlArthwD Little

r

Qu~hty Auunnce ProJeCt Plan for Plclllo Farm July 9 1990

Ruuion No I Po1e ll of ll

10 Clbrltlon Proetdurts

Generll proccdurts for calibrmlion are JIVtn 1n the PMO Generic QAP]P Secrion 10 Calibrttion procedures for the analysiS of volaule oraanics in the private well water an Jiven in Me1hod j242 Methoda for the Oetcnnjnarion olt Orllnki Compoonda jn Drinlqnr WIC[ EPA60014-88039 and ror he analysis of volaule oraanks In the monuonna well ampfOUnd water in US EPA Concrct Laboratory Propam (aP Statement of Work for the Analysts of Volanle Oraanics February 1988

Calibnrion procedures and frequency for other critical measuremenu 13 summarized in Table 8middot 1 wuh the appropriate references

ArtlurD Little

r

)

Qu~hty Assu nnce ProJect Plan for Ptctllo Fum July 9 1990

Re vision No I Pase 14 of 33

TIIM )3 Target Compound List (TCL) for Volltllt Org1nlc1 In Monitoring Wtllt utlng AA S Method

Ouantltatlon Limit Water

VcMatUte (Ugl)

Chloromtthane 10 Brornomethanc 10 Vinyl Chlonde 10 Chloroethanc 10 Methylene Chloride l Acetone 10 Carbon Disulnde l 11-Dichloroethcne l 11-Dichloroethane l 12-0ichloroethene Iota) l Chloroform l 12-0 ichloroethane l 2-Butanone 10 11 1-Trichloroethane l Carbon Tetrachloride l Vinyl AcetaiC 10 Bromodichloromethane l 12-Dichloropropane l I2-Dichloropropane l cis-13-Dic h)oropropene l Trichlorocthene l Dibromochloromethane l 11 2middot Trichloroethane l Benzene l transmiddot13-Dichloropropene l Bromofonn l 4-Mcthyl-2-pcntanone 10 2-Hcunone 10 Te01Chloroethcne l Toluene l 1122-Tett1chloroethane l Chlorobenzene l Ethyl Benzene l Styrene l Xylenes (toul) l

Plus Ten (10) Tentative ly Identified Compounds

QP Statement of Work (February 1988) RAS methods

ArtJur D Little 62lSlARCltIII

- r I

QuaHy Auunnce ProjtCI Plan for Ptc1ilo Fann July 9 1990

Revtston No I pbullbull ll ol JJ

Otttctton Limit V~IUie Organic Compound ugl Soli G11

lll-Trkhloltoellane ITCAJ 0000

Trkhloroelllene (TCEJ 00001

Me1hylcne Chloride 0002

Toluene 002

002

~-n = =U

bull Acetone may be subsntuted for ylcnes dependent on initial results

AltlurD Little

- r -

QuJiuy Anur1ncc ProJtCI Plan for Plc111o Farm July 9 1990

ReviSIOn No I p 16 ol ))

0 Protect Orgenlutlon and Anponsfblllty

See PMP QAPP Secuon 7 a for funher tllplanauon of quahty assurance responsibilhies and projtct oraaniuuon and PMP Section 2 0 for overall proaram responsibiliues )

llclllo bull lroject Sttt

Pmjec1 Manaaer Roben Lambc

Health and Safc ry Project Manaacrmiddot Davtd lscnberJ

lrogrem ~ent Office Staff

Deputy Proampnm Manaacr David Lanascth

Qualily Assurance Officer Richard Waterman (responsibili ties include project speciftc performancesys te ms audits)

Lead Chemis1 Roben O Nc1l

Health and Safety Officer Corey Bnus

The project oraanization and re sponsibilities are shown in Fiaure 4-1

ArtlurD Little

--

-(_

Figure 4-l Proect OJgMizat- Slruct

L EPA~~ J [)ane Kelley r --- --

I

~ IL J I

David Langseth L J I Ii

l

__J I

l ADL EPA- Jl I PrcgtJoc~ David Isenbergl J L J JRobert Lambe Anna Ktasko

_l c-- l I DIU Subcont-ctors~

Kristen Steck Scot Foster Kalhy Thrun Phil Aury - -RolgtertONei Tony IAajahad (To be selected]

Task2 Tasks 35 Tasks 135 Tasks 35

Task4

1 Task3

JeH Fonnermiddot Kevin KuecNer

Kevin Cahil

Tasks 35 middoton site tleallh and Sakgtty COOidmaKw

middot middotmiddotmiddot r~~ middot~ OliOOJll IAUVlUSUrrl-0yen IUtbull ft30P Mil 10 bulln-bull M(l

WVVJ OTl~ 01 -middot bull1 n qtoN bull1-1111 bullbull1111iOOJid bullbullap nat bullbullbullbull1pabull os M~bull 11 3lUOM

r -

-QuJILy -uurJnce Pro)laquot Plan for P1c111o Farm

July 9 1990 Revision No I Pa1e 11 of 33

SO Data Oulllty Ob)eetlvll for Critical Meaturernentt In Terma of ~recllion Accuracy Complett nllt Rtprtllntlt lveneaa and ComparebiiUy

(See PMP QAPP Section 7 9 and Genenc QAPJP Secnon $0 for funher u planauona)

51 Summary

D1t1 Quality Objectives for cnucal musuremen11 durinamp the private well monitorin1 well and soil ampas surveys are summariud in Table $-1

52 AepreMntetlveneu

(See PMO Generic QAPJP Secuon $6 for a furthe r explanarion)

Representati veness is defined in QAMSmiddot00$80 as an expression of the dcaree to which the data accurately and precisely represe ntS a characteristic of a population parameter variations at a samplina point a process condition or an environmental condition The objectives for repre sentativeness are described in the Field Samplin1 Plan Section 20 and this Quality Auunnce Project Plltl Section 30 These objectives will be met throu1h the proper implementation of the Field Samplin1 Plan and the Quali ty Assurance Projcct Plan Each of the surveys wert detiJIICd usin1 infonnat ion obtained durinamp pre vious Sludies and are therefore fcxussed on detectinamp areas of potentiJl contamination and assessin1 current levels of contamination at sites found previously to be contaminated

Compuability is defmed in QAMS-00$80 as an expression of the confidence with which one data set can be compared to another

Data units will be expressed unifonnly for each s~cific site

MNeurement

Concentrltion (aqueous) Concentration (soil aas) Concentration (air) Concentrltion (HNu air) Temperature Distance Conducli vi1y pH radioactivity Maampnetic fie ld Seismic Velocity

Artlur D Little

Units

ugL ugL ugL ppmbullc feelt umhoscmJ pH uni1s pCilamp uCicm aam mas ~secm msecm

~Rihr mRhr

- r -

J

Quahty AlSUIInce Prottct Plan for Plctllo Farm Ju ly 9 1990

Re visaon No I Paac 19 of JJ

0111 Outllly Objectives for Critic Mtesurtmtnls Precision Accurecy 1nd Compltttntll (page 1 or 2)

Levtl ot Anllysbull Mltrlbull

Anllyall P1rameter

EltlmiK Accurtcy

Eltlmlltd P-clskJn Completeness

Laboratory Mtuurtmenu Private WcUt (Sublask 32)

v ow 1242 CLP RAS J CLP RAS Volaules

Monltorina Wdls (Subcask 13)

IV ow CLP RAS CL P RAS CLP RAS TCL VOAs

Field Mcuurtmcnts Soil Gu Survey Subtask 17)

so Volatiles Rttovcry RPO 1011-I IOtt SOO

Privaee and Monitarinl Wells Monthly W3ter Level Mcasuremcms (SubtaskJ 32 13 311 )

ow pH +02 pH un its bull 02 pH units 900 ow Tcmperuure bulllmiddot lmiddotc c ow Conducti vity +middot2111 scal e +middot lloscale

or 10 umhos shyow Depth Hclahl +middot(gt0111 OQI n shy

Health W Safety Support -HNu PID +middot2lo scale bullmiddotI scale

or I ppm ExpiOS1vhy shyRadiation tlllO tlllO 1000

(GciJer Counter)

Maancrometcr Survey (Subtask 3Ji)

NA NA Field Intensity tl aamma tl aamma -6llUAJICOIIArtlurD Little

I

I r I

Quaht) Auurance Proect Plan fot Pic1llo Farm July 9 1990

Revisbullon No 1 Paac 20 ot JJ

Tlble 5-1 (continued page 2 of 2)

~ Of Anltytlt htimlttd AMtrM Mllrlx P1rameter Accuracy

Seink Sutty (Subcask 3 6)

NA NA Wave Velouy 12 btt ttsoluttOn from

2msecto~clsample -ElcVItlon Survey (Subtask 3 8)

NA NA Dm~nce tl fi tl fooc 10010 NA NA Elevauon tOOl ft plusmn001 ft 10010

Maub ow bull Ground Waur sa SOli Gas A bull Ambient AirI

bull aPmiddotRAS bull Objectives for these meuun=ments will be taken from the US EPA Reaion I Ouidme for Vllidltbullna Ora11mc and lnoraanic Data

NA bull Noc AppUcabk

62JS1Aitcltltl

r

Qualuy Assurance Project Plan for PICtllo Farm July 9 1990

ReY tS IOfl No I Pace 21 of Jl

DuMJ the evaluation of the data rtsuluna from thts sue the variabtluy usoctalfd with the data in terms of prectslon accunCy and representameness wtll abo be UJeSsed and tncludcd 10 the diSCUSS IOn of tht datL

10 Swnpllng Procedurtl

f1 Sampling Locltlon tnd Frequency

The samplina locauons and frtquency of samplina for the surveys is Jiven in the Field Samplina Plan Sccuon 30

12 Sampling Proctdurta

Standard OpendnJ ProcedurtJ SOPs) for each of the samplinc openrions and r~ld te ninJ procedures that wtll be undertaken are attached to the Field Samplinc Plan A summary of each of these procedures alon J with a reference to the appropriate SOP is ampiven in Seclion ~ 0 of the Field SamplinJ Plan

eon ivn 1nd Holding nmn These items arc civen in the Field Samplin1 Plan Section 60

Pletd OrtconWmlneUOn ProcKurtl Field decontamination procedures are riven in the followinJ SOPs Field Decoruaminadon of Metal Samplina Equipment SOP No ADL-1009 and Field Dccoruaminarion of Tenon or Glass SamplinJ Equipment SOP No ADL-1008

d Oocumenlallon Procedurn Field documenwion procedu~s art summarized in the PMP Generic QA PjP Section 67 and the followina SOPs Standard OperatinJ Procedures SOP) for Schedulina ARCS Analylical Services SOP No ARC-20 Geotechnical Documentalion SOP No ADLmiddot4014 and Sample Cunody SOP No EPAmiddot IOOI

70 smp Cuetody

Sample custody procedures arc summarized in the PMP Generic QAPjP Section 70 and detai led in Sample Custody SOP No EPA-1001

I

J 6lllARaltlArthwD Little

r

Qu~hty Auunnce ProJeCt Plan for Plclllo Farm July 9 1990

Ruuion No I Po1e ll of ll

10 Clbrltlon Proetdurts

Generll proccdurts for calibrmlion are JIVtn 1n the PMO Generic QAP]P Secrion 10 Calibrttion procedures for the analysiS of volaule oraanics in the private well water an Jiven in Me1hod j242 Methoda for the Oetcnnjnarion olt Orllnki Compoonda jn Drinlqnr WIC[ EPA60014-88039 and ror he analysis of volaule oraanks In the monuonna well ampfOUnd water in US EPA Concrct Laboratory Propam (aP Statement of Work for the Analysts of Volanle Oraanics February 1988

Calibnrion procedures and frequency for other critical measuremenu 13 summarized in Table 8middot 1 wuh the appropriate references

ArtlurD Little

- r I

QuaHy Auunnce ProjtCI Plan for Ptc1ilo Fann July 9 1990

Revtston No I pbullbull ll ol JJ

Otttctton Limit V~IUie Organic Compound ugl Soli G11

lll-Trkhloltoellane ITCAJ 0000

Trkhloroelllene (TCEJ 00001

Me1hylcne Chloride 0002

Toluene 002

002

~-n = =U

bull Acetone may be subsntuted for ylcnes dependent on initial results

AltlurD Little

- r -

QuJiuy Anur1ncc ProJtCI Plan for Plc111o Farm July 9 1990

ReviSIOn No I p 16 ol ))

0 Protect Orgenlutlon and Anponsfblllty

See PMP QAPP Secuon 7 a for funher tllplanauon of quahty assurance responsibilhies and projtct oraaniuuon and PMP Section 2 0 for overall proaram responsibiliues )

llclllo bull lroject Sttt

Pmjec1 Manaaer Roben Lambc

Health and Safc ry Project Manaacrmiddot Davtd lscnberJ

lrogrem ~ent Office Staff

Deputy Proampnm Manaacr David Lanascth

Qualily Assurance Officer Richard Waterman (responsibili ties include project speciftc performancesys te ms audits)

Lead Chemis1 Roben O Nc1l

Health and Safety Officer Corey Bnus

The project oraanization and re sponsibilities are shown in Fiaure 4-1

ArtlurD Little

--

-(_

Figure 4-l Proect OJgMizat- Slruct

L EPA~~ J [)ane Kelley r --- --

I

~ IL J I

David Langseth L J I Ii

l

__J I

l ADL EPA- Jl I PrcgtJoc~ David Isenbergl J L J JRobert Lambe Anna Ktasko

_l c-- l I DIU Subcont-ctors~

Kristen Steck Scot Foster Kalhy Thrun Phil Aury - -RolgtertONei Tony IAajahad (To be selected]

Task2 Tasks 35 Tasks 135 Tasks 35

Task4

1 Task3

JeH Fonnermiddot Kevin KuecNer

Kevin Cahil

Tasks 35 middoton site tleallh and Sakgtty COOidmaKw

middot middotmiddotmiddot r~~ middot~ OliOOJll IAUVlUSUrrl-0yen IUtbull ft30P Mil 10 bulln-bull M(l

WVVJ OTl~ 01 -middot bull1 n qtoN bull1-1111 bullbull1111iOOJid bullbullap nat bullbullbullbull1pabull os M~bull 11 3lUOM

r -

-QuJILy -uurJnce Pro)laquot Plan for P1c111o Farm

July 9 1990 Revision No I Pa1e 11 of 33

SO Data Oulllty Ob)eetlvll for Critical Meaturernentt In Terma of ~recllion Accuracy Complett nllt Rtprtllntlt lveneaa and ComparebiiUy

(See PMP QAPP Section 7 9 and Genenc QAPJP Secnon $0 for funher u planauona)

51 Summary

D1t1 Quality Objectives for cnucal musuremen11 durinamp the private well monitorin1 well and soil ampas surveys are summariud in Table $-1

52 AepreMntetlveneu

(See PMO Generic QAPJP Secuon $6 for a furthe r explanarion)

Representati veness is defined in QAMSmiddot00$80 as an expression of the dcaree to which the data accurately and precisely represe ntS a characteristic of a population parameter variations at a samplina point a process condition or an environmental condition The objectives for repre sentativeness are described in the Field Samplin1 Plan Section 20 and this Quality Auunnce Project Plltl Section 30 These objectives will be met throu1h the proper implementation of the Field Samplin1 Plan and the Quali ty Assurance Projcct Plan Each of the surveys wert detiJIICd usin1 infonnat ion obtained durinamp pre vious Sludies and are therefore fcxussed on detectinamp areas of potentiJl contamination and assessin1 current levels of contamination at sites found previously to be contaminated

Compuability is defmed in QAMS-00$80 as an expression of the confidence with which one data set can be compared to another

Data units will be expressed unifonnly for each s~cific site

MNeurement

Concentrltion (aqueous) Concentration (soil aas) Concentration (air) Concentrltion (HNu air) Temperature Distance Conducli vi1y pH radioactivity Maampnetic fie ld Seismic Velocity

Artlur D Little

Units

ugL ugL ugL ppmbullc feelt umhoscmJ pH uni1s pCilamp uCicm aam mas ~secm msecm

~Rihr mRhr

- r -

J

Quahty AlSUIInce Prottct Plan for Plctllo Farm Ju ly 9 1990

Re visaon No I Paac 19 of JJ

0111 Outllly Objectives for Critic Mtesurtmtnls Precision Accurecy 1nd Compltttntll (page 1 or 2)

Levtl ot Anllysbull Mltrlbull

Anllyall P1rameter

EltlmiK Accurtcy

Eltlmlltd P-clskJn Completeness

Laboratory Mtuurtmenu Private WcUt (Sublask 32)

v ow 1242 CLP RAS J CLP RAS Volaules

Monltorina Wdls (Subcask 13)

IV ow CLP RAS CL P RAS CLP RAS TCL VOAs

Field Mcuurtmcnts Soil Gu Survey Subtask 17)

so Volatiles Rttovcry RPO 1011-I IOtt SOO

Privaee and Monitarinl Wells Monthly W3ter Level Mcasuremcms (SubtaskJ 32 13 311 )

ow pH +02 pH un its bull 02 pH units 900 ow Tcmperuure bulllmiddot lmiddotc c ow Conducti vity +middot2111 scal e +middot lloscale

or 10 umhos shyow Depth Hclahl +middot(gt0111 OQI n shy

Health W Safety Support -HNu PID +middot2lo scale bullmiddotI scale

or I ppm ExpiOS1vhy shyRadiation tlllO tlllO 1000

(GciJer Counter)

Maancrometcr Survey (Subtask 3Ji)

NA NA Field Intensity tl aamma tl aamma -6llUAJICOIIArtlurD Little

I

I r I

Quaht) Auurance Proect Plan fot Pic1llo Farm July 9 1990

Revisbullon No 1 Paac 20 ot JJ

Tlble 5-1 (continued page 2 of 2)

~ Of Anltytlt htimlttd AMtrM Mllrlx P1rameter Accuracy

Seink Sutty (Subcask 3 6)

NA NA Wave Velouy 12 btt ttsoluttOn from

2msecto~clsample -ElcVItlon Survey (Subtask 3 8)

NA NA Dm~nce tl fi tl fooc 10010 NA NA Elevauon tOOl ft plusmn001 ft 10010

Maub ow bull Ground Waur sa SOli Gas A bull Ambient AirI

bull aPmiddotRAS bull Objectives for these meuun=ments will be taken from the US EPA Reaion I Ouidme for Vllidltbullna Ora11mc and lnoraanic Data

NA bull Noc AppUcabk

62JS1Aitcltltl

r

Qualuy Assurance Project Plan for PICtllo Farm July 9 1990

ReY tS IOfl No I Pace 21 of Jl

DuMJ the evaluation of the data rtsuluna from thts sue the variabtluy usoctalfd with the data in terms of prectslon accunCy and representameness wtll abo be UJeSsed and tncludcd 10 the diSCUSS IOn of tht datL

10 Swnpllng Procedurtl

f1 Sampling Locltlon tnd Frequency

The samplina locauons and frtquency of samplina for the surveys is Jiven in the Field Samplina Plan Sccuon 30

12 Sampling Proctdurta

Standard OpendnJ ProcedurtJ SOPs) for each of the samplinc openrions and r~ld te ninJ procedures that wtll be undertaken are attached to the Field Samplinc Plan A summary of each of these procedures alon J with a reference to the appropriate SOP is ampiven in Seclion ~ 0 of the Field SamplinJ Plan

eon ivn 1nd Holding nmn These items arc civen in the Field Samplin1 Plan Section 60

Pletd OrtconWmlneUOn ProcKurtl Field decontamination procedures are riven in the followinJ SOPs Field Decoruaminadon of Metal Samplina Equipment SOP No ADL-1009 and Field Dccoruaminarion of Tenon or Glass SamplinJ Equipment SOP No ADL-1008

d Oocumenlallon Procedurn Field documenwion procedu~s art summarized in the PMP Generic QA PjP Section 67 and the followina SOPs Standard OperatinJ Procedures SOP) for Schedulina ARCS Analylical Services SOP No ARC-20 Geotechnical Documentalion SOP No ADLmiddot4014 and Sample Cunody SOP No EPAmiddot IOOI

70 smp Cuetody

Sample custody procedures arc summarized in the PMP Generic QAPjP Section 70 and detai led in Sample Custody SOP No EPA-1001

I

J 6lllARaltlArthwD Little

r

Qu~hty Auunnce ProJeCt Plan for Plclllo Farm July 9 1990

Ruuion No I Po1e ll of ll

10 Clbrltlon Proetdurts

Generll proccdurts for calibrmlion are JIVtn 1n the PMO Generic QAP]P Secrion 10 Calibrttion procedures for the analysiS of volaule oraanics in the private well water an Jiven in Me1hod j242 Methoda for the Oetcnnjnarion olt Orllnki Compoonda jn Drinlqnr WIC[ EPA60014-88039 and ror he analysis of volaule oraanks In the monuonna well ampfOUnd water in US EPA Concrct Laboratory Propam (aP Statement of Work for the Analysts of Volanle Oraanics February 1988

Calibnrion procedures and frequency for other critical measuremenu 13 summarized in Table 8middot 1 wuh the appropriate references

ArtlurD Little

- r -

QuJiuy Anur1ncc ProJtCI Plan for Plc111o Farm July 9 1990

ReviSIOn No I p 16 ol ))

0 Protect Orgenlutlon and Anponsfblllty

See PMP QAPP Secuon 7 a for funher tllplanauon of quahty assurance responsibilhies and projtct oraaniuuon and PMP Section 2 0 for overall proaram responsibiliues )

llclllo bull lroject Sttt

Pmjec1 Manaaer Roben Lambc

Health and Safc ry Project Manaacrmiddot Davtd lscnberJ

lrogrem ~ent Office Staff

Deputy Proampnm Manaacr David Lanascth

Qualily Assurance Officer Richard Waterman (responsibili ties include project speciftc performancesys te ms audits)

Lead Chemis1 Roben O Nc1l

Health and Safety Officer Corey Bnus

The project oraanization and re sponsibilities are shown in Fiaure 4-1

ArtlurD Little

--

-(_

Figure 4-l Proect OJgMizat- Slruct

L EPA~~ J [)ane Kelley r --- --

I

~ IL J I

David Langseth L J I Ii

l

__J I

l ADL EPA- Jl I PrcgtJoc~ David Isenbergl J L J JRobert Lambe Anna Ktasko

_l c-- l I DIU Subcont-ctors~

Kristen Steck Scot Foster Kalhy Thrun Phil Aury - -RolgtertONei Tony IAajahad (To be selected]

Task2 Tasks 35 Tasks 135 Tasks 35

Task4

1 Task3

JeH Fonnermiddot Kevin KuecNer

Kevin Cahil

Tasks 35 middoton site tleallh and Sakgtty COOidmaKw

middot middotmiddotmiddot r~~ middot~ OliOOJll IAUVlUSUrrl-0yen IUtbull ft30P Mil 10 bulln-bull M(l

WVVJ OTl~ 01 -middot bull1 n qtoN bull1-1111 bullbull1111iOOJid bullbullap nat bullbullbullbull1pabull os M~bull 11 3lUOM

r -

-QuJILy -uurJnce Pro)laquot Plan for P1c111o Farm

July 9 1990 Revision No I Pa1e 11 of 33

SO Data Oulllty Ob)eetlvll for Critical Meaturernentt In Terma of ~recllion Accuracy Complett nllt Rtprtllntlt lveneaa and ComparebiiUy

(See PMP QAPP Section 7 9 and Genenc QAPJP Secnon $0 for funher u planauona)

51 Summary

D1t1 Quality Objectives for cnucal musuremen11 durinamp the private well monitorin1 well and soil ampas surveys are summariud in Table $-1

52 AepreMntetlveneu

(See PMO Generic QAPJP Secuon $6 for a furthe r explanarion)

Representati veness is defined in QAMSmiddot00$80 as an expression of the dcaree to which the data accurately and precisely represe ntS a characteristic of a population parameter variations at a samplina point a process condition or an environmental condition The objectives for repre sentativeness are described in the Field Samplin1 Plan Section 20 and this Quality Auunnce Project Plltl Section 30 These objectives will be met throu1h the proper implementation of the Field Samplin1 Plan and the Quali ty Assurance Projcct Plan Each of the surveys wert detiJIICd usin1 infonnat ion obtained durinamp pre vious Sludies and are therefore fcxussed on detectinamp areas of potentiJl contamination and assessin1 current levels of contamination at sites found previously to be contaminated

Compuability is defmed in QAMS-00$80 as an expression of the confidence with which one data set can be compared to another

Data units will be expressed unifonnly for each s~cific site

MNeurement

Concentrltion (aqueous) Concentration (soil aas) Concentration (air) Concentrltion (HNu air) Temperature Distance Conducli vi1y pH radioactivity Maampnetic fie ld Seismic Velocity

Artlur D Little

Units

ugL ugL ugL ppmbullc feelt umhoscmJ pH uni1s pCilamp uCicm aam mas ~secm msecm

~Rihr mRhr

- r -

J

Quahty AlSUIInce Prottct Plan for Plctllo Farm Ju ly 9 1990

Re visaon No I Paac 19 of JJ

0111 Outllly Objectives for Critic Mtesurtmtnls Precision Accurecy 1nd Compltttntll (page 1 or 2)

Levtl ot Anllysbull Mltrlbull

Anllyall P1rameter

EltlmiK Accurtcy

Eltlmlltd P-clskJn Completeness

Laboratory Mtuurtmenu Private WcUt (Sublask 32)

v ow 1242 CLP RAS J CLP RAS Volaules

Monltorina Wdls (Subcask 13)

IV ow CLP RAS CL P RAS CLP RAS TCL VOAs

Field Mcuurtmcnts Soil Gu Survey Subtask 17)

so Volatiles Rttovcry RPO 1011-I IOtt SOO

Privaee and Monitarinl Wells Monthly W3ter Level Mcasuremcms (SubtaskJ 32 13 311 )

ow pH +02 pH un its bull 02 pH units 900 ow Tcmperuure bulllmiddot lmiddotc c ow Conducti vity +middot2111 scal e +middot lloscale

or 10 umhos shyow Depth Hclahl +middot(gt0111 OQI n shy

Health W Safety Support -HNu PID +middot2lo scale bullmiddotI scale

or I ppm ExpiOS1vhy shyRadiation tlllO tlllO 1000

(GciJer Counter)

Maancrometcr Survey (Subtask 3Ji)

NA NA Field Intensity tl aamma tl aamma -6llUAJICOIIArtlurD Little

I

I r I

Quaht) Auurance Proect Plan fot Pic1llo Farm July 9 1990

Revisbullon No 1 Paac 20 ot JJ

Tlble 5-1 (continued page 2 of 2)

~ Of Anltytlt htimlttd AMtrM Mllrlx P1rameter Accuracy

Seink Sutty (Subcask 3 6)

NA NA Wave Velouy 12 btt ttsoluttOn from

2msecto~clsample -ElcVItlon Survey (Subtask 3 8)

NA NA Dm~nce tl fi tl fooc 10010 NA NA Elevauon tOOl ft plusmn001 ft 10010

Maub ow bull Ground Waur sa SOli Gas A bull Ambient AirI

bull aPmiddotRAS bull Objectives for these meuun=ments will be taken from the US EPA Reaion I Ouidme for Vllidltbullna Ora11mc and lnoraanic Data

NA bull Noc AppUcabk

62JS1Aitcltltl

r

Qualuy Assurance Project Plan for PICtllo Farm July 9 1990

ReY tS IOfl No I Pace 21 of Jl

DuMJ the evaluation of the data rtsuluna from thts sue the variabtluy usoctalfd with the data in terms of prectslon accunCy and representameness wtll abo be UJeSsed and tncludcd 10 the diSCUSS IOn of tht datL

10 Swnpllng Procedurtl

f1 Sampling Locltlon tnd Frequency

The samplina locauons and frtquency of samplina for the surveys is Jiven in the Field Samplina Plan Sccuon 30

12 Sampling Proctdurta

Standard OpendnJ ProcedurtJ SOPs) for each of the samplinc openrions and r~ld te ninJ procedures that wtll be undertaken are attached to the Field Samplinc Plan A summary of each of these procedures alon J with a reference to the appropriate SOP is ampiven in Seclion ~ 0 of the Field SamplinJ Plan

eon ivn 1nd Holding nmn These items arc civen in the Field Samplin1 Plan Section 60

Pletd OrtconWmlneUOn ProcKurtl Field decontamination procedures are riven in the followinJ SOPs Field Decoruaminadon of Metal Samplina Equipment SOP No ADL-1009 and Field Dccoruaminarion of Tenon or Glass SamplinJ Equipment SOP No ADL-1008

d Oocumenlallon Procedurn Field documenwion procedu~s art summarized in the PMP Generic QA PjP Section 67 and the followina SOPs Standard OperatinJ Procedures SOP) for Schedulina ARCS Analylical Services SOP No ARC-20 Geotechnical Documentalion SOP No ADLmiddot4014 and Sample Cunody SOP No EPAmiddot IOOI

70 smp Cuetody

Sample custody procedures arc summarized in the PMP Generic QAPjP Section 70 and detai led in Sample Custody SOP No EPA-1001

I

J 6lllARaltlArthwD Little

r

Qu~hty Auunnce ProJeCt Plan for Plclllo Farm July 9 1990

Ruuion No I Po1e ll of ll

10 Clbrltlon Proetdurts

Generll proccdurts for calibrmlion are JIVtn 1n the PMO Generic QAP]P Secrion 10 Calibrttion procedures for the analysiS of volaule oraanics in the private well water an Jiven in Me1hod j242 Methoda for the Oetcnnjnarion olt Orllnki Compoonda jn Drinlqnr WIC[ EPA60014-88039 and ror he analysis of volaule oraanks In the monuonna well ampfOUnd water in US EPA Concrct Laboratory Propam (aP Statement of Work for the Analysts of Volanle Oraanics February 1988

Calibnrion procedures and frequency for other critical measuremenu 13 summarized in Table 8middot 1 wuh the appropriate references

ArtlurD Little

--

-(_

Figure 4-l Proect OJgMizat- Slruct

L EPA~~ J [)ane Kelley r --- --

I

~ IL J I

David Langseth L J I Ii

l

__J I

l ADL EPA- Jl I PrcgtJoc~ David Isenbergl J L J JRobert Lambe Anna Ktasko

_l c-- l I DIU Subcont-ctors~

Kristen Steck Scot Foster Kalhy Thrun Phil Aury - -RolgtertONei Tony IAajahad (To be selected]

Task2 Tasks 35 Tasks 135 Tasks 35

Task4

1 Task3

JeH Fonnermiddot Kevin KuecNer

Kevin Cahil

Tasks 35 middoton site tleallh and Sakgtty COOidmaKw

middot middotmiddotmiddot r~~ middot~ OliOOJll IAUVlUSUrrl-0yen IUtbull ft30P Mil 10 bulln-bull M(l

WVVJ OTl~ 01 -middot bull1 n qtoN bull1-1111 bullbull1111iOOJid bullbullap nat bullbullbullbull1pabull os M~bull 11 3lUOM

r -

-QuJILy -uurJnce Pro)laquot Plan for P1c111o Farm

July 9 1990 Revision No I Pa1e 11 of 33

SO Data Oulllty Ob)eetlvll for Critical Meaturernentt In Terma of ~recllion Accuracy Complett nllt Rtprtllntlt lveneaa and ComparebiiUy

(See PMP QAPP Section 7 9 and Genenc QAPJP Secnon $0 for funher u planauona)

51 Summary

D1t1 Quality Objectives for cnucal musuremen11 durinamp the private well monitorin1 well and soil ampas surveys are summariud in Table $-1

52 AepreMntetlveneu

(See PMO Generic QAPJP Secuon $6 for a furthe r explanarion)

Representati veness is defined in QAMSmiddot00$80 as an expression of the dcaree to which the data accurately and precisely represe ntS a characteristic of a population parameter variations at a samplina point a process condition or an environmental condition The objectives for repre sentativeness are described in the Field Samplin1 Plan Section 20 and this Quality Auunnce Project Plltl Section 30 These objectives will be met throu1h the proper implementation of the Field Samplin1 Plan and the Quali ty Assurance Projcct Plan Each of the surveys wert detiJIICd usin1 infonnat ion obtained durinamp pre vious Sludies and are therefore fcxussed on detectinamp areas of potentiJl contamination and assessin1 current levels of contamination at sites found previously to be contaminated

Compuability is defmed in QAMS-00$80 as an expression of the confidence with which one data set can be compared to another

Data units will be expressed unifonnly for each s~cific site

MNeurement

Concentrltion (aqueous) Concentration (soil aas) Concentration (air) Concentrltion (HNu air) Temperature Distance Conducli vi1y pH radioactivity Maampnetic fie ld Seismic Velocity

Artlur D Little

Units

ugL ugL ugL ppmbullc feelt umhoscmJ pH uni1s pCilamp uCicm aam mas ~secm msecm

~Rihr mRhr

- r -

J

Quahty AlSUIInce Prottct Plan for Plctllo Farm Ju ly 9 1990

Re visaon No I Paac 19 of JJ

0111 Outllly Objectives for Critic Mtesurtmtnls Precision Accurecy 1nd Compltttntll (page 1 or 2)

Levtl ot Anllysbull Mltrlbull

Anllyall P1rameter

EltlmiK Accurtcy

Eltlmlltd P-clskJn Completeness

Laboratory Mtuurtmenu Private WcUt (Sublask 32)

v ow 1242 CLP RAS J CLP RAS Volaules

Monltorina Wdls (Subcask 13)

IV ow CLP RAS CL P RAS CLP RAS TCL VOAs

Field Mcuurtmcnts Soil Gu Survey Subtask 17)

so Volatiles Rttovcry RPO 1011-I IOtt SOO

Privaee and Monitarinl Wells Monthly W3ter Level Mcasuremcms (SubtaskJ 32 13 311 )

ow pH +02 pH un its bull 02 pH units 900 ow Tcmperuure bulllmiddot lmiddotc c ow Conducti vity +middot2111 scal e +middot lloscale

or 10 umhos shyow Depth Hclahl +middot(gt0111 OQI n shy

Health W Safety Support -HNu PID +middot2lo scale bullmiddotI scale

or I ppm ExpiOS1vhy shyRadiation tlllO tlllO 1000

(GciJer Counter)

Maancrometcr Survey (Subtask 3Ji)

NA NA Field Intensity tl aamma tl aamma -6llUAJICOIIArtlurD Little

I

I r I

Quaht) Auurance Proect Plan fot Pic1llo Farm July 9 1990

Revisbullon No 1 Paac 20 ot JJ

Tlble 5-1 (continued page 2 of 2)

~ Of Anltytlt htimlttd AMtrM Mllrlx P1rameter Accuracy

Seink Sutty (Subcask 3 6)

NA NA Wave Velouy 12 btt ttsoluttOn from

2msecto~clsample -ElcVItlon Survey (Subtask 3 8)

NA NA Dm~nce tl fi tl fooc 10010 NA NA Elevauon tOOl ft plusmn001 ft 10010

Maub ow bull Ground Waur sa SOli Gas A bull Ambient AirI

bull aPmiddotRAS bull Objectives for these meuun=ments will be taken from the US EPA Reaion I Ouidme for Vllidltbullna Ora11mc and lnoraanic Data

NA bull Noc AppUcabk

62JS1Aitcltltl

r

Qualuy Assurance Project Plan for PICtllo Farm July 9 1990

ReY tS IOfl No I Pace 21 of Jl

DuMJ the evaluation of the data rtsuluna from thts sue the variabtluy usoctalfd with the data in terms of prectslon accunCy and representameness wtll abo be UJeSsed and tncludcd 10 the diSCUSS IOn of tht datL

10 Swnpllng Procedurtl

f1 Sampling Locltlon tnd Frequency

The samplina locauons and frtquency of samplina for the surveys is Jiven in the Field Samplina Plan Sccuon 30

12 Sampling Proctdurta

Standard OpendnJ ProcedurtJ SOPs) for each of the samplinc openrions and r~ld te ninJ procedures that wtll be undertaken are attached to the Field Samplinc Plan A summary of each of these procedures alon J with a reference to the appropriate SOP is ampiven in Seclion ~ 0 of the Field SamplinJ Plan

eon ivn 1nd Holding nmn These items arc civen in the Field Samplin1 Plan Section 60

Pletd OrtconWmlneUOn ProcKurtl Field decontamination procedures are riven in the followinJ SOPs Field Decoruaminadon of Metal Samplina Equipment SOP No ADL-1009 and Field Dccoruaminarion of Tenon or Glass SamplinJ Equipment SOP No ADL-1008

d Oocumenlallon Procedurn Field documenwion procedu~s art summarized in the PMP Generic QA PjP Section 67 and the followina SOPs Standard OperatinJ Procedures SOP) for Schedulina ARCS Analylical Services SOP No ARC-20 Geotechnical Documentalion SOP No ADLmiddot4014 and Sample Cunody SOP No EPAmiddot IOOI

70 smp Cuetody

Sample custody procedures arc summarized in the PMP Generic QAPjP Section 70 and detai led in Sample Custody SOP No EPA-1001

I

J 6lllARaltlArthwD Little

r

Qu~hty Auunnce ProJeCt Plan for Plclllo Farm July 9 1990

Ruuion No I Po1e ll of ll

10 Clbrltlon Proetdurts

Generll proccdurts for calibrmlion are JIVtn 1n the PMO Generic QAP]P Secrion 10 Calibrttion procedures for the analysiS of volaule oraanics in the private well water an Jiven in Me1hod j242 Methoda for the Oetcnnjnarion olt Orllnki Compoonda jn Drinlqnr WIC[ EPA60014-88039 and ror he analysis of volaule oraanks In the monuonna well ampfOUnd water in US EPA Concrct Laboratory Propam (aP Statement of Work for the Analysts of Volanle Oraanics February 1988

Calibnrion procedures and frequency for other critical measuremenu 13 summarized in Table 8middot 1 wuh the appropriate references

ArtlurD Little

r -

-QuJILy -uurJnce Pro)laquot Plan for P1c111o Farm

July 9 1990 Revision No I Pa1e 11 of 33

SO Data Oulllty Ob)eetlvll for Critical Meaturernentt In Terma of ~recllion Accuracy Complett nllt Rtprtllntlt lveneaa and ComparebiiUy

(See PMP QAPP Section 7 9 and Genenc QAPJP Secnon $0 for funher u planauona)

51 Summary

D1t1 Quality Objectives for cnucal musuremen11 durinamp the private well monitorin1 well and soil ampas surveys are summariud in Table $-1

52 AepreMntetlveneu

(See PMO Generic QAPJP Secuon $6 for a furthe r explanarion)

Representati veness is defined in QAMSmiddot00$80 as an expression of the dcaree to which the data accurately and precisely represe ntS a characteristic of a population parameter variations at a samplina point a process condition or an environmental condition The objectives for repre sentativeness are described in the Field Samplin1 Plan Section 20 and this Quality Auunnce Project Plltl Section 30 These objectives will be met throu1h the proper implementation of the Field Samplin1 Plan and the Quali ty Assurance Projcct Plan Each of the surveys wert detiJIICd usin1 infonnat ion obtained durinamp pre vious Sludies and are therefore fcxussed on detectinamp areas of potentiJl contamination and assessin1 current levels of contamination at sites found previously to be contaminated

Compuability is defmed in QAMS-00$80 as an expression of the confidence with which one data set can be compared to another

Data units will be expressed unifonnly for each s~cific site

MNeurement

Concentrltion (aqueous) Concentration (soil aas) Concentration (air) Concentrltion (HNu air) Temperature Distance Conducli vi1y pH radioactivity Maampnetic fie ld Seismic Velocity

Artlur D Little

Units

ugL ugL ugL ppmbullc feelt umhoscmJ pH uni1s pCilamp uCicm aam mas ~secm msecm

~Rihr mRhr

- r -

J

Quahty AlSUIInce Prottct Plan for Plctllo Farm Ju ly 9 1990

Re visaon No I Paac 19 of JJ

0111 Outllly Objectives for Critic Mtesurtmtnls Precision Accurecy 1nd Compltttntll (page 1 or 2)

Levtl ot Anllysbull Mltrlbull

Anllyall P1rameter

EltlmiK Accurtcy

Eltlmlltd P-clskJn Completeness

Laboratory Mtuurtmenu Private WcUt (Sublask 32)

v ow 1242 CLP RAS J CLP RAS Volaules

Monltorina Wdls (Subcask 13)

IV ow CLP RAS CL P RAS CLP RAS TCL VOAs

Field Mcuurtmcnts Soil Gu Survey Subtask 17)

so Volatiles Rttovcry RPO 1011-I IOtt SOO

Privaee and Monitarinl Wells Monthly W3ter Level Mcasuremcms (SubtaskJ 32 13 311 )

ow pH +02 pH un its bull 02 pH units 900 ow Tcmperuure bulllmiddot lmiddotc c ow Conducti vity +middot2111 scal e +middot lloscale

or 10 umhos shyow Depth Hclahl +middot(gt0111 OQI n shy

Health W Safety Support -HNu PID +middot2lo scale bullmiddotI scale

or I ppm ExpiOS1vhy shyRadiation tlllO tlllO 1000

(GciJer Counter)

Maancrometcr Survey (Subtask 3Ji)

NA NA Field Intensity tl aamma tl aamma -6llUAJICOIIArtlurD Little

I

I r I

Quaht) Auurance Proect Plan fot Pic1llo Farm July 9 1990

Revisbullon No 1 Paac 20 ot JJ

Tlble 5-1 (continued page 2 of 2)

~ Of Anltytlt htimlttd AMtrM Mllrlx P1rameter Accuracy

Seink Sutty (Subcask 3 6)

NA NA Wave Velouy 12 btt ttsoluttOn from

2msecto~clsample -ElcVItlon Survey (Subtask 3 8)

NA NA Dm~nce tl fi tl fooc 10010 NA NA Elevauon tOOl ft plusmn001 ft 10010

Maub ow bull Ground Waur sa SOli Gas A bull Ambient AirI

bull aPmiddotRAS bull Objectives for these meuun=ments will be taken from the US EPA Reaion I Ouidme for Vllidltbullna Ora11mc and lnoraanic Data

NA bull Noc AppUcabk

62JS1Aitcltltl

r

Qualuy Assurance Project Plan for PICtllo Farm July 9 1990

ReY tS IOfl No I Pace 21 of Jl

DuMJ the evaluation of the data rtsuluna from thts sue the variabtluy usoctalfd with the data in terms of prectslon accunCy and representameness wtll abo be UJeSsed and tncludcd 10 the diSCUSS IOn of tht datL

10 Swnpllng Procedurtl

f1 Sampling Locltlon tnd Frequency

The samplina locauons and frtquency of samplina for the surveys is Jiven in the Field Samplina Plan Sccuon 30

12 Sampling Proctdurta

Standard OpendnJ ProcedurtJ SOPs) for each of the samplinc openrions and r~ld te ninJ procedures that wtll be undertaken are attached to the Field Samplinc Plan A summary of each of these procedures alon J with a reference to the appropriate SOP is ampiven in Seclion ~ 0 of the Field SamplinJ Plan

eon ivn 1nd Holding nmn These items arc civen in the Field Samplin1 Plan Section 60

Pletd OrtconWmlneUOn ProcKurtl Field decontamination procedures are riven in the followinJ SOPs Field Decoruaminadon of Metal Samplina Equipment SOP No ADL-1009 and Field Dccoruaminarion of Tenon or Glass SamplinJ Equipment SOP No ADL-1008

d Oocumenlallon Procedurn Field documenwion procedu~s art summarized in the PMP Generic QA PjP Section 67 and the followina SOPs Standard OperatinJ Procedures SOP) for Schedulina ARCS Analylical Services SOP No ARC-20 Geotechnical Documentalion SOP No ADLmiddot4014 and Sample Cunody SOP No EPAmiddot IOOI

70 smp Cuetody

Sample custody procedures arc summarized in the PMP Generic QAPjP Section 70 and detai led in Sample Custody SOP No EPA-1001

I

J 6lllARaltlArthwD Little

r

Qu~hty Auunnce ProJeCt Plan for Plclllo Farm July 9 1990

Ruuion No I Po1e ll of ll

10 Clbrltlon Proetdurts

Generll proccdurts for calibrmlion are JIVtn 1n the PMO Generic QAP]P Secrion 10 Calibrttion procedures for the analysiS of volaule oraanics in the private well water an Jiven in Me1hod j242 Methoda for the Oetcnnjnarion olt Orllnki Compoonda jn Drinlqnr WIC[ EPA60014-88039 and ror he analysis of volaule oraanks In the monuonna well ampfOUnd water in US EPA Concrct Laboratory Propam (aP Statement of Work for the Analysts of Volanle Oraanics February 1988

Calibnrion procedures and frequency for other critical measuremenu 13 summarized in Table 8middot 1 wuh the appropriate references

ArtlurD Little

- r -

J

Quahty AlSUIInce Prottct Plan for Plctllo Farm Ju ly 9 1990

Re visaon No I Paac 19 of JJ

0111 Outllly Objectives for Critic Mtesurtmtnls Precision Accurecy 1nd Compltttntll (page 1 or 2)

Levtl ot Anllysbull Mltrlbull

Anllyall P1rameter

EltlmiK Accurtcy

Eltlmlltd P-clskJn Completeness

Laboratory Mtuurtmenu Private WcUt (Sublask 32)

v ow 1242 CLP RAS J CLP RAS Volaules

Monltorina Wdls (Subcask 13)

IV ow CLP RAS CL P RAS CLP RAS TCL VOAs

Field Mcuurtmcnts Soil Gu Survey Subtask 17)

so Volatiles Rttovcry RPO 1011-I IOtt SOO

Privaee and Monitarinl Wells Monthly W3ter Level Mcasuremcms (SubtaskJ 32 13 311 )

ow pH +02 pH un its bull 02 pH units 900 ow Tcmperuure bulllmiddot lmiddotc c ow Conducti vity +middot2111 scal e +middot lloscale

or 10 umhos shyow Depth Hclahl +middot(gt0111 OQI n shy

Health W Safety Support -HNu PID +middot2lo scale bullmiddotI scale

or I ppm ExpiOS1vhy shyRadiation tlllO tlllO 1000

(GciJer Counter)

Maancrometcr Survey (Subtask 3Ji)

NA NA Field Intensity tl aamma tl aamma -6llUAJICOIIArtlurD Little

I

I r I

Quaht) Auurance Proect Plan fot Pic1llo Farm July 9 1990

Revisbullon No 1 Paac 20 ot JJ

Tlble 5-1 (continued page 2 of 2)

~ Of Anltytlt htimlttd AMtrM Mllrlx P1rameter Accuracy

Seink Sutty (Subcask 3 6)

NA NA Wave Velouy 12 btt ttsoluttOn from

2msecto~clsample -ElcVItlon Survey (Subtask 3 8)

NA NA Dm~nce tl fi tl fooc 10010 NA NA Elevauon tOOl ft plusmn001 ft 10010

Maub ow bull Ground Waur sa SOli Gas A bull Ambient AirI

bull aPmiddotRAS bull Objectives for these meuun=ments will be taken from the US EPA Reaion I Ouidme for Vllidltbullna Ora11mc and lnoraanic Data

NA bull Noc AppUcabk

62JS1Aitcltltl

r

Qualuy Assurance Project Plan for PICtllo Farm July 9 1990

ReY tS IOfl No I Pace 21 of Jl

DuMJ the evaluation of the data rtsuluna from thts sue the variabtluy usoctalfd with the data in terms of prectslon accunCy and representameness wtll abo be UJeSsed and tncludcd 10 the diSCUSS IOn of tht datL

10 Swnpllng Procedurtl

f1 Sampling Locltlon tnd Frequency

The samplina locauons and frtquency of samplina for the surveys is Jiven in the Field Samplina Plan Sccuon 30

12 Sampling Proctdurta

Standard OpendnJ ProcedurtJ SOPs) for each of the samplinc openrions and r~ld te ninJ procedures that wtll be undertaken are attached to the Field Samplinc Plan A summary of each of these procedures alon J with a reference to the appropriate SOP is ampiven in Seclion ~ 0 of the Field SamplinJ Plan

eon ivn 1nd Holding nmn These items arc civen in the Field Samplin1 Plan Section 60

Pletd OrtconWmlneUOn ProcKurtl Field decontamination procedures are riven in the followinJ SOPs Field Decoruaminadon of Metal Samplina Equipment SOP No ADL-1009 and Field Dccoruaminarion of Tenon or Glass SamplinJ Equipment SOP No ADL-1008

d Oocumenlallon Procedurn Field documenwion procedu~s art summarized in the PMP Generic QA PjP Section 67 and the followina SOPs Standard OperatinJ Procedures SOP) for Schedulina ARCS Analylical Services SOP No ARC-20 Geotechnical Documentalion SOP No ADLmiddot4014 and Sample Cunody SOP No EPAmiddot IOOI

70 smp Cuetody

Sample custody procedures arc summarized in the PMP Generic QAPjP Section 70 and detai led in Sample Custody SOP No EPA-1001

I

J 6lllARaltlArthwD Little

r

Qu~hty Auunnce ProJeCt Plan for Plclllo Farm July 9 1990

Ruuion No I Po1e ll of ll

10 Clbrltlon Proetdurts

Generll proccdurts for calibrmlion are JIVtn 1n the PMO Generic QAP]P Secrion 10 Calibrttion procedures for the analysiS of volaule oraanics in the private well water an Jiven in Me1hod j242 Methoda for the Oetcnnjnarion olt Orllnki Compoonda jn Drinlqnr WIC[ EPA60014-88039 and ror he analysis of volaule oraanks In the monuonna well ampfOUnd water in US EPA Concrct Laboratory Propam (aP Statement of Work for the Analysts of Volanle Oraanics February 1988

Calibnrion procedures and frequency for other critical measuremenu 13 summarized in Table 8middot 1 wuh the appropriate references

ArtlurD Little

I r I

Quaht) Auurance Proect Plan fot Pic1llo Farm July 9 1990

Revisbullon No 1 Paac 20 ot JJ

Tlble 5-1 (continued page 2 of 2)

~ Of Anltytlt htimlttd AMtrM Mllrlx P1rameter Accuracy

Seink Sutty (Subcask 3 6)

NA NA Wave Velouy 12 btt ttsoluttOn from

2msecto~clsample -ElcVItlon Survey (Subtask 3 8)

NA NA Dm~nce tl fi tl fooc 10010 NA NA Elevauon tOOl ft plusmn001 ft 10010

Maub ow bull Ground Waur sa SOli Gas A bull Ambient AirI

bull aPmiddotRAS bull Objectives for these meuun=ments will be taken from the US EPA Reaion I Ouidme for Vllidltbullna Ora11mc and lnoraanic Data

NA bull Noc AppUcabk

62JS1Aitcltltl

r

Qualuy Assurance Project Plan for PICtllo Farm July 9 1990

ReY tS IOfl No I Pace 21 of Jl

DuMJ the evaluation of the data rtsuluna from thts sue the variabtluy usoctalfd with the data in terms of prectslon accunCy and representameness wtll abo be UJeSsed and tncludcd 10 the diSCUSS IOn of tht datL

10 Swnpllng Procedurtl

f1 Sampling Locltlon tnd Frequency

The samplina locauons and frtquency of samplina for the surveys is Jiven in the Field Samplina Plan Sccuon 30

12 Sampling Proctdurta

Standard OpendnJ ProcedurtJ SOPs) for each of the samplinc openrions and r~ld te ninJ procedures that wtll be undertaken are attached to the Field Samplinc Plan A summary of each of these procedures alon J with a reference to the appropriate SOP is ampiven in Seclion ~ 0 of the Field SamplinJ Plan

eon ivn 1nd Holding nmn These items arc civen in the Field Samplin1 Plan Section 60

Pletd OrtconWmlneUOn ProcKurtl Field decontamination procedures are riven in the followinJ SOPs Field Decoruaminadon of Metal Samplina Equipment SOP No ADL-1009 and Field Dccoruaminarion of Tenon or Glass SamplinJ Equipment SOP No ADL-1008

d Oocumenlallon Procedurn Field documenwion procedu~s art summarized in the PMP Generic QA PjP Section 67 and the followina SOPs Standard OperatinJ Procedures SOP) for Schedulina ARCS Analylical Services SOP No ARC-20 Geotechnical Documentalion SOP No ADLmiddot4014 and Sample Cunody SOP No EPAmiddot IOOI

70 smp Cuetody

Sample custody procedures arc summarized in the PMP Generic QAPjP Section 70 and detai led in Sample Custody SOP No EPA-1001

I

J 6lllARaltlArthwD Little

r

Qu~hty Auunnce ProJeCt Plan for Plclllo Farm July 9 1990

Ruuion No I Po1e ll of ll

10 Clbrltlon Proetdurts

Generll proccdurts for calibrmlion are JIVtn 1n the PMO Generic QAP]P Secrion 10 Calibrttion procedures for the analysiS of volaule oraanics in the private well water an Jiven in Me1hod j242 Methoda for the Oetcnnjnarion olt Orllnki Compoonda jn Drinlqnr WIC[ EPA60014-88039 and ror he analysis of volaule oraanks In the monuonna well ampfOUnd water in US EPA Concrct Laboratory Propam (aP Statement of Work for the Analysts of Volanle Oraanics February 1988

Calibnrion procedures and frequency for other critical measuremenu 13 summarized in Table 8middot 1 wuh the appropriate references

ArtlurD Little

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Qualuy Assurance Project Plan for PICtllo Farm July 9 1990

ReY tS IOfl No I Pace 21 of Jl

DuMJ the evaluation of the data rtsuluna from thts sue the variabtluy usoctalfd with the data in terms of prectslon accunCy and representameness wtll abo be UJeSsed and tncludcd 10 the diSCUSS IOn of tht datL

10 Swnpllng Procedurtl

f1 Sampling Locltlon tnd Frequency

The samplina locauons and frtquency of samplina for the surveys is Jiven in the Field Samplina Plan Sccuon 30

12 Sampling Proctdurta

Standard OpendnJ ProcedurtJ SOPs) for each of the samplinc openrions and r~ld te ninJ procedures that wtll be undertaken are attached to the Field Samplinc Plan A summary of each of these procedures alon J with a reference to the appropriate SOP is ampiven in Seclion ~ 0 of the Field SamplinJ Plan

eon ivn 1nd Holding nmn These items arc civen in the Field Samplin1 Plan Section 60

Pletd OrtconWmlneUOn ProcKurtl Field decontamination procedures are riven in the followinJ SOPs Field Decoruaminadon of Metal Samplina Equipment SOP No ADL-1009 and Field Dccoruaminarion of Tenon or Glass SamplinJ Equipment SOP No ADL-1008

d Oocumenlallon Procedurn Field documenwion procedu~s art summarized in the PMP Generic QA PjP Section 67 and the followina SOPs Standard OperatinJ Procedures SOP) for Schedulina ARCS Analylical Services SOP No ARC-20 Geotechnical Documentalion SOP No ADLmiddot4014 and Sample Cunody SOP No EPAmiddot IOOI

70 smp Cuetody

Sample custody procedures arc summarized in the PMP Generic QAPjP Section 70 and detai led in Sample Custody SOP No EPA-1001

I

J 6lllARaltlArthwD Little

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Qu~hty Auunnce ProJeCt Plan for Plclllo Farm July 9 1990

Ruuion No I Po1e ll of ll

10 Clbrltlon Proetdurts

Generll proccdurts for calibrmlion are JIVtn 1n the PMO Generic QAP]P Secrion 10 Calibrttion procedures for the analysiS of volaule oraanics in the private well water an Jiven in Me1hod j242 Methoda for the Oetcnnjnarion olt Orllnki Compoonda jn Drinlqnr WIC[ EPA60014-88039 and ror he analysis of volaule oraanks In the monuonna well ampfOUnd water in US EPA Concrct Laboratory Propam (aP Statement of Work for the Analysts of Volanle Oraanics February 1988

Calibnrion procedures and frequency for other critical measuremenu 13 summarized in Table 8middot 1 wuh the appropriate references

ArtlurD Little

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Qu~hty Auunnce ProJeCt Plan for Plclllo Farm July 9 1990

Ruuion No I Po1e ll of ll

10 Clbrltlon Proetdurts

Generll proccdurts for calibrmlion are JIVtn 1n the PMO Generic QAP]P Secrion 10 Calibrttion procedures for the analysiS of volaule oraanics in the private well water an Jiven in Me1hod j242 Methoda for the Oetcnnjnarion olt Orllnki Compoonda jn Drinlqnr WIC[ EPA60014-88039 and ror he analysis of volaule oraanks In the monuonna well ampfOUnd water in US EPA Concrct Laboratory Propam (aP Statement of Work for the Analysts of Volanle Oraanics February 1988

Calibnrion procedures and frequency for other critical measuremenu 13 summarized in Table 8middot 1 wuh the appropriate references

ArtlurD Little

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Qutluy Auunnce ProJetl ptan for Plctllo Farm July 9 1990

RcvtslOII No I Paae 23 of 33

Tlbte Cllbr~tlon Proeedurts and lfrtquency

lleld lnvtlg~tlon

Subtbullk P1r1mettr Proetdurtflrtqutncy ftrence ll))lll pH Buffers at pH ltt 7 10 SOP No ADLmiddotSOll

lllrre times per day (beiJMina mid end)

Temperuure NBS ~nnometer SOP under Two umes per day dcvtlopmeru

bliJMint end)

Conducuvity OOINKCI (160 mmhos) SOP No ADLmiddotOI I 029NKCI (400) mm hos)

0 ION KCI (12800 mmhol) Two times per day

befiMinJ end)

Depth HtiJht Manufacturer NA Spectllcauon

]j MaifCtic Fie ld AMual Confidential SOP Field Intensity F~ctory Calibrat ion

36 Wave Velocity AMUal Confidential SOP F1t1octor Calibtation

38 LocatiorV Se mi AMual Confidential SOP Elevation Check with NGS

Cenifled Baselines

HNu PID lsobutylene (28 ppm) SO P No ADL- 0 12 Volatile OIJanics Thne times per day

(bcJiMina mid end)

Explosivity AM ual NA Factory Caliblltion

Radiation Semi AMual SOP under (GtiJer Counter) NB S Traceable Standard devdopment

Daily (btsimina end) Check Sourte Standard

37 Volaule Oqpmcs St3ndards Subcontractor SOP in Sotl Gas to be dttenniool

ba~d on subcontractor

Artlur D Little 6mlARCAJtl

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Qu1l11y AlS utlncr Protcl Plan for PltliiO Farm July 9 1990

Revmon No l PIJC 24 of 33

t O Anlllytteel Procedures

Labontory and neki analyncampl proccduru art summ1nzed 1n Table 9-1 wtth the tppropnate rcfertncrs

100 0111 Reduction V1lld1Uon and Reporting

101 Dati Reduction

References for da1a Nuction procedurts are 11ven in Table 9-1 Dara reduction procedures for subcomracted acuvmes maampnctomttcr survey seismic survey and elevation survey arc summanzcd below

Field rudinas taken durinJ the mtanctomctcr survey arc expressed in IOta maanctic field (lammas) thcrtfore the only d111 reduction necessary Is application of diurnal comcdons u needed Maaneuc field values arc plotted as profiles or COIIIOUtS durinamp the analo1 d111 proccnLnl Data accuracy is verified typically by a second qualified acophysicLst who checks a representative sample of the contour data DisitaJ data processing consists of emennJ the data dirtttly from the maJne10meter intO a persond computer The da~a 11 subsequenlly profiled andor contOUred usinJ proprietary or commerc1tly available software Final interpretations are recorded in a senes of magnetic profiles and contour maps Additional detail concerning the dua reduction validation and reponing of magnetic data can be found in confidenual subcontractor standard operalinJ procedures in the project files

Seismic data obtained in the field IS convened into a series of limedistance plots for each seismic refraction line Field recordinJs are spot chec ked in the oCfice to insure data accuracy Interpretation of the timedistance plots consists of spot checkinJ the accur1cy of the tr~vel time readings and the resultinJ timedistance plots Seismic velocity values ue measured and depths to seismic velocity interfaces can be calculated Oetatls of the data reduction validation and reporting for seismic data can be found in confidential subcontractor standard operatinJ procedures in the project files

The surveyinJ data will be reduced by utiiting an lntergraph and autoCad-based diampital mappinamp system to perfonn calculations These synems will perfonn ~asks such as meuurement correction for atmospheric conditions geomeaic corrections for slope offsets and eccenmcity Spedalited software is utilited for the reduction of Jlobal positioninJ systems data Data is validated and checked throoJh a system of built-in procedures Details of the surveying data reduction validation and reponinJ are auached to the Field SamplinJ Plan

Artlur D Little 62mARCOtl

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Qllhty Auunnce Procct Pl1n for Ptctllo Farm luly 9 1990

Revtsion No I Paae ll of ll

Tlble 1-1 Laboratory and ltld Analytical Proetduru

IOld lnveatlgatlon

Subtbullk P1rameter Mltrtx Reference

Prinbull Well Volaule ow MelhOd $242 Methodt rorlhc 31 Ora ames Determ ination of Ot)anic

Compounds in Dnnltin1 Waitt EPA6004middotIIW39

Monltorin1 WeU Votmle OW US EPA CLP SOW 33 Or11amcs RAS Method for Volatiles

in Water

3233311 pH OW SOP No ADLmiddot5013

32333 11 Tem~rmturt OW SOP under devtlopmenc

3233311 Conducuvuy ow SOP No ADLmiddot5011

32)3311 OepWHtllhl ow SOP No ADL4012

3233311 WeU Volume ow SOP No AOL-4014

JlJ) J 1 Plm pin1 Rate ow SoU Gu Survey Volatile so Subcontractor SOP

37 Ol]anics

MqnttOmmr Maampnellc Subcontractor SOP Sulley 5 Field

Seismic Survey Wave VeOCII) Subcontractor SOP 36

Elcvltion Location Subcontractor SOP Sutvey 31 Elev3UOn

Heallh ard Volatile SOP No ADL-S02 sarety Suppon Oraanics by

HNu PIO

ExpiOSI YII) SOP unde r deveOpmtnl

Radiauon SOP under development

)

Artlur I) Little

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Qllhty Auunnce Procct Pl1n for Ptctllo Farm luly 9 1990

Revtsion No I Paae ll of ll

Tlble 1-1 Laboratory and ltld Analytical Proetduru

IOld lnveatlgatlon

Subtbullk P1rameter Mltrtx Reference

Prinbull Well Volaule ow MelhOd $242 Methodt rorlhc 31 Ora ames Determ ination of Ot)anic

Compounds in Dnnltin1 Waitt EPA6004middotIIW39

Monltorin1 WeU Votmle OW US EPA CLP SOW 33 Or11amcs RAS Method for Volatiles

in Water

3233311 pH OW SOP No ADLmiddot5013

32333 11 Tem~rmturt OW SOP under devtlopmenc

3233311 Conducuvuy ow SOP No ADLmiddot5011

32)3311 OepWHtllhl ow SOP No ADL4012

3233311 WeU Volume ow SOP No AOL-4014

JlJ) J 1 Plm pin1 Rate ow SoU Gu Survey Volatile so Subcontractor SOP

37 Ol]anics

MqnttOmmr Maampnellc Subcontractor SOP Sulley 5 Field

Seismic Survey Wave VeOCII) Subcontractor SOP 36

Elcvltion Location Subcontractor SOP Sutvey 31 Elev3UOn

Heallh ard Volatile SOP No ADL-S02 sarety Suppon Oraanics by

HNu PIO

ExpiOSI YII) SOP unde r deveOpmtnl

Radiauon SOP under development

)

Artlur I) Little

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Quahry Ai unnce Projt CI Plln few PCillo Flltm July 9 1990

Re v1s1on No 1 Pap 26 o( JJ

102 Dati Velld8tlon

An over1ll Otscnpuon of datJ Jhdauon 11 JLHn 10 the P~tP Gtncnc QAPJP Seclion 1012 The requ1rtd JhdIUon schcmei for uch of the levels of analym a Jiven below

LoYol v Data resuhinJ from the rnalysts of Oiaule oraanus 10 pnVIIC well samples by Method 24 2 will be validated YSIOJ Rulon I Laboratory pall Yalidauon Funsrional GujdclinSJ for Evalumn r OrtaDLCJ AnalyKs modified November I 1988 The Lead Chemist 11 responsi ble for this vahdanon

LoYol IV Data resuhinJ from the analysLs of volaue orJanks 1n rnonnorinJ well samples by the US EPA CLP SOW Me thod will be validated us1nl Rccjon I LabofiOO Qaa Ya1jdadon fynctjona Gyjdc hnts fo r Evauatjnbull Or11njq Analyst modiftcd November 1 1988 The Lead Chcmisl is responsible for this validation

LoYol u The meuuremen for pH lcmperature conductivity and water depth will be validaled by comparinamp the results of tesrinJ Quality Conrrol samp les with the Daa Quality Objectives ampiven in Sccuon 33 Table 3middot 1 of this QAPjP This PMO QA Oftlccr or his deSiJnatc is responstble for this validation durinJ review of field documentation

LoYoll The meuurements for volatile oraanics usinJ an HNu PID explosivity meter and fldiarion meter will be validated by companna the results of ttstinJ Quality Control samples (calibration aas and duplicate measurements for the HNu PID) wi th the Data Quality Objectives 1iven in Section 33 Table 3middot 1 of the QAPj P The PMO QA Officer or his desiampnate is responsible for this validation durinJ the fie ld site audit and nview of field documentation

103 ow end Reporting of 0 111 end Rtlponalble Steff for 0111

The flow of raw data and samples from the field samplina crew throuJh delivery o( Vallda~ed data and storage of raw data LS shown in Fiaun 10middot1

Field documentation and measurement data art provided to the PMO QA Officer or his dcsianate by the Field Supervi sor The PMO QA Officer reviews and validates the field documentation and measurement data Field samples for analysis are provided to the CLP alonamp with appropriate documentation The labontory provides the Lead Chemist wuh data packages In rum the Lead Chemist is nsponsible for distributing l ~ boratory data packages to ProJrlm Data Reviewen After validation the Lead Chemtst documents the results of data validation and indicates any data li mitations The Lead Chemist provides the Project Manaaer and appropriate EPA staff with the Data Summary and Data Validation Repons The PMO QA Officer provides a summary of the reviewmiddot and

6lmARC~llArtJur D Little

-n= = U

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sl I FltiCIMeuur~ o --

~ OataPecQgn DalaPildiIQtt (l IV V) shyn =

T Ut=~

R11uhol Review

Artlur D Little

I

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Quali ty r 1SurJnce Project Plan for Ptctllo Farm July 9 1990

RevLSIOII No 1 Paac 21 of 33

validation of rleld docu~ntanon and meuurcmem dlta 10 tle PrO)tCI Manaaer Field staff or the PMO QA Officer provide field documenutton aiKi measurement dall to the Project Manaaer

11 0 Internal Ou1Uty Control Cheeks

Internal Qua lity Control amptes are aenerally descnbed in the PMP Genenc QAPjP Section 11 0 The Internal Qualuy Control Samples for the analysis of volatile OIJinks in the pnvate well samples w-e dcscnbed in Method j242 Mstbodbull fgr the Oetnn tnatjqn of Ornntc Comoounds jn Dnnkjnr W11er EPA60014-811039 for the analysiS of volanlc oraamcs in the monhorina well samples US EPA Conttact LaboraOry ProJTam (CLP) Stattrfl(nt of Work for the Analysis of Volatile Oraamcs tucu version

11 1 llenk Sam~bull

The rtsults from the analysis of bllnk nmplcs are used to assess possible levels of contamination introduced into the iamples duri namp man ufacture handlina in the raeld durinamp shipment or in the llbontory

11 11 lonte llenkbull The f~uency of bottle blanks is one per samplinamp epLsode Boule blanks will be analyzed as pan of the Pri vate Well (Subtask 32) and MonitorinJ Welt (Subtask 33) SWIcys volatile oraan ics analysis

A bottle blank is prepartd by the su pplier (i n this case the Arthur D Little laboratory) of the sample containers to the field uaff by fill inamp a contai ner with deionized distilled water with oraanics removed by carbon adsorption This boule blank is sent directly to the CLP labonnory from the Arthur 0 Little laboratory Therefore this blank is never exposed to field conditions

The results obtained from the an11l ysis of boule blanks are used to assess potential sources of contamination durinamp manufacture prcpar11tion and storaae of the bonJes Potential sources of contamination include manufacturinamp and preparation opendons ambient air and contact with analytical alasswa rthardware durinamp laboratory sample preparation mnd an~lysis

111 2 Trip lllnkl The frequency of aip bl1nks is one pcr shipment Trip bl1nks will be analyzed u pan of the Private Well (Subta sk 3 2) and Monitorina Well (Subtask 33) Surveys volatile oraanics analysis

A aip blank is a sample boule contamma deionized disuled water with oraanics removed by carbon adsorption preplred 1n the labo r~tory and preservatives (if used with field samples) The rrip blanks accompanies unused sample bottles to the field and is then returned to the laboratory Trip blanks are handled transponed

Artlur D Little

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Qualuy Auunnce ProJect Plan for Ptctllo Farm

July 9 1990 Revision No I Pore l9 of ll

and analyzed in the same manner as the field samples collected ucepc thac tnp bilmk sample bottles are 21 opened m rhe field

The results obtained rrom analym of tnp blanks arc used ro aucu pocenriaJ JOWCU or concamination in the labornory and dunnamp nnspon Potenaal sources ol concamination include laborltory reaampencs sample contau1er and laboramry alassware cleanlna procedures cross contamtnauon dunnamp sh1pmcnr arnb1cn1 lUI or con~a~t with analyrical slauwltthardware dunnJ laboratory sample preparation and anaJysil

11 13 Equipment ll1nks The frequenc y of aqueous equipment blanks is one per day of samplina and the frequency of aascous equipmcnc blanks n at least one system blamplk per day of sampUna Equipment blanks will be analyzed as pan of the Private We ll (Subtask 32) MonilorinJ Well (Subutsk 33) and Sot Gas (Subtask 37) Surveys

An equipment blank is prepartd by eltposina samplina materials (bottles collection devius etc) to the samphnJ envtronment without allowinamp them to actively mix with the matrix of interest

For 1he aqueous samples collected from the Private and Monitorina Wells deionized distilled water with oraanics removed by carbon adsorption (reaaent water) is sent to the field and used tO produce an equipment blank The rcatent water is exposed to field conditions paned throuah decontaminated sample equipment and collected in an empty sample conta iner for analysis In the case of private wells samples will typically be collected directly into the sample container Thcrdore the equipment blank would be e~tposed only tO field conditions not samplina equipment other than the container

For the soil au maaiK system blanks are run to chetk the decontaminated samplina appantus (probe adaptor IOcc syrinae) for contamination by dtawina ambient air from above around throuah the syste m and comparinJ the analysis to a concumn1ly sampled ambient air analysis

Equipment blanks arc handled (i n the case of the aqueous samples from the wells preserved) tnnsponed and analyzed bulln the same manner as the samples collected that day

Results obtained from analysis of equipment blanks are used to assess the same potential contamination as trip blanks and additional potential contamination from samplinamp equipment used to collect and transfer samples (such as buckets tubina and corers) and site ambient conditions

1114 Method lllnks The frequency of lflalyzina method blanks in the laboratory for the analysis of

_ volatile oraanics from Private and Monttorinamp Wells is specified in the referenced methods Method blanks for the sot aas survey are analyzed at least once a day

-n = = Cll

Artlur D Little 6UUARCltILI

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Quahty Assurance Project Plan for Plctllo Farm Ju ly 9 1990

Rc vts lon No I Pare 30 or 33

The dKontaminatcd 2 cc subsamphnJ synn1cs m checked for contamination pnor 10 wnplinJ uch day by inJCCIInJ nnroampen earner JU 1nto the aas chromato~faph

11 2 Oupllelle S1mplt1

Duplicate tamples are defined u scpante samples Ween from the same soutte The analyncal sul11 obtained from these samples are used to eSiablish control and u seu llld document the p~cJsJon of analysis andor samplinJ so that COITCctive aclions may be 1aken as necessary and precision may be documented Sevtnl types of duplicaiC samples are dcscnbed below

~2~q~y0o1~C field duplicates for private and monitorinJ well samplina is one per 20 samples collected per sample maUb In th is case the aqueous samples from the private and rnonnorinJ wells are considered two differtnt maaicn The frequency of Jaseoos fi eld duplicates for the Soil Gas Surve y is one per 20 samples collec1ed and analyzed

Soil 111 duplcares are collecred by urracrina separate aliquou from rhe probe The initial sample is collecred in a syri nae and analyzed Conditions are allowed 10 equilibrare for 11 Jeasr 5 minutes and then a duplicm1e sample aliquoc is coUecled in the syrinae and analyzed

Field duplica~es are handled transponed and anal yzed in he same manner as are the orher samples collec~ed 1ha1 day

Duplicate restinJ will also be undenaken for pH conductivily ~emperature ndiarion explosivily field intensiry and elevariondistance at a frequency of at leut I in 20 measuremems

The resuhs obtained from analyzina field duplicares are used to assess and documenl the reproducibilily of overall samplinJ handlinJ and analyrical procedures Duplicate samples raken in the field represent rhe non-homoaeneity of field conditions Therefore it is expected rhat precision estimates obcained from the analysis of field duplicate samples will have substantial associated variability more so than replicate samples prepared in the laboratory

11 22 Ubcntory AepllcatH Replicate samples are defined as rwo sa mple aliquots taken from the same sample comainer and analyzed independe ntly The frequency of laboratory replicates for volatiles analysis of aqueous samples is speci fied in the method references All soil au samples In 1he syri nge are analyzed a1 least a minimum of rwice to insure reproducabiliry

)

623UARC~IArtlur D Little

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Quahty A~surampnce Pro~c1 Plan fat Pactllo farm July 9 1990

Rcvasaon No 1 Pase ll o( ll

11 3 Spiked Sampltl

The frequency of analyrlnJ mam spbullkesmamx spLkt duplicates of aqueous pmplcs for volaules samples 11 one per case of field samples or per 20 samples (whichever is tIIR f~quenl) A matru sptke 11 ln ahquoc of a fieki sample spiked with lhc analytes of 1nterts1 1n the laboratOf) SurTOJitCI lR added in the labontOf) 10 all samples taken for 1he analysbulls of volatile oraanics by JIS ctuOmltopphytman spectrometry Surroaates are compounds not typkally found u contaminants in the environment They are Similar in StrUCt1~ 10 compounds beinJ metsured These compounds are frequenlly isOiopically labelled such u deutented oraanics

The resuhs obtained from the analysis of these spiked samples ue used tO control assess and documtnl the Kcurncy of an analyucal me1hod

11 bull f Standards

SlllldardJ will be used at the frequency specified in Seclion 8 of lhis QAPjP Standampnb for the volati le oraanics analysis or aqueous and soil au samples are pven in the specified rtfertnces and SOP Standards for the other panmeltn include

pH-buffen traceable to NIST (formtrly NBS)

ConducrivitymiddotKCI solutions

TemperaturtmiddotNIST (formerly NBS) cenified thennometer

HNu PID-isobutylene standard

Radiation-Source Check Standard

Maanetometer

Seismic

Elevation bullbull NOS Cenified Baselines

120 Perlormence 1nd Systems Audits

Definirions and procedurts for perfonnance and systems audits are Jiven in the PMP QAPP Section 712 and the Generic QAPjP Section 120

Activities for this project will be audited as part or the quanerly schedule established in the ProJlm Manaaement Plan For this project that quanerly audit will specifically include a visit to the site durinamp field activities to audit practices and I rtview or field documenlltion

Artlur D Little

-a-n = = ~

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Qullny Assu rJ nce ProjeCt P1an for PiCIIIo Fum July 9 1990

Revbullsbullon No 1 p ll of))

Performance and systems audm of the llbomones used for the volaciles orJamcs analysis are conducced u pm of the US EPA ConDact Laboratory Proampnm (CLP)

130 Preventlttve Malntenbullnct

Equipmcnl for the onrall proanm u mamta1ned as abullven in lhe Pro11am Manaaement Plan Secuon 50 Propcny ManaJemcnt

In lhe field spare pan lnvcn10ncs m maincained for the pH meter conductivity meter HNu PID field Ja5 chromat01faph and expendable hems includinJ

pH Meie r electrodes banenes

Conductivity Mcaer baucries

HNu PID batteries

Explosivity meter bmcncs

Field Gas Chromatoaraph sp1 ~ GC column syrinJeS swaJclock fhtinas

140 lpectftc ftou llne Procedurebull UMd to AtHtt 01111 Precltlon Accurecy 8ftd Comptetentu

Explanalions and fonnulas for calculatina the necessary statistics for asseuinJ data precision accuracy and completeness arc aiven in the PMP Generic QAPjP Section 140 and the QAPP Section 79 A summary of the Qualhy Control samples analyzed to produce rtsuhs for suuiSiical catcualions is aiven in Table 14middot l

150 Corrtcttve Actions

Procedurts and types of corrective actions art 1iven in the PMP QAPP Section 7 )0

140 OUIIlty Auurence Reports to Mlnagement

Procedures and a descri ption of the comem for QA repons to manaJement are liven in the PMP QAPP Secrion 743

ArtlurD Little

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QuaJuy A surJnce Project Plan for Ptc1llo Farm July 9 1990

Rev1110n No 1

bullmiddot ll olll

TM6e 1 1 aullty Control Slmpltt Analynd to Product Ru111 for ltlltlltlcal CaJeuletlons

t~Uflct Caeulonbull Quatlty Control Prtelt~n rtey

Samp+tt Averlgtlfirenc ecovwr Spectfleatlon

Volailc field Ouptlcue Oltprucs

in Aqueous MSIMSD X Sampla

SumJJlte Sptke X

Vofable Sysaem (probe) Orpnics Collocalts X

In SoU Ou $ampa SIIOOatds X

pH Con6uctivily Field Tbull penNre Duplicate X HNu PIO

Volllilc Standard X ~ Rldildon

623SlAAOILIAltlurD LlttJe

1. barcode 575210
2. barcodetext SDMS Doc ID 575210

I r I

sl I FltiCIMeuur~ o --

~ OataPecQgn DalaPildiIQtt (l IV V) shyn =

T Ut=~

R11uhol Review

Artlur D Little

I

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Quali ty r 1SurJnce Project Plan for Ptctllo Farm July 9 1990

RevLSIOII No 1 Paac 21 of 33

validation of rleld docu~ntanon and meuurcmem dlta 10 tle PrO)tCI Manaaer Field staff or the PMO QA Officer provide field documenutton aiKi measurement dall to the Project Manaaer

11 0 Internal Ou1Uty Control Cheeks

Internal Qua lity Control amptes are aenerally descnbed in the PMP Genenc QAPjP Section 11 0 The Internal Qualuy Control Samples for the analysis of volatile OIJinks in the pnvate well samples w-e dcscnbed in Method j242 Mstbodbull fgr the Oetnn tnatjqn of Ornntc Comoounds jn Dnnkjnr W11er EPA60014-811039 for the analysiS of volanlc oraamcs in the monhorina well samples US EPA Conttact LaboraOry ProJTam (CLP) Stattrfl(nt of Work for the Analysis of Volatile Oraamcs tucu version

11 1 llenk Sam~bull

The rtsults from the analysis of bllnk nmplcs are used to assess possible levels of contamination introduced into the iamples duri namp man ufacture handlina in the raeld durinamp shipment or in the llbontory

11 11 lonte llenkbull The f~uency of bottle blanks is one per samplinamp epLsode Boule blanks will be analyzed as pan of the Pri vate Well (Subtask 32) and MonitorinJ Welt (Subtask 33) SWIcys volatile oraan ics analysis

A bottle blank is prepartd by the su pplier (i n this case the Arthur D Little laboratory) of the sample containers to the field uaff by fill inamp a contai ner with deionized distilled water with oraanics removed by carbon adsorption This boule blank is sent directly to the CLP labonnory from the Arthur 0 Little laboratory Therefore this blank is never exposed to field conditions

The results obtained from the an11l ysis of boule blanks are used to assess potential sources of contamination durinamp manufacture prcpar11tion and storaae of the bonJes Potential sources of contamination include manufacturinamp and preparation opendons ambient air and contact with analytical alasswa rthardware durinamp laboratory sample preparation mnd an~lysis

111 2 Trip lllnkl The frequency of aip bl1nks is one pcr shipment Trip bl1nks will be analyzed u pan of the Private Well (Subta sk 3 2) and Monitorina Well (Subtask 33) Surveys volatile oraanics analysis

A aip blank is a sample boule contamma deionized disuled water with oraanics removed by carbon adsorption preplred 1n the labo r~tory and preservatives (if used with field samples) The rrip blanks accompanies unused sample bottles to the field and is then returned to the laboratory Trip blanks are handled transponed

Artlur D Little

I r I

Qualuy Auunnce ProJect Plan for Ptctllo Farm

July 9 1990 Revision No I Pore l9 of ll

and analyzed in the same manner as the field samples collected ucepc thac tnp bilmk sample bottles are 21 opened m rhe field

The results obtained rrom analym of tnp blanks arc used ro aucu pocenriaJ JOWCU or concamination in the labornory and dunnamp nnspon Potenaal sources ol concamination include laborltory reaampencs sample contau1er and laboramry alassware cleanlna procedures cross contamtnauon dunnamp sh1pmcnr arnb1cn1 lUI or con~a~t with analyrical slauwltthardware dunnJ laboratory sample preparation and anaJysil

11 13 Equipment ll1nks The frequenc y of aqueous equipment blanks is one per day of samplina and the frequency of aascous equipmcnc blanks n at least one system blamplk per day of sampUna Equipment blanks will be analyzed as pan of the Private We ll (Subtask 32) MonilorinJ Well (Subutsk 33) and Sot Gas (Subtask 37) Surveys

An equipment blank is prepartd by eltposina samplina materials (bottles collection devius etc) to the samphnJ envtronment without allowinamp them to actively mix with the matrix of interest

For 1he aqueous samples collected from the Private and Monitorina Wells deionized distilled water with oraanics removed by carbon adsorption (reaaent water) is sent to the field and used tO produce an equipment blank The rcatent water is exposed to field conditions paned throuah decontaminated sample equipment and collected in an empty sample conta iner for analysis In the case of private wells samples will typically be collected directly into the sample container Thcrdore the equipment blank would be e~tposed only tO field conditions not samplina equipment other than the container

For the soil au maaiK system blanks are run to chetk the decontaminated samplina appantus (probe adaptor IOcc syrinae) for contamination by dtawina ambient air from above around throuah the syste m and comparinJ the analysis to a concumn1ly sampled ambient air analysis

Equipment blanks arc handled (i n the case of the aqueous samples from the wells preserved) tnnsponed and analyzed bulln the same manner as the samples collected that day

Results obtained from analysis of equipment blanks are used to assess the same potential contamination as trip blanks and additional potential contamination from samplinamp equipment used to collect and transfer samples (such as buckets tubina and corers) and site ambient conditions

1114 Method lllnks The frequency of lflalyzina method blanks in the laboratory for the analysis of

_ volatile oraanics from Private and Monttorinamp Wells is specified in the referenced methods Method blanks for the sot aas survey are analyzed at least once a day

-n = = Cll

Artlur D Little 6UUARCltILI

- r I

Quahty Assurance Project Plan for Plctllo Farm Ju ly 9 1990

Rc vts lon No I Pare 30 or 33

The dKontaminatcd 2 cc subsamphnJ synn1cs m checked for contamination pnor 10 wnplinJ uch day by inJCCIInJ nnroampen earner JU 1nto the aas chromato~faph

11 2 Oupllelle S1mplt1

Duplicate tamples are defined u scpante samples Ween from the same soutte The analyncal sul11 obtained from these samples are used to eSiablish control and u seu llld document the p~cJsJon of analysis andor samplinJ so that COITCctive aclions may be 1aken as necessary and precision may be documented Sevtnl types of duplicaiC samples are dcscnbed below

~2~q~y0o1~C field duplicates for private and monitorinJ well samplina is one per 20 samples collected per sample maUb In th is case the aqueous samples from the private and rnonnorinJ wells are considered two differtnt maaicn The frequency of Jaseoos fi eld duplicates for the Soil Gas Surve y is one per 20 samples collec1ed and analyzed

Soil 111 duplcares are collecred by urracrina separate aliquou from rhe probe The initial sample is collecred in a syri nae and analyzed Conditions are allowed 10 equilibrare for 11 Jeasr 5 minutes and then a duplicm1e sample aliquoc is coUecled in the syrinae and analyzed

Field duplica~es are handled transponed and anal yzed in he same manner as are the orher samples collec~ed 1ha1 day

Duplicate restinJ will also be undenaken for pH conductivily ~emperature ndiarion explosivily field intensiry and elevariondistance at a frequency of at leut I in 20 measuremems

The resuhs obtained from analyzina field duplicares are used to assess and documenl the reproducibilily of overall samplinJ handlinJ and analyrical procedures Duplicate samples raken in the field represent rhe non-homoaeneity of field conditions Therefore it is expected rhat precision estimates obcained from the analysis of field duplicate samples will have substantial associated variability more so than replicate samples prepared in the laboratory

11 22 Ubcntory AepllcatH Replicate samples are defined as rwo sa mple aliquots taken from the same sample comainer and analyzed independe ntly The frequency of laboratory replicates for volatiles analysis of aqueous samples is speci fied in the method references All soil au samples In 1he syri nge are analyzed a1 least a minimum of rwice to insure reproducabiliry

)

623UARC~IArtlur D Little

- r --

Quahty A~surampnce Pro~c1 Plan fat Pactllo farm July 9 1990

Rcvasaon No 1 Pase ll o( ll

11 3 Spiked Sampltl

The frequency of analyrlnJ mam spbullkesmamx spLkt duplicates of aqueous pmplcs for volaules samples 11 one per case of field samples or per 20 samples (whichever is tIIR f~quenl) A matru sptke 11 ln ahquoc of a fieki sample spiked with lhc analytes of 1nterts1 1n the laboratOf) SurTOJitCI lR added in the labontOf) 10 all samples taken for 1he analysbulls of volatile oraanics by JIS ctuOmltopphytman spectrometry Surroaates are compounds not typkally found u contaminants in the environment They are Similar in StrUCt1~ 10 compounds beinJ metsured These compounds are frequenlly isOiopically labelled such u deutented oraanics

The resuhs obtained from the analysis of these spiked samples ue used tO control assess and documtnl the Kcurncy of an analyucal me1hod

11 bull f Standards

SlllldardJ will be used at the frequency specified in Seclion 8 of lhis QAPjP Standampnb for the volati le oraanics analysis or aqueous and soil au samples are pven in the specified rtfertnces and SOP Standards for the other panmeltn include

pH-buffen traceable to NIST (formtrly NBS)

ConducrivitymiddotKCI solutions

TemperaturtmiddotNIST (formerly NBS) cenified thennometer

HNu PID-isobutylene standard

Radiation-Source Check Standard

Maanetometer

Seismic

Elevation bullbull NOS Cenified Baselines

120 Perlormence 1nd Systems Audits

Definirions and procedurts for perfonnance and systems audits are Jiven in the PMP QAPP Section 712 and the Generic QAPjP Section 120

Activities for this project will be audited as part or the quanerly schedule established in the ProJlm Manaaement Plan For this project that quanerly audit will specifically include a visit to the site durinamp field activities to audit practices and I rtview or field documenlltion

Artlur D Little

-a-n = = ~

r

Qullny Assu rJ nce ProjeCt P1an for PiCIIIo Fum July 9 1990

Revbullsbullon No 1 p ll of))

Performance and systems audm of the llbomones used for the volaciles orJamcs analysis are conducced u pm of the US EPA ConDact Laboratory Proampnm (CLP)

130 Preventlttve Malntenbullnct

Equipmcnl for the onrall proanm u mamta1ned as abullven in lhe Pro11am Manaaement Plan Secuon 50 Propcny ManaJemcnt

In lhe field spare pan lnvcn10ncs m maincained for the pH meter conductivity meter HNu PID field Ja5 chromat01faph and expendable hems includinJ

pH Meie r electrodes banenes

Conductivity Mcaer baucries

HNu PID batteries

Explosivity meter bmcncs

Field Gas Chromatoaraph sp1 ~ GC column syrinJeS swaJclock fhtinas

140 lpectftc ftou llne Procedurebull UMd to AtHtt 01111 Precltlon Accurecy 8ftd Comptetentu

Explanalions and fonnulas for calculatina the necessary statistics for asseuinJ data precision accuracy and completeness arc aiven in the PMP Generic QAPjP Section 140 and the QAPP Section 79 A summary of the Qualhy Control samples analyzed to produce rtsuhs for suuiSiical catcualions is aiven in Table 14middot l

150 Corrtcttve Actions

Procedurts and types of corrective actions art 1iven in the PMP QAPP Section 7 )0

140 OUIIlty Auurence Reports to Mlnagement

Procedures and a descri ption of the comem for QA repons to manaJement are liven in the PMP QAPP Secrion 743

ArtlurD Little

- r -

QuaJuy A surJnce Project Plan for Ptc1llo Farm July 9 1990

Rev1110n No 1

bullmiddot ll olll

TM6e 1 1 aullty Control Slmpltt Analynd to Product Ru111 for ltlltlltlcal CaJeuletlons

t~Uflct Caeulonbull Quatlty Control Prtelt~n rtey

Samp+tt Averlgtlfirenc ecovwr Spectfleatlon

Volailc field Ouptlcue Oltprucs

in Aqueous MSIMSD X Sampla

SumJJlte Sptke X

Vofable Sysaem (probe) Orpnics Collocalts X

In SoU Ou $ampa SIIOOatds X

pH Con6uctivily Field Tbull penNre Duplicate X HNu PIO

Volllilc Standard X ~ Rldildon

623SlAAOILIAltlurD LlttJe

1. barcode 575210
2. barcodetext SDMS Doc ID 575210

I

-- -

Quali ty r 1SurJnce Project Plan for Ptctllo Farm July 9 1990

RevLSIOII No 1 Paac 21 of 33

validation of rleld docu~ntanon and meuurcmem dlta 10 tle PrO)tCI Manaaer Field staff or the PMO QA Officer provide field documenutton aiKi measurement dall to the Project Manaaer

11 0 Internal Ou1Uty Control Cheeks

Internal Qua lity Control amptes are aenerally descnbed in the PMP Genenc QAPjP Section 11 0 The Internal Qualuy Control Samples for the analysis of volatile OIJinks in the pnvate well samples w-e dcscnbed in Method j242 Mstbodbull fgr the Oetnn tnatjqn of Ornntc Comoounds jn Dnnkjnr W11er EPA60014-811039 for the analysiS of volanlc oraamcs in the monhorina well samples US EPA Conttact LaboraOry ProJTam (CLP) Stattrfl(nt of Work for the Analysis of Volatile Oraamcs tucu version

11 1 llenk Sam~bull

The rtsults from the analysis of bllnk nmplcs are used to assess possible levels of contamination introduced into the iamples duri namp man ufacture handlina in the raeld durinamp shipment or in the llbontory

11 11 lonte llenkbull The f~uency of bottle blanks is one per samplinamp epLsode Boule blanks will be analyzed as pan of the Pri vate Well (Subtask 32) and MonitorinJ Welt (Subtask 33) SWIcys volatile oraan ics analysis

A bottle blank is prepartd by the su pplier (i n this case the Arthur D Little laboratory) of the sample containers to the field uaff by fill inamp a contai ner with deionized distilled water with oraanics removed by carbon adsorption This boule blank is sent directly to the CLP labonnory from the Arthur 0 Little laboratory Therefore this blank is never exposed to field conditions

The results obtained from the an11l ysis of boule blanks are used to assess potential sources of contamination durinamp manufacture prcpar11tion and storaae of the bonJes Potential sources of contamination include manufacturinamp and preparation opendons ambient air and contact with analytical alasswa rthardware durinamp laboratory sample preparation mnd an~lysis

111 2 Trip lllnkl The frequency of aip bl1nks is one pcr shipment Trip bl1nks will be analyzed u pan of the Private Well (Subta sk 3 2) and Monitorina Well (Subtask 33) Surveys volatile oraanics analysis

A aip blank is a sample boule contamma deionized disuled water with oraanics removed by carbon adsorption preplred 1n the labo r~tory and preservatives (if used with field samples) The rrip blanks accompanies unused sample bottles to the field and is then returned to the laboratory Trip blanks are handled transponed

Artlur D Little

I r I

Qualuy Auunnce ProJect Plan for Ptctllo Farm

July 9 1990 Revision No I Pore l9 of ll

and analyzed in the same manner as the field samples collected ucepc thac tnp bilmk sample bottles are 21 opened m rhe field

The results obtained rrom analym of tnp blanks arc used ro aucu pocenriaJ JOWCU or concamination in the labornory and dunnamp nnspon Potenaal sources ol concamination include laborltory reaampencs sample contau1er and laboramry alassware cleanlna procedures cross contamtnauon dunnamp sh1pmcnr arnb1cn1 lUI or con~a~t with analyrical slauwltthardware dunnJ laboratory sample preparation and anaJysil

11 13 Equipment ll1nks The frequenc y of aqueous equipment blanks is one per day of samplina and the frequency of aascous equipmcnc blanks n at least one system blamplk per day of sampUna Equipment blanks will be analyzed as pan of the Private We ll (Subtask 32) MonilorinJ Well (Subutsk 33) and Sot Gas (Subtask 37) Surveys

An equipment blank is prepartd by eltposina samplina materials (bottles collection devius etc) to the samphnJ envtronment without allowinamp them to actively mix with the matrix of interest

For 1he aqueous samples collected from the Private and Monitorina Wells deionized distilled water with oraanics removed by carbon adsorption (reaaent water) is sent to the field and used tO produce an equipment blank The rcatent water is exposed to field conditions paned throuah decontaminated sample equipment and collected in an empty sample conta iner for analysis In the case of private wells samples will typically be collected directly into the sample container Thcrdore the equipment blank would be e~tposed only tO field conditions not samplina equipment other than the container

For the soil au maaiK system blanks are run to chetk the decontaminated samplina appantus (probe adaptor IOcc syrinae) for contamination by dtawina ambient air from above around throuah the syste m and comparinJ the analysis to a concumn1ly sampled ambient air analysis

Equipment blanks arc handled (i n the case of the aqueous samples from the wells preserved) tnnsponed and analyzed bulln the same manner as the samples collected that day

Results obtained from analysis of equipment blanks are used to assess the same potential contamination as trip blanks and additional potential contamination from samplinamp equipment used to collect and transfer samples (such as buckets tubina and corers) and site ambient conditions

1114 Method lllnks The frequency of lflalyzina method blanks in the laboratory for the analysis of

_ volatile oraanics from Private and Monttorinamp Wells is specified in the referenced methods Method blanks for the sot aas survey are analyzed at least once a day

-n = = Cll

Artlur D Little 6UUARCltILI

- r I

Quahty Assurance Project Plan for Plctllo Farm Ju ly 9 1990

Rc vts lon No I Pare 30 or 33

The dKontaminatcd 2 cc subsamphnJ synn1cs m checked for contamination pnor 10 wnplinJ uch day by inJCCIInJ nnroampen earner JU 1nto the aas chromato~faph

11 2 Oupllelle S1mplt1

Duplicate tamples are defined u scpante samples Ween from the same soutte The analyncal sul11 obtained from these samples are used to eSiablish control and u seu llld document the p~cJsJon of analysis andor samplinJ so that COITCctive aclions may be 1aken as necessary and precision may be documented Sevtnl types of duplicaiC samples are dcscnbed below

~2~q~y0o1~C field duplicates for private and monitorinJ well samplina is one per 20 samples collected per sample maUb In th is case the aqueous samples from the private and rnonnorinJ wells are considered two differtnt maaicn The frequency of Jaseoos fi eld duplicates for the Soil Gas Surve y is one per 20 samples collec1ed and analyzed

Soil 111 duplcares are collecred by urracrina separate aliquou from rhe probe The initial sample is collecred in a syri nae and analyzed Conditions are allowed 10 equilibrare for 11 Jeasr 5 minutes and then a duplicm1e sample aliquoc is coUecled in the syrinae and analyzed

Field duplica~es are handled transponed and anal yzed in he same manner as are the orher samples collec~ed 1ha1 day

Duplicate restinJ will also be undenaken for pH conductivily ~emperature ndiarion explosivily field intensiry and elevariondistance at a frequency of at leut I in 20 measuremems

The resuhs obtained from analyzina field duplicares are used to assess and documenl the reproducibilily of overall samplinJ handlinJ and analyrical procedures Duplicate samples raken in the field represent rhe non-homoaeneity of field conditions Therefore it is expected rhat precision estimates obcained from the analysis of field duplicate samples will have substantial associated variability more so than replicate samples prepared in the laboratory

11 22 Ubcntory AepllcatH Replicate samples are defined as rwo sa mple aliquots taken from the same sample comainer and analyzed independe ntly The frequency of laboratory replicates for volatiles analysis of aqueous samples is speci fied in the method references All soil au samples In 1he syri nge are analyzed a1 least a minimum of rwice to insure reproducabiliry

)

623UARC~IArtlur D Little

- r --

Quahty A~surampnce Pro~c1 Plan fat Pactllo farm July 9 1990

Rcvasaon No 1 Pase ll o( ll

11 3 Spiked Sampltl

The frequency of analyrlnJ mam spbullkesmamx spLkt duplicates of aqueous pmplcs for volaules samples 11 one per case of field samples or per 20 samples (whichever is tIIR f~quenl) A matru sptke 11 ln ahquoc of a fieki sample spiked with lhc analytes of 1nterts1 1n the laboratOf) SurTOJitCI lR added in the labontOf) 10 all samples taken for 1he analysbulls of volatile oraanics by JIS ctuOmltopphytman spectrometry Surroaates are compounds not typkally found u contaminants in the environment They are Similar in StrUCt1~ 10 compounds beinJ metsured These compounds are frequenlly isOiopically labelled such u deutented oraanics

The resuhs obtained from the analysis of these spiked samples ue used tO control assess and documtnl the Kcurncy of an analyucal me1hod

11 bull f Standards

SlllldardJ will be used at the frequency specified in Seclion 8 of lhis QAPjP Standampnb for the volati le oraanics analysis or aqueous and soil au samples are pven in the specified rtfertnces and SOP Standards for the other panmeltn include

pH-buffen traceable to NIST (formtrly NBS)

ConducrivitymiddotKCI solutions

TemperaturtmiddotNIST (formerly NBS) cenified thennometer

HNu PID-isobutylene standard

Radiation-Source Check Standard

Maanetometer

Seismic

Elevation bullbull NOS Cenified Baselines

120 Perlormence 1nd Systems Audits

Definirions and procedurts for perfonnance and systems audits are Jiven in the PMP QAPP Section 712 and the Generic QAPjP Section 120

Activities for this project will be audited as part or the quanerly schedule established in the ProJlm Manaaement Plan For this project that quanerly audit will specifically include a visit to the site durinamp field activities to audit practices and I rtview or field documenlltion

Artlur D Little

-a-n = = ~

r

Qullny Assu rJ nce ProjeCt P1an for PiCIIIo Fum July 9 1990

Revbullsbullon No 1 p ll of))

Performance and systems audm of the llbomones used for the volaciles orJamcs analysis are conducced u pm of the US EPA ConDact Laboratory Proampnm (CLP)

130 Preventlttve Malntenbullnct

Equipmcnl for the onrall proanm u mamta1ned as abullven in lhe Pro11am Manaaement Plan Secuon 50 Propcny ManaJemcnt

In lhe field spare pan lnvcn10ncs m maincained for the pH meter conductivity meter HNu PID field Ja5 chromat01faph and expendable hems includinJ

pH Meie r electrodes banenes

Conductivity Mcaer baucries

HNu PID batteries

Explosivity meter bmcncs

Field Gas Chromatoaraph sp1 ~ GC column syrinJeS swaJclock fhtinas

140 lpectftc ftou llne Procedurebull UMd to AtHtt 01111 Precltlon Accurecy 8ftd Comptetentu

Explanalions and fonnulas for calculatina the necessary statistics for asseuinJ data precision accuracy and completeness arc aiven in the PMP Generic QAPjP Section 140 and the QAPP Section 79 A summary of the Qualhy Control samples analyzed to produce rtsuhs for suuiSiical catcualions is aiven in Table 14middot l

150 Corrtcttve Actions

Procedurts and types of corrective actions art 1iven in the PMP QAPP Section 7 )0

140 OUIIlty Auurence Reports to Mlnagement

Procedures and a descri ption of the comem for QA repons to manaJement are liven in the PMP QAPP Secrion 743

ArtlurD Little

- r -

QuaJuy A surJnce Project Plan for Ptc1llo Farm July 9 1990

Rev1110n No 1

bullmiddot ll olll

TM6e 1 1 aullty Control Slmpltt Analynd to Product Ru111 for ltlltlltlcal CaJeuletlons

t~Uflct Caeulonbull Quatlty Control Prtelt~n rtey

Samp+tt Averlgtlfirenc ecovwr Spectfleatlon

Volailc field Ouptlcue Oltprucs

in Aqueous MSIMSD X Sampla

SumJJlte Sptke X

Vofable Sysaem (probe) Orpnics Collocalts X

In SoU Ou $ampa SIIOOatds X

pH Con6uctivily Field Tbull penNre Duplicate X HNu PIO

Volllilc Standard X ~ Rldildon

623SlAAOILIAltlurD LlttJe

1. barcode 575210
2. barcodetext SDMS Doc ID 575210

I r I

Qualuy Auunnce ProJect Plan for Ptctllo Farm

July 9 1990 Revision No I Pore l9 of ll

and analyzed in the same manner as the field samples collected ucepc thac tnp bilmk sample bottles are 21 opened m rhe field

The results obtained rrom analym of tnp blanks arc used ro aucu pocenriaJ JOWCU or concamination in the labornory and dunnamp nnspon Potenaal sources ol concamination include laborltory reaampencs sample contau1er and laboramry alassware cleanlna procedures cross contamtnauon dunnamp sh1pmcnr arnb1cn1 lUI or con~a~t with analyrical slauwltthardware dunnJ laboratory sample preparation and anaJysil

11 13 Equipment ll1nks The frequenc y of aqueous equipment blanks is one per day of samplina and the frequency of aascous equipmcnc blanks n at least one system blamplk per day of sampUna Equipment blanks will be analyzed as pan of the Private We ll (Subtask 32) MonilorinJ Well (Subutsk 33) and Sot Gas (Subtask 37) Surveys

An equipment blank is prepartd by eltposina samplina materials (bottles collection devius etc) to the samphnJ envtronment without allowinamp them to actively mix with the matrix of interest

For 1he aqueous samples collected from the Private and Monitorina Wells deionized distilled water with oraanics removed by carbon adsorption (reaaent water) is sent to the field and used tO produce an equipment blank The rcatent water is exposed to field conditions paned throuah decontaminated sample equipment and collected in an empty sample conta iner for analysis In the case of private wells samples will typically be collected directly into the sample container Thcrdore the equipment blank would be e~tposed only tO field conditions not samplina equipment other than the container

For the soil au maaiK system blanks are run to chetk the decontaminated samplina appantus (probe adaptor IOcc syrinae) for contamination by dtawina ambient air from above around throuah the syste m and comparinJ the analysis to a concumn1ly sampled ambient air analysis

Equipment blanks arc handled (i n the case of the aqueous samples from the wells preserved) tnnsponed and analyzed bulln the same manner as the samples collected that day

Results obtained from analysis of equipment blanks are used to assess the same potential contamination as trip blanks and additional potential contamination from samplinamp equipment used to collect and transfer samples (such as buckets tubina and corers) and site ambient conditions

1114 Method lllnks The frequency of lflalyzina method blanks in the laboratory for the analysis of

_ volatile oraanics from Private and Monttorinamp Wells is specified in the referenced methods Method blanks for the sot aas survey are analyzed at least once a day

-n = = Cll

Artlur D Little 6UUARCltILI

- r I

Quahty Assurance Project Plan for Plctllo Farm Ju ly 9 1990

Rc vts lon No I Pare 30 or 33

The dKontaminatcd 2 cc subsamphnJ synn1cs m checked for contamination pnor 10 wnplinJ uch day by inJCCIInJ nnroampen earner JU 1nto the aas chromato~faph

11 2 Oupllelle S1mplt1

Duplicate tamples are defined u scpante samples Ween from the same soutte The analyncal sul11 obtained from these samples are used to eSiablish control and u seu llld document the p~cJsJon of analysis andor samplinJ so that COITCctive aclions may be 1aken as necessary and precision may be documented Sevtnl types of duplicaiC samples are dcscnbed below

~2~q~y0o1~C field duplicates for private and monitorinJ well samplina is one per 20 samples collected per sample maUb In th is case the aqueous samples from the private and rnonnorinJ wells are considered two differtnt maaicn The frequency of Jaseoos fi eld duplicates for the Soil Gas Surve y is one per 20 samples collec1ed and analyzed

Soil 111 duplcares are collecred by urracrina separate aliquou from rhe probe The initial sample is collecred in a syri nae and analyzed Conditions are allowed 10 equilibrare for 11 Jeasr 5 minutes and then a duplicm1e sample aliquoc is coUecled in the syrinae and analyzed

Field duplica~es are handled transponed and anal yzed in he same manner as are the orher samples collec~ed 1ha1 day

Duplicate restinJ will also be undenaken for pH conductivily ~emperature ndiarion explosivily field intensiry and elevariondistance at a frequency of at leut I in 20 measuremems

The resuhs obtained from analyzina field duplicares are used to assess and documenl the reproducibilily of overall samplinJ handlinJ and analyrical procedures Duplicate samples raken in the field represent rhe non-homoaeneity of field conditions Therefore it is expected rhat precision estimates obcained from the analysis of field duplicate samples will have substantial associated variability more so than replicate samples prepared in the laboratory

11 22 Ubcntory AepllcatH Replicate samples are defined as rwo sa mple aliquots taken from the same sample comainer and analyzed independe ntly The frequency of laboratory replicates for volatiles analysis of aqueous samples is speci fied in the method references All soil au samples In 1he syri nge are analyzed a1 least a minimum of rwice to insure reproducabiliry

)

623UARC~IArtlur D Little

- r --

Quahty A~surampnce Pro~c1 Plan fat Pactllo farm July 9 1990

Rcvasaon No 1 Pase ll o( ll

11 3 Spiked Sampltl

The frequency of analyrlnJ mam spbullkesmamx spLkt duplicates of aqueous pmplcs for volaules samples 11 one per case of field samples or per 20 samples (whichever is tIIR f~quenl) A matru sptke 11 ln ahquoc of a fieki sample spiked with lhc analytes of 1nterts1 1n the laboratOf) SurTOJitCI lR added in the labontOf) 10 all samples taken for 1he analysbulls of volatile oraanics by JIS ctuOmltopphytman spectrometry Surroaates are compounds not typkally found u contaminants in the environment They are Similar in StrUCt1~ 10 compounds beinJ metsured These compounds are frequenlly isOiopically labelled such u deutented oraanics

The resuhs obtained from the analysis of these spiked samples ue used tO control assess and documtnl the Kcurncy of an analyucal me1hod

11 bull f Standards

SlllldardJ will be used at the frequency specified in Seclion 8 of lhis QAPjP Standampnb for the volati le oraanics analysis or aqueous and soil au samples are pven in the specified rtfertnces and SOP Standards for the other panmeltn include

pH-buffen traceable to NIST (formtrly NBS)

ConducrivitymiddotKCI solutions

TemperaturtmiddotNIST (formerly NBS) cenified thennometer

HNu PID-isobutylene standard

Radiation-Source Check Standard

Maanetometer

Seismic

Elevation bullbull NOS Cenified Baselines

120 Perlormence 1nd Systems Audits

Definirions and procedurts for perfonnance and systems audits are Jiven in the PMP QAPP Section 712 and the Generic QAPjP Section 120

Activities for this project will be audited as part or the quanerly schedule established in the ProJlm Manaaement Plan For this project that quanerly audit will specifically include a visit to the site durinamp field activities to audit practices and I rtview or field documenlltion

Artlur D Little

-a-n = = ~

r

Qullny Assu rJ nce ProjeCt P1an for PiCIIIo Fum July 9 1990

Revbullsbullon No 1 p ll of))

Performance and systems audm of the llbomones used for the volaciles orJamcs analysis are conducced u pm of the US EPA ConDact Laboratory Proampnm (CLP)

130 Preventlttve Malntenbullnct

Equipmcnl for the onrall proanm u mamta1ned as abullven in lhe Pro11am Manaaement Plan Secuon 50 Propcny ManaJemcnt

In lhe field spare pan lnvcn10ncs m maincained for the pH meter conductivity meter HNu PID field Ja5 chromat01faph and expendable hems includinJ

pH Meie r electrodes banenes

Conductivity Mcaer baucries

HNu PID batteries

Explosivity meter bmcncs

Field Gas Chromatoaraph sp1 ~ GC column syrinJeS swaJclock fhtinas

140 lpectftc ftou llne Procedurebull UMd to AtHtt 01111 Precltlon Accurecy 8ftd Comptetentu

Explanalions and fonnulas for calculatina the necessary statistics for asseuinJ data precision accuracy and completeness arc aiven in the PMP Generic QAPjP Section 140 and the QAPP Section 79 A summary of the Qualhy Control samples analyzed to produce rtsuhs for suuiSiical catcualions is aiven in Table 14middot l

150 Corrtcttve Actions

Procedurts and types of corrective actions art 1iven in the PMP QAPP Section 7 )0

140 OUIIlty Auurence Reports to Mlnagement

Procedures and a descri ption of the comem for QA repons to manaJement are liven in the PMP QAPP Secrion 743

ArtlurD Little

- r -

QuaJuy A surJnce Project Plan for Ptc1llo Farm July 9 1990

Rev1110n No 1

bullmiddot ll olll

TM6e 1 1 aullty Control Slmpltt Analynd to Product Ru111 for ltlltlltlcal CaJeuletlons

t~Uflct Caeulonbull Quatlty Control Prtelt~n rtey

Samp+tt Averlgtlfirenc ecovwr Spectfleatlon

Volailc field Ouptlcue Oltprucs

in Aqueous MSIMSD X Sampla

SumJJlte Sptke X

Vofable Sysaem (probe) Orpnics Collocalts X

In SoU Ou $ampa SIIOOatds X

pH Con6uctivily Field Tbull penNre Duplicate X HNu PIO

Volllilc Standard X ~ Rldildon

623SlAAOILIAltlurD LlttJe

1. barcode 575210
2. barcodetext SDMS Doc ID 575210

- r I

Quahty Assurance Project Plan for Plctllo Farm Ju ly 9 1990

Rc vts lon No I Pare 30 or 33

The dKontaminatcd 2 cc subsamphnJ synn1cs m checked for contamination pnor 10 wnplinJ uch day by inJCCIInJ nnroampen earner JU 1nto the aas chromato~faph

11 2 Oupllelle S1mplt1

Duplicate tamples are defined u scpante samples Ween from the same soutte The analyncal sul11 obtained from these samples are used to eSiablish control and u seu llld document the p~cJsJon of analysis andor samplinJ so that COITCctive aclions may be 1aken as necessary and precision may be documented Sevtnl types of duplicaiC samples are dcscnbed below

~2~q~y0o1~C field duplicates for private and monitorinJ well samplina is one per 20 samples collected per sample maUb In th is case the aqueous samples from the private and rnonnorinJ wells are considered two differtnt maaicn The frequency of Jaseoos fi eld duplicates for the Soil Gas Surve y is one per 20 samples collec1ed and analyzed

Soil 111 duplcares are collecred by urracrina separate aliquou from rhe probe The initial sample is collecred in a syri nae and analyzed Conditions are allowed 10 equilibrare for 11 Jeasr 5 minutes and then a duplicm1e sample aliquoc is coUecled in the syrinae and analyzed

Field duplica~es are handled transponed and anal yzed in he same manner as are the orher samples collec~ed 1ha1 day

Duplicate restinJ will also be undenaken for pH conductivily ~emperature ndiarion explosivily field intensiry and elevariondistance at a frequency of at leut I in 20 measuremems

The resuhs obtained from analyzina field duplicares are used to assess and documenl the reproducibilily of overall samplinJ handlinJ and analyrical procedures Duplicate samples raken in the field represent rhe non-homoaeneity of field conditions Therefore it is expected rhat precision estimates obcained from the analysis of field duplicate samples will have substantial associated variability more so than replicate samples prepared in the laboratory

11 22 Ubcntory AepllcatH Replicate samples are defined as rwo sa mple aliquots taken from the same sample comainer and analyzed independe ntly The frequency of laboratory replicates for volatiles analysis of aqueous samples is speci fied in the method references All soil au samples In 1he syri nge are analyzed a1 least a minimum of rwice to insure reproducabiliry

)

623UARC~IArtlur D Little

- r --

Quahty A~surampnce Pro~c1 Plan fat Pactllo farm July 9 1990

Rcvasaon No 1 Pase ll o( ll

11 3 Spiked Sampltl

The frequency of analyrlnJ mam spbullkesmamx spLkt duplicates of aqueous pmplcs for volaules samples 11 one per case of field samples or per 20 samples (whichever is tIIR f~quenl) A matru sptke 11 ln ahquoc of a fieki sample spiked with lhc analytes of 1nterts1 1n the laboratOf) SurTOJitCI lR added in the labontOf) 10 all samples taken for 1he analysbulls of volatile oraanics by JIS ctuOmltopphytman spectrometry Surroaates are compounds not typkally found u contaminants in the environment They are Similar in StrUCt1~ 10 compounds beinJ metsured These compounds are frequenlly isOiopically labelled such u deutented oraanics

The resuhs obtained from the analysis of these spiked samples ue used tO control assess and documtnl the Kcurncy of an analyucal me1hod

11 bull f Standards

SlllldardJ will be used at the frequency specified in Seclion 8 of lhis QAPjP Standampnb for the volati le oraanics analysis or aqueous and soil au samples are pven in the specified rtfertnces and SOP Standards for the other panmeltn include

pH-buffen traceable to NIST (formtrly NBS)

ConducrivitymiddotKCI solutions

TemperaturtmiddotNIST (formerly NBS) cenified thennometer

HNu PID-isobutylene standard

Radiation-Source Check Standard

Maanetometer

Seismic

Elevation bullbull NOS Cenified Baselines

120 Perlormence 1nd Systems Audits

Definirions and procedurts for perfonnance and systems audits are Jiven in the PMP QAPP Section 712 and the Generic QAPjP Section 120

Activities for this project will be audited as part or the quanerly schedule established in the ProJlm Manaaement Plan For this project that quanerly audit will specifically include a visit to the site durinamp field activities to audit practices and I rtview or field documenlltion

Artlur D Little

-a-n = = ~

r

Qullny Assu rJ nce ProjeCt P1an for PiCIIIo Fum July 9 1990

Revbullsbullon No 1 p ll of))

Performance and systems audm of the llbomones used for the volaciles orJamcs analysis are conducced u pm of the US EPA ConDact Laboratory Proampnm (CLP)

130 Preventlttve Malntenbullnct

Equipmcnl for the onrall proanm u mamta1ned as abullven in lhe Pro11am Manaaement Plan Secuon 50 Propcny ManaJemcnt

In lhe field spare pan lnvcn10ncs m maincained for the pH meter conductivity meter HNu PID field Ja5 chromat01faph and expendable hems includinJ

pH Meie r electrodes banenes

Conductivity Mcaer baucries

HNu PID batteries

Explosivity meter bmcncs

Field Gas Chromatoaraph sp1 ~ GC column syrinJeS swaJclock fhtinas

140 lpectftc ftou llne Procedurebull UMd to AtHtt 01111 Precltlon Accurecy 8ftd Comptetentu

Explanalions and fonnulas for calculatina the necessary statistics for asseuinJ data precision accuracy and completeness arc aiven in the PMP Generic QAPjP Section 140 and the QAPP Section 79 A summary of the Qualhy Control samples analyzed to produce rtsuhs for suuiSiical catcualions is aiven in Table 14middot l

150 Corrtcttve Actions

Procedurts and types of corrective actions art 1iven in the PMP QAPP Section 7 )0

140 OUIIlty Auurence Reports to Mlnagement

Procedures and a descri ption of the comem for QA repons to manaJement are liven in the PMP QAPP Secrion 743

ArtlurD Little

- r -

QuaJuy A surJnce Project Plan for Ptc1llo Farm July 9 1990

Rev1110n No 1

bullmiddot ll olll

TM6e 1 1 aullty Control Slmpltt Analynd to Product Ru111 for ltlltlltlcal CaJeuletlons

t~Uflct Caeulonbull Quatlty Control Prtelt~n rtey

Samp+tt Averlgtlfirenc ecovwr Spectfleatlon

Volailc field Ouptlcue Oltprucs

in Aqueous MSIMSD X Sampla

SumJJlte Sptke X

Vofable Sysaem (probe) Orpnics Collocalts X

In SoU Ou $ampa SIIOOatds X

pH Con6uctivily Field Tbull penNre Duplicate X HNu PIO

Volllilc Standard X ~ Rldildon

623SlAAOILIAltlurD LlttJe

1. barcode 575210
2. barcodetext SDMS Doc ID 575210

- r --

Quahty A~surampnce Pro~c1 Plan fat Pactllo farm July 9 1990

Rcvasaon No 1 Pase ll o( ll

11 3 Spiked Sampltl

The frequency of analyrlnJ mam spbullkesmamx spLkt duplicates of aqueous pmplcs for volaules samples 11 one per case of field samples or per 20 samples (whichever is tIIR f~quenl) A matru sptke 11 ln ahquoc of a fieki sample spiked with lhc analytes of 1nterts1 1n the laboratOf) SurTOJitCI lR added in the labontOf) 10 all samples taken for 1he analysbulls of volatile oraanics by JIS ctuOmltopphytman spectrometry Surroaates are compounds not typkally found u contaminants in the environment They are Similar in StrUCt1~ 10 compounds beinJ metsured These compounds are frequenlly isOiopically labelled such u deutented oraanics

The resuhs obtained from the analysis of these spiked samples ue used tO control assess and documtnl the Kcurncy of an analyucal me1hod

11 bull f Standards

SlllldardJ will be used at the frequency specified in Seclion 8 of lhis QAPjP Standampnb for the volati le oraanics analysis or aqueous and soil au samples are pven in the specified rtfertnces and SOP Standards for the other panmeltn include

pH-buffen traceable to NIST (formtrly NBS)

ConducrivitymiddotKCI solutions

TemperaturtmiddotNIST (formerly NBS) cenified thennometer

HNu PID-isobutylene standard

Radiation-Source Check Standard

Maanetometer

Seismic

Elevation bullbull NOS Cenified Baselines

120 Perlormence 1nd Systems Audits

Definirions and procedurts for perfonnance and systems audits are Jiven in the PMP QAPP Section 712 and the Generic QAPjP Section 120

Activities for this project will be audited as part or the quanerly schedule established in the ProJlm Manaaement Plan For this project that quanerly audit will specifically include a visit to the site durinamp field activities to audit practices and I rtview or field documenlltion

Artlur D Little

-a-n = = ~

r

Qullny Assu rJ nce ProjeCt P1an for PiCIIIo Fum July 9 1990

Revbullsbullon No 1 p ll of))

Performance and systems audm of the llbomones used for the volaciles orJamcs analysis are conducced u pm of the US EPA ConDact Laboratory Proampnm (CLP)

130 Preventlttve Malntenbullnct

Equipmcnl for the onrall proanm u mamta1ned as abullven in lhe Pro11am Manaaement Plan Secuon 50 Propcny ManaJemcnt

In lhe field spare pan lnvcn10ncs m maincained for the pH meter conductivity meter HNu PID field Ja5 chromat01faph and expendable hems includinJ

pH Meie r electrodes banenes

Conductivity Mcaer baucries

HNu PID batteries

Explosivity meter bmcncs

Field Gas Chromatoaraph sp1 ~ GC column syrinJeS swaJclock fhtinas

140 lpectftc ftou llne Procedurebull UMd to AtHtt 01111 Precltlon Accurecy 8ftd Comptetentu

Explanalions and fonnulas for calculatina the necessary statistics for asseuinJ data precision accuracy and completeness arc aiven in the PMP Generic QAPjP Section 140 and the QAPP Section 79 A summary of the Qualhy Control samples analyzed to produce rtsuhs for suuiSiical catcualions is aiven in Table 14middot l

150 Corrtcttve Actions

Procedurts and types of corrective actions art 1iven in the PMP QAPP Section 7 )0

140 OUIIlty Auurence Reports to Mlnagement

Procedures and a descri ption of the comem for QA repons to manaJement are liven in the PMP QAPP Secrion 743

ArtlurD Little

- r -

QuaJuy A surJnce Project Plan for Ptc1llo Farm July 9 1990

Rev1110n No 1

bullmiddot ll olll

TM6e 1 1 aullty Control Slmpltt Analynd to Product Ru111 for ltlltlltlcal CaJeuletlons

t~Uflct Caeulonbull Quatlty Control Prtelt~n rtey

Samp+tt Averlgtlfirenc ecovwr Spectfleatlon

Volailc field Ouptlcue Oltprucs

in Aqueous MSIMSD X Sampla

SumJJlte Sptke X

Vofable Sysaem (probe) Orpnics Collocalts X

In SoU Ou $ampa SIIOOatds X

pH Con6uctivily Field Tbull penNre Duplicate X HNu PIO

Volllilc Standard X ~ Rldildon

623SlAAOILIAltlurD LlttJe

1. barcode 575210
2. barcodetext SDMS Doc ID 575210

r

Qullny Assu rJ nce ProjeCt P1an for PiCIIIo Fum July 9 1990

Revbullsbullon No 1 p ll of))

Performance and systems audm of the llbomones used for the volaciles orJamcs analysis are conducced u pm of the US EPA ConDact Laboratory Proampnm (CLP)

130 Preventlttve Malntenbullnct

Equipmcnl for the onrall proanm u mamta1ned as abullven in lhe Pro11am Manaaement Plan Secuon 50 Propcny ManaJemcnt

In lhe field spare pan lnvcn10ncs m maincained for the pH meter conductivity meter HNu PID field Ja5 chromat01faph and expendable hems includinJ

pH Meie r electrodes banenes

Conductivity Mcaer baucries

HNu PID batteries

Explosivity meter bmcncs

Field Gas Chromatoaraph sp1 ~ GC column syrinJeS swaJclock fhtinas

140 lpectftc ftou llne Procedurebull UMd to AtHtt 01111 Precltlon Accurecy 8ftd Comptetentu

Explanalions and fonnulas for calculatina the necessary statistics for asseuinJ data precision accuracy and completeness arc aiven in the PMP Generic QAPjP Section 140 and the QAPP Section 79 A summary of the Qualhy Control samples analyzed to produce rtsuhs for suuiSiical catcualions is aiven in Table 14middot l

150 Corrtcttve Actions

Procedurts and types of corrective actions art 1iven in the PMP QAPP Section 7 )0

140 OUIIlty Auurence Reports to Mlnagement

Procedures and a descri ption of the comem for QA repons to manaJement are liven in the PMP QAPP Secrion 743

ArtlurD Little

- r -

QuaJuy A surJnce Project Plan for Ptc1llo Farm July 9 1990

Rev1110n No 1

bullmiddot ll olll

TM6e 1 1 aullty Control Slmpltt Analynd to Product Ru111 for ltlltlltlcal CaJeuletlons

t~Uflct Caeulonbull Quatlty Control Prtelt~n rtey

Samp+tt Averlgtlfirenc ecovwr Spectfleatlon

Volailc field Ouptlcue Oltprucs

in Aqueous MSIMSD X Sampla

SumJJlte Sptke X

Vofable Sysaem (probe) Orpnics Collocalts X

In SoU Ou $ampa SIIOOatds X

pH Con6uctivily Field Tbull penNre Duplicate X HNu PIO

Volllilc Standard X ~ Rldildon

623SlAAOILIAltlurD LlttJe

1. barcode 575210
2. barcodetext SDMS Doc ID 575210

- r -

QuaJuy A surJnce Project Plan for Ptc1llo Farm July 9 1990

Rev1110n No 1

bullmiddot ll olll

TM6e 1 1 aullty Control Slmpltt Analynd to Product Ru111 for ltlltlltlcal CaJeuletlons

t~Uflct Caeulonbull Quatlty Control Prtelt~n rtey

Samp+tt Averlgtlfirenc ecovwr Spectfleatlon

Volailc field Ouptlcue Oltprucs

in Aqueous MSIMSD X Sampla

SumJJlte Sptke X

Vofable Sysaem (probe) Orpnics Collocalts X

In SoU Ou $ampa SIIOOatds X

pH Con6uctivily Field Tbull penNre Duplicate X HNu PIO

Volllilc Standard X ~ Rldildon

623SlAAOILIAltlurD LlttJe

1. barcode 575210
2. barcodetext SDMS Doc ID 575210