...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring...

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Transcript of ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring...

Page 1: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer
Page 2: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer
Page 3: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer
Page 4: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer
Page 5: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer
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91-02522-C October 2011

Figure 1

Berkeley Transfer StationBerkeley, California

Site Vicinity Map

N

Site

Page 12: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

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BBB

’B

Qsl Qsl

- Geologic Unit - Franciscan Complex

- Geologic Unit - Hillslope Deposits

- Approximate Boring Location

Geologic Cross Section

AA A’A’

A’

A’

A’

A’

B-3B-3

Figure 2

Berkeley Transfer StationBerkeley, California

Site Plan and Site Geology Map

October 201191-02522-C

Not to ScaleB-2B-2

B-1B-1

Source: United StatesGeologic Survey, GeologicMap of Alameda County, USGSScientific Map Investigations2918

B-2B-2

- Artificial fill

- Alluvium (Holocene)

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Page 13: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

October 31, 2011

Dear Roger:

WorkOrder: 1110650

Client Project ID: #91-02522-C; Berkeley Transfer

Station

Geosphere Consultants

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Date Sampled: 10/21/11

Date Received: 10/21/11

Date Reported: 10/31/11

Date Completed: 10/28/11

Analytical Report

All analyses were completed satisfactorily and all QC samples were found to be within our control limits.

If you have any questions or concerns, please feel free to give me a call. Thank you for choosing

McCampbell Analytical Laboratories for your analytical needs.

Best regards,

Enclosed within are:

2) A QC report for the above samples,

4) An invoice for analytical services.

3) A copy of the chain of custody, and

#91-02522-C; Berkeley Transfer Station,1) The results of the analyzed samples from your project:3

Angela Rydelius

Laboratory Manager

McCampbell Analytical, Inc.

The analytical results relate only to the items tested.

Page 1 of 22

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Page 2 of 22

Page 15: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

McCampbell Analytical, Inc.

1534 Willow Pass Rd

Pittsburg, CA 94565-1701

(925) 252-9262

CHAIN-OF-CUSTODY RECORD Page

Lab ID Matrix Collection Date Hold

Requested Tests (See legend below)

Report to:

Roger Wilcox

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

925-314-7180 FAX: 925-855-7140

PO:

10/21/2011

Client ID

ProjectNo: #91-02522-C; Berkeley Transfer Station

WorkOrder: 1110650

1 of 1

Date Printed:

Date Received: 10/21/2011

1 2 3 4 5 6 7 8 9 10 11 12

Geosphere Consultants

Bill to:

Jennifer Janeson

Geosphere Consultants

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Requested TAT: 5 days

ClientCode: GCSR

Email: [email protected]

EDF Fax Email HardCopy ThirdParty

[email protected]

Excel J-flagWriteOn

cc:

WaterTrax

A1110650-001 Soil 10/21/2011 7:30B1-1 A A A A A A

A1110650-002 Soil 10/21/2011 8:10B2-1 A A A A A A

A1110650-003 Soil 10/21/2011 9:10B3-1 A A A A A A

Prepared by: Maria Venegas

NOTE: Soil samples are discarded 60 days after results are reported unless other arrangements are made (Water samples are 30 days). Hazardous samples will be returned to client or disposed of at client expense.

Comments:

8081PCB_S 8260B_S 8270D_S CAM17MS_S G-MBTEX_S

STLCMETALMS_S TPH(DMO)_S

1 2 3 4 5

6 7 8 9 10

Test Legend:

11 12

Page 3 of 22

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Sample Receipt Checklist

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

Client Name: Geosphere Consultants

WorkOrder N°: 1110650

Date and Time Received: 10/21/2011 1:38:26 PM

Checklist completed and reviewed by: Maria Venegas

Matrix: Soil Carrier: Client Drop-In

Shipping container/cooler in good condition? Yes No

Custody seals intact on shipping container/cooler? Yes No NA

Samples Received on Ice? Yes No

Chain of custody present? Yes No

Chain of custody signed when relinquished and received? Yes No

Chain of custody agrees with sample labels? Yes No

Samples in proper containers/bottles? Yes No

Sample containers intact? Yes No

Sufficient sample volume for indicated test? Yes No

All samples received within holding time? Yes No

NAContainer/Temp Blank temperature

Yes No No VOA vials submittedWater - VOA vials have zero headspace / no bubbles?

Metal - pH acceptable upon receipt (pH<2)? Yes No NA

* NOTE: If the "No" box is checked, see comments below.

Cooler Temp: 18.2°C

Chain of Custody (COC) Information

Yes NoSample IDs noted by Client on COC?

Yes NoDate and Time of collection noted by Client on COC?

Yes NoSampler's name noted on COC?

Sample Receipt Information

Sample Preservation and Hold Time (HT) Information

Sample labels checked for correct preservation? Yes No

Project Name: #91-02522-C; Berkeley Transfer Station

(Ice Type: BLUE ICE )

Client contacted: Date contacted: Contacted by:

Comments:

Page 4 of 22

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Client Project ID: #91-02522-C;

Berkeley Transfer Station

Geosphere Consultants

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Date Sampled: 10/21/11

Date Received: 10/21/11

Date Extracted: 10/21/11

Date Analyzed: 10/22/11

1110650-001A 1110650-002A 1110650-003A

B1-1 B2-1 B3-1

Lab ID

Client ID

S S S

200 1000 500

Matrix

DF

Reporting Limit for

DF =1

S W

Extraction Method: Analytical Method:

Organochlorine Pesticides (8080 Basic Target List) + PCBs

SW8081A/8082SW3550B Work Order: 1110650

mg/kg µg/LCompound Concentration

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

0.001 NAAldrin ND<0.20 ND<1.0 ND<0.50

0.001 NAa-BHC ND<0.20 ND<1.0 ND<0.50

0.001 NAb-BHC ND<0.20 ND<1.0 ND<0.50

0.001 NAd-BHC ND<0.20 ND<1.0 ND<0.50

0.001 NAg-BHC ND<0.20 ND<1.0 ND<0.50

0.025 NAChlordane (Technical) ND<5.0 ND<25 ND<12

0.001 NAa-Chlordane ND<0.20 ND<1.0 ND<0.50

0.001 NAg-Chlordane ND<0.20 ND<1.0 ND<0.50

0.001 NAp,p-DDD ND<0.20 ND<1.0 ND<0.50

0.001 NAp,p-DDE ND<0.20 ND<1.0 ND<0.50

0.001 NAp,p-DDT ND<0.20 ND<1.0 ND<0.50

0.001 NADieldrin ND<0.20 ND<1.0 ND<0.50

0.001 NAEndosulfan I ND<0.20 ND<1.0 ND<0.50

0.001 NAEndosulfan II ND<0.20 ND<1.0 ND<0.50

0.001 NAEndosulfan sulfate ND<0.20 ND<1.0 ND<0.50

0.001 NAEndrin ND<0.20 ND<1.0 ND<0.50

0.001 NAEndrin aldehyde ND<0.20 ND<1.0 ND<0.50

0.001 NAEndrin ketone ND<0.20 ND<1.0 ND<0.50

0.001 NAHeptachlor ND<0.20 ND<1.0 ND<0.50

0.001 NAHeptachlor epoxide ND<0.20 ND<1.0 ND<0.50

0.01 NAHexachlorobenzene ND<2.0 ND<10 ND<5.0

0.02 NAHexachlorocyclopentadiene ND<4.0 ND<20 ND<10

0.001 NAMethoxychlor ND<0.20 ND<1.0 ND<0.50

0.05 NAToxaphene ND<10 ND<50 ND<25

0.05 NAAroclor1016 ND<10 ND<50 ND<25

0.05 NAAroclor1221 ND<10 ND<50 ND<25

0.05 NAAroclor1232 ND<10 ND<50 ND<25

0.05 NAAroclor1242 ND<10 ND<50 ND<25

0.05 NAAroclor1248 ND<10 ND<50 ND<25

0.05 NAAroclor1254 ND<10 ND<50 ND<25

0.05 NAAroclor1260 ND<10 ND<50 ND<25

0.05 NAPCBs, total ND<10 ND<50 ND<25

Comments a3 a3 a3

* soil/sludge/solid samples in mg/kg.

ND means not detected above the reporting limit/method detection limit; N/A means analyte not applicable to this analysis; %SS = Percent Recovery of

Surrogate Standard; DF = Dilution Factor.

# surrogate diluted out of range or surrogate coelutes with another peak

a3) sample diluted due to high organic content.

Surrogate Recoveries (%)

%SS: 107 ---# 108

DHS ELAP Certification 1644 Angela Rydelius, Lab Manager

Page 5 of 22

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B1-1

Client Project ID: #91-02522-C;

Berkeley Transfer Station

Geosphere Consultants

Extraction Method: Analytical Method:

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Lab ID

Client ID

Matrix Soil

1110650-001A

Compound Concentration * Compound Concentration *Reporting

LimitDFReporting

LimitDF

Volatile Organics by P&T and GC/MS (Basic Target List)*

SW8260BSW5030B Work Order: 1110650

Date Sampled: 10/21/11

Date Received: 10/21/11

Date Extracted: 10/21/11

Date Analyzed: 10/26/11

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

Surrogate Recoveries (%)

Acetone 0.18 1.0 0.05 tert-Amyl methyl ether (TAME) ND 1.0 0.005

Benzene ND 1.0 0.005 Bromobenzene ND 1.0 0.005

Bromochloromethane ND 1.0 0.005 Bromodichloromethane ND 1.0 0.005

Bromoform ND 1.0 0.005 Bromomethane ND 1.0 0.005

2-Butanone (MEK) 0.030 1.0 0.02 t-Butyl alcohol (TBA) ND 1.0 0.05

n-Butyl benzene ND 1.0 0.005 sec-Butyl benzene ND 1.0 0.005

tert-Butyl benzene ND 1.0 0.005 Carbon Disulfide ND 1.0 0.005

Carbon Tetrachloride ND 1.0 0.005 Chlorobenzene ND 1.0 0.005

Chloroethane ND 1.0 0.005 Chloroform ND 1.0 0.005

Chloromethane ND 1.0 0.005 2-Chlorotoluene ND 1.0 0.005

4-Chlorotoluene ND 1.0 0.005 Dibromochloromethane ND 1.0 0.005

1,2-Dibromo-3-chloropropane ND 1.0 0.004 1,2-Dibromoethane (EDB) ND 1.0 0.004

Dibromomethane ND 1.0 0.005 1,2-Dichlorobenzene ND 1.0 0.005

1,3-Dichlorobenzene ND 1.0 0.005 1,4-Dichlorobenzene ND 1.0 0.005

Dichlorodifluoromethane ND 1.0 0.005 1,1-Dichloroethane ND 1.0 0.005

1,2-Dichloroethane (1,2-DCA) ND 1.0 0.004 1,1-Dichloroethene ND 1.0 0.005

cis-1,2-Dichloroethene ND 1.0 0.005 trans-1,2-Dichloroethene ND 1.0 0.005

1,2-Dichloropropane ND 1.0 0.005 1,3-Dichloropropane ND 1.0 0.005

2,2-Dichloropropane ND 1.0 0.005 1,1-Dichloropropene ND 1.0 0.005

cis-1,3-Dichloropropene ND 1.0 0.005 trans-1,3-Dichloropropene ND 1.0 0.005

Diisopropyl ether (DIPE) ND 1.0 0.005 Ethylbenzene ND 1.0 0.005

Ethyl tert-butyl ether (ETBE) ND 1.0 0.005 Freon 113 ND 1.0 0.1

Hexachlorobutadiene ND 1.0 0.005 Hexachloroethane ND 1.0 0.005

2-Hexanone ND 1.0 0.005 Isopropylbenzene ND 1.0 0.005

4-Isopropyl toluene ND 1.0 0.005 Methyl-t-butyl ether (MTBE) ND 1.0 0.005

Methylene chloride ND 1.0 0.005 4-Methyl-2-pentanone (MIBK) ND 1.0 0.005

Naphthalene ND 1.0 0.005 n-Propyl benzene ND 1.0 0.005

Styrene ND 1.0 0.005 1,1,1,2-Tetrachloroethane ND 1.0 0.005

1,1,2,2-Tetrachloroethane ND 1.0 0.005 Tetrachloroethene ND 1.0 0.005

Toluene ND 1.0 0.005 1,2,3-Trichlorobenzene ND 1.0 0.005

1,2,4-Trichlorobenzene ND 1.0 0.005 1,1,1-Trichloroethane ND 1.0 0.005

1,1,2-Trichloroethane ND 1.0 0.005 Trichloroethene ND 1.0 0.005

Trichlorofluoromethane ND 1.0 0.005 1,2,3-Trichloropropane ND 1.0 0.005

1,2,4-Trimethylbenzene ND 1.0 0.005 1,3,5-Trimethylbenzene ND 1.0 0.005

Vinyl Chloride ND 1.0 0.005 Xylenes, Total ND 1.0 0.005

%SS1: 113 %SS2: 116

%SS3: 111

* water and vapor samples are reported in µg/L, soil/sludge/solid samples in mg/kg, product/oil/non-aqueous liquid samples and all TCLP & SPLP extracts are

reported in mg/L, wipe samples in µg/wipe.

ND means not detected above the reporting limit/method detection limit; N/A means analyte not applicable to this analysis; %SS = Percent Recovery of Surrogate

Standard; DF = Dilution Factor

# surrogate diluted out of range or coelutes with another peak; &) low surrogate due to matrix interference.

Comments:

DHS ELAP Certification 1644 Angela Rydelius, Lab ManagerPage 6 of 22

Page 19: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

B2-1

Client Project ID: #91-02522-C;

Berkeley Transfer Station

Geosphere Consultants

Extraction Method: Analytical Method:

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Lab ID

Client ID

Matrix Soil

1110650-002A

Compound Concentration * Compound Concentration *Reporting

LimitDFReporting

LimitDF

Volatile Organics by P&T and GC/MS (Basic Target List)*

SW8260BSW5030B Work Order: 1110650

Date Sampled: 10/21/11

Date Received: 10/21/11

Date Extracted: 10/21/11

Date Analyzed: 10/24/11

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

Surrogate Recoveries (%)

Acetone ND 1.0 0.05 tert-Amyl methyl ether (TAME) ND 1.0 0.005

Benzene ND 1.0 0.005 Bromobenzene ND 1.0 0.005

Bromochloromethane ND 1.0 0.005 Bromodichloromethane ND 1.0 0.005

Bromoform ND 1.0 0.005 Bromomethane ND 1.0 0.005

2-Butanone (MEK) ND 1.0 0.02 t-Butyl alcohol (TBA) ND 1.0 0.05

n-Butyl benzene ND 1.0 0.005 sec-Butyl benzene ND 1.0 0.005

tert-Butyl benzene ND 1.0 0.005 Carbon Disulfide ND 1.0 0.005

Carbon Tetrachloride ND 1.0 0.005 Chlorobenzene ND 1.0 0.005

Chloroethane ND 1.0 0.005 Chloroform ND 1.0 0.005

Chloromethane ND 1.0 0.005 2-Chlorotoluene ND 1.0 0.005

4-Chlorotoluene ND 1.0 0.005 Dibromochloromethane ND 1.0 0.005

1,2-Dibromo-3-chloropropane ND 1.0 0.004 1,2-Dibromoethane (EDB) ND 1.0 0.004

Dibromomethane ND 1.0 0.005 1,2-Dichlorobenzene ND 1.0 0.005

1,3-Dichlorobenzene ND 1.0 0.005 1,4-Dichlorobenzene ND 1.0 0.005

Dichlorodifluoromethane ND 1.0 0.005 1,1-Dichloroethane ND 1.0 0.005

1,2-Dichloroethane (1,2-DCA) ND 1.0 0.004 1,1-Dichloroethene ND 1.0 0.005

cis-1,2-Dichloroethene ND 1.0 0.005 trans-1,2-Dichloroethene ND 1.0 0.005

1,2-Dichloropropane ND 1.0 0.005 1,3-Dichloropropane ND 1.0 0.005

2,2-Dichloropropane ND 1.0 0.005 1,1-Dichloropropene ND 1.0 0.005

cis-1,3-Dichloropropene ND 1.0 0.005 trans-1,3-Dichloropropene ND 1.0 0.005

Diisopropyl ether (DIPE) ND 1.0 0.005 Ethylbenzene ND 1.0 0.005

Ethyl tert-butyl ether (ETBE) ND 1.0 0.005 Freon 113 ND 1.0 0.1

Hexachlorobutadiene ND 1.0 0.005 Hexachloroethane ND 1.0 0.005

2-Hexanone ND 1.0 0.005 Isopropylbenzene ND 1.0 0.005

4-Isopropyl toluene ND 1.0 0.005 Methyl-t-butyl ether (MTBE) ND 1.0 0.005

Methylene chloride ND 1.0 0.005 4-Methyl-2-pentanone (MIBK) ND 1.0 0.005

Naphthalene 0.018 1.0 0.005 n-Propyl benzene ND 1.0 0.005

Styrene ND 1.0 0.005 1,1,1,2-Tetrachloroethane ND 1.0 0.005

1,1,2,2-Tetrachloroethane ND 1.0 0.005 Tetrachloroethene ND 1.0 0.005

Toluene ND 1.0 0.005 1,2,3-Trichlorobenzene ND 1.0 0.005

1,2,4-Trichlorobenzene ND 1.0 0.005 1,1,1-Trichloroethane ND 1.0 0.005

1,1,2-Trichloroethane ND 1.0 0.005 Trichloroethene ND 1.0 0.005

Trichlorofluoromethane ND 1.0 0.005 1,2,3-Trichloropropane ND 1.0 0.005

1,2,4-Trimethylbenzene ND 1.0 0.005 1,3,5-Trimethylbenzene ND 1.0 0.005

Vinyl Chloride ND 1.0 0.005 Xylenes, Total ND 1.0 0.005

%SS1: 113 %SS2: 117

%SS3: 110

* water and vapor samples are reported in µg/L, soil/sludge/solid samples in mg/kg, product/oil/non-aqueous liquid samples and all TCLP & SPLP extracts are

reported in mg/L, wipe samples in µg/wipe.

ND means not detected above the reporting limit/method detection limit; N/A means analyte not applicable to this analysis; %SS = Percent Recovery of Surrogate

Standard; DF = Dilution Factor

# surrogate diluted out of range or coelutes with another peak; &) low surrogate due to matrix interference.

Comments:

DHS ELAP Certification 1644 Angela Rydelius, Lab ManagerPage 7 of 22

Page 20: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

B3-1

Client Project ID: #91-02522-C;

Berkeley Transfer Station

Geosphere Consultants

Extraction Method: Analytical Method:

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Lab ID

Client ID

Matrix Soil

1110650-003A

Compound Concentration * Compound Concentration *Reporting

LimitDFReporting

LimitDF

Volatile Organics by P&T and GC/MS (Basic Target List)*

SW8260BSW5030B Work Order: 1110650

Date Sampled: 10/21/11

Date Received: 10/21/11

Date Extracted: 10/21/11

Date Analyzed: 10/26/11

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

Surrogate Recoveries (%)

Acetone ND<2.5 50 0.05 tert-Amyl methyl ether (TAME) ND<0.25 50 0.005

Benzene ND<0.25 50 0.005 Bromobenzene ND<0.25 50 0.005

Bromochloromethane ND<0.25 50 0.005 Bromodichloromethane ND<0.25 50 0.005

Bromoform ND<0.25 50 0.005 Bromomethane ND<0.25 50 0.005

2-Butanone (MEK) ND<1.0 50 0.02 t-Butyl alcohol (TBA) ND<2.5 50 0.05

n-Butyl benzene ND<0.25 50 0.005 sec-Butyl benzene ND<0.25 50 0.005

tert-Butyl benzene ND<0.25 50 0.005 Carbon Disulfide ND<0.25 50 0.005

Carbon Tetrachloride ND<0.25 50 0.005 Chlorobenzene ND<0.25 50 0.005

Chloroethane ND<0.25 50 0.005 Chloroform ND<0.25 50 0.005

Chloromethane ND<0.25 50 0.005 2-Chlorotoluene ND<0.25 50 0.005

4-Chlorotoluene ND<0.25 50 0.005 Dibromochloromethane ND<0.25 50 0.005

1,2-Dibromo-3-chloropropane ND<0.20 50 0.004 1,2-Dibromoethane (EDB) ND<0.20 50 0.004

Dibromomethane ND<0.25 50 0.005 1,2-Dichlorobenzene ND<0.25 50 0.005

1,3-Dichlorobenzene ND<0.25 50 0.005 1,4-Dichlorobenzene ND<0.25 50 0.005

Dichlorodifluoromethane ND<0.25 50 0.005 1,1-Dichloroethane ND<0.25 50 0.005

1,2-Dichloroethane (1,2-DCA) ND<0.20 50 0.004 1,1-Dichloroethene ND<0.25 50 0.005

cis-1,2-Dichloroethene ND<0.25 50 0.005 trans-1,2-Dichloroethene ND<0.25 50 0.005

1,2-Dichloropropane ND<0.25 50 0.005 1,3-Dichloropropane ND<0.25 50 0.005

2,2-Dichloropropane ND<0.25 50 0.005 1,1-Dichloropropene ND<0.25 50 0.005

cis-1,3-Dichloropropene ND<0.25 50 0.005 trans-1,3-Dichloropropene ND<0.25 50 0.005

Diisopropyl ether (DIPE) ND<0.25 50 0.005 Ethylbenzene ND<0.25 50 0.005

Ethyl tert-butyl ether (ETBE) ND<0.25 50 0.005 Freon 113 ND<5.0 50 0.1

Hexachlorobutadiene ND<0.25 50 0.005 Hexachloroethane ND<0.25 50 0.005

2-Hexanone ND<0.25 50 0.005 Isopropylbenzene ND<0.25 50 0.005

4-Isopropyl toluene ND<0.25 50 0.005 Methyl-t-butyl ether (MTBE) ND<0.25 50 0.005

Methylene chloride ND<0.25 50 0.005 4-Methyl-2-pentanone (MIBK) ND<0.25 50 0.005

Naphthalene 7.5 50 0.005 n-Propyl benzene ND<0.25 50 0.005

Styrene ND<0.25 50 0.005 1,1,1,2-Tetrachloroethane ND<0.25 50 0.005

1,1,2,2-Tetrachloroethane ND<0.25 50 0.005 Tetrachloroethene ND<0.25 50 0.005

Toluene ND<0.25 50 0.005 1,2,3-Trichlorobenzene ND<0.25 50 0.005

1,2,4-Trichlorobenzene ND<0.25 50 0.005 1,1,1-Trichloroethane ND<0.25 50 0.005

1,1,2-Trichloroethane ND<0.25 50 0.005 Trichloroethene ND<0.25 50 0.005

Trichlorofluoromethane ND<0.25 50 0.005 1,2,3-Trichloropropane ND<0.25 50 0.005

1,2,4-Trimethylbenzene ND<0.25 50 0.005 1,3,5-Trimethylbenzene ND<0.25 50 0.005

Vinyl Chloride ND<0.25 50 0.005 Xylenes, Total ND<0.25 50 0.005

%SS1: 116 %SS2: 110

%SS3: 100

* water and vapor samples are reported in µg/L, soil/sludge/solid samples in mg/kg, product/oil/non-aqueous liquid samples and all TCLP & SPLP extracts are

reported in mg/L, wipe samples in µg/wipe.

ND means not detected above the reporting limit/method detection limit; N/A means analyte not applicable to this analysis; %SS = Percent Recovery of Surrogate

Standard; DF = Dilution Factor

# surrogate diluted out of range or coelutes with another peak; &) low surrogate due to matrix interference.

Comments:

DHS ELAP Certification 1644 Angela Rydelius, Lab ManagerPage 8 of 22

Page 21: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

B1-1

Client Project ID: #91-02522-C;

Berkeley Transfer Station

Geosphere Consultants

Extraction Method: Analytical Method:

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Lab ID

Client ID

Matrix Soil

1110650-001A

Compound Concentration * Compound Concentration *Reporting

LimitDFReporting

LimitDF

Semi-Volatile Organics by GC/MS (Basic Target List)*

SW8270CSW3550B Work Order: 1110650

Date Sampled: 10/21/11

Date Received: 10/21/11

Date Extracted: 10/21/11

Date Analyzed: 10/28/11

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

Surrogate Recoveries (%)

Acenaphthene ND<6.6 20 0.33 Acenaphthylene ND<6.6 20 0.33

Acetochlor ND<6.6 20 0.33 Anthracene ND<6.6 20 0.33

Benzidine ND<32 20 1.6 Benzoic Acid ND<32 20 1.6

Benzo (a) anthracene ND<6.6 20 0.33 Benzo (b) fluoranthene ND<6.6 20 0.33

Benzo (k) fluoranthene ND<6.6 20 0.33 Benzo (g,h,i) perylene ND<6.6 20 0.33

Benzo (a) pyrene ND<6.6 20 0.33 Benzyl Alcohol ND<32 20 1.6

1,1-Biphenyl ND<6.6 20 0.33 Bis (2-chloroethoxy) Methane ND<6.6 20 0.33

Bis (2-chloroethyl) Ether ND<6.6 20 0.33 Bis (2-chloroisopropyl) Ether ND<6.6 20 0.33

Bis (2-ethylhexyl) Phthalate ND<6.6 20 0.33 4-Bromophenyl Phenyl Ether ND<6.6 20 0.33

Butylbenzyl Phthalate ND<6.6 20 0.33 4-Chloroaniline ND<13 20 0.66

4-Chloro-3-methylphenol ND<6.6 20 0.33 2-Chloronaphthalene ND<6.6 20 0.33

2-Chlorophenol ND<6.6 20 0.33 4-Chlorophenyl Phenyl Ether ND<6.6 20 0.33

Chrysene ND<6.6 20 0.33 Dibenzo (a,h) anthracene ND<6.6 20 0.33

Dibenzofuran ND<6.6 20 0.33 Di-n-butyl Phthalate ND<6.6 20 0.33

1,2-Dichlorobenzene ND<6.6 20 0.33 1,3-Dichlorobenzene ND<6.6 20 0.33

1,4-Dichlorobenzene ND<6.6 20 0.33 3,3-Dichlorobenzidine ND<13 20 0.66

2,4-Dichlorophenol ND<6.6 20 0.33 Diethyl Phthalate ND<6.6 20 0.33

2,4-Dimethylphenol ND<6.6 20 0.33 Dimethyl Phthalate ND<6.6 20 0.33

4,6-Dinitro-2-methylphenol ND<32 20 1.6 2,4-Dinitrophenol ND<32 20 1.6

2,4-Dinitrotoluene ND<6.6 20 0.33 2,6-Dinitrotoluene ND<6.6 20 0.33

Di-n-octyl Phthalate ND<6.6 20 0.33 1,2-Diphenylhydrazine ND<6.6 20 0.33

Fluoranthene ND<6.6 20 0.33 Fluorene ND<6.6 20 0.33

Hexachlorobenzene ND<6.6 20 0.33 Hexachlorobutadiene ND<6.6 20 0.33

Hexachlorocyclopentadiene ND<32 20 1.6 Hexachloroethane ND<6.6 20 0.33

Indeno (1,2,3-cd) pyrene ND<6.6 20 0.33 Isophorone ND<6.6 20 0.33

2-Methylnaphthalene ND<6.6 20 0.33 2-Methylphenol (o-Cresol) ND<6.6 20 0.33

3 &/or 4-Methylphenol (m,p-Cresol) ND<6.6 20 0.33 Naphthalene ND<6.6 20 0.33

2-Nitroaniline ND<32 20 1.6 3-Nitroaniline ND<32 20 1.6

4-Nitroaniline ND<32 20 1.6 Nitrobenzene ND<6.6 20 0.33

2-Nitrophenol ND<32 20 1.6 4-Nitrophenol ND<32 20 1.6

N-Nitrosodiphenylamine ND<6.6 20 0.33 N-Nitrosodi-n-propylamine ND<6.6 20 0.33

Pentachlorophenol ND<32 20 1.6 Phenanthrene ND<6.6 20 0.33

Phenol ND<6.6 20 0.33 Pyrene ND<6.6 20 0.33

1,2,4-Trichlorobenzene ND<6.6 20 0.33 2,4,5-Trichlorophenol ND<6.6 20 0.33

2,4,6-Trichlorophenol ND<6.6 20 0.33

%SS1: 52 %SS2: ---#

%SS3: 62 %SS4: 78

%SS5: ---# %SS6: 84

* water samples in µg/L, soil/sludge/solid samples in mg/kg, wipe samples in µg/wipe, product/oil/non-aqueous liquid samples and all TCLP & SPLP

extracts are reported in mg/L.

ND means not detected at or above the reporting limit/method detection limit; N/A means analyte not applicable to this analysis; %SS = Percent

Recovery of Surrogate Standard; DF = Dilution Factor

#) surrogate diluted out of range or surrogate coelutes with another peak.

a3) sample diluted due to high organic content.

Comments: a3

DHS ELAP Certification 1644 Angela Rydelius, Lab ManagerPage 9 of 22

Page 22: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

B2-1

Client Project ID: #91-02522-C;

Berkeley Transfer Station

Geosphere Consultants

Extraction Method: Analytical Method:

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Lab ID

Client ID

Matrix Soil

1110650-002A

Compound Concentration * Compound Concentration *Reporting

LimitDFReporting

LimitDF

Semi-Volatile Organics by GC/MS (Basic Target List)*

SW8270CSW3550B Work Order: 1110650

Date Sampled: 10/21/11

Date Received: 10/21/11

Date Extracted: 10/21/11

Date Analyzed: 10/28/11

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

Surrogate Recoveries (%)

Acenaphthene ND<16 50 0.33 Acenaphthylene ND<16 50 0.33

Acetochlor ND<16 50 0.33 Anthracene ND<16 50 0.33

Benzidine ND<80 50 1.6 Benzoic Acid ND<80 50 1.6

Benzo (a) anthracene ND<16 50 0.33 Benzo (b) fluoranthene ND<16 50 0.33

Benzo (k) fluoranthene ND<16 50 0.33 Benzo (g,h,i) perylene ND<16 50 0.33

Benzo (a) pyrene ND<16 50 0.33 Benzyl Alcohol ND<80 50 1.6

1,1-Biphenyl ND<16 50 0.33 Bis (2-chloroethoxy) Methane ND<16 50 0.33

Bis (2-chloroethyl) Ether ND<16 50 0.33 Bis (2-chloroisopropyl) Ether ND<16 50 0.33

Bis (2-ethylhexyl) Phthalate ND<16 50 0.33 4-Bromophenyl Phenyl Ether ND<16 50 0.33

Butylbenzyl Phthalate ND<16 50 0.33 4-Chloroaniline ND<33 50 0.66

4-Chloro-3-methylphenol ND<16 50 0.33 2-Chloronaphthalene ND<16 50 0.33

2-Chlorophenol ND<16 50 0.33 4-Chlorophenyl Phenyl Ether ND<16 50 0.33

Chrysene ND<16 50 0.33 Dibenzo (a,h) anthracene ND<16 50 0.33

Dibenzofuran ND<16 50 0.33 Di-n-butyl Phthalate ND<16 50 0.33

1,2-Dichlorobenzene ND<16 50 0.33 1,3-Dichlorobenzene ND<16 50 0.33

1,4-Dichlorobenzene ND<16 50 0.33 3,3-Dichlorobenzidine ND<33 50 0.66

2,4-Dichlorophenol ND<16 50 0.33 Diethyl Phthalate ND<16 50 0.33

2,4-Dimethylphenol ND<16 50 0.33 Dimethyl Phthalate ND<16 50 0.33

4,6-Dinitro-2-methylphenol ND<80 50 1.6 2,4-Dinitrophenol ND<80 50 1.6

2,4-Dinitrotoluene ND<16 50 0.33 2,6-Dinitrotoluene ND<16 50 0.33

Di-n-octyl Phthalate ND<16 50 0.33 1,2-Diphenylhydrazine ND<16 50 0.33

Fluoranthene ND<16 50 0.33 Fluorene ND<16 50 0.33

Hexachlorobenzene ND<16 50 0.33 Hexachlorobutadiene ND<16 50 0.33

Hexachlorocyclopentadiene ND<80 50 1.6 Hexachloroethane ND<16 50 0.33

Indeno (1,2,3-cd) pyrene ND<16 50 0.33 Isophorone ND<16 50 0.33

2-Methylnaphthalene ND<16 50 0.33 2-Methylphenol (o-Cresol) ND<16 50 0.33

3 &/or 4-Methylphenol (m,p-Cresol) ND<16 50 0.33 Naphthalene ND<16 50 0.33

2-Nitroaniline ND<80 50 1.6 3-Nitroaniline ND<80 50 1.6

4-Nitroaniline ND<80 50 1.6 Nitrobenzene ND<16 50 0.33

2-Nitrophenol ND<80 50 1.6 4-Nitrophenol ND<80 50 1.6

N-Nitrosodiphenylamine ND<16 50 0.33 N-Nitrosodi-n-propylamine ND<16 50 0.33

Pentachlorophenol ND<80 50 1.6 Phenanthrene ND<16 50 0.33

Phenol ND<16 50 0.33 Pyrene ND<16 50 0.33

1,2,4-Trichlorobenzene ND<16 50 0.33 2,4,5-Trichlorophenol ND<16 50 0.33

2,4,6-Trichlorophenol ND<16 50 0.33

%SS1: ---# %SS2: ---#

%SS3: ---# %SS4: ---#

%SS5: ---# %SS6: ---#

* water samples in µg/L, soil/sludge/solid samples in mg/kg, wipe samples in µg/wipe, product/oil/non-aqueous liquid samples and all TCLP & SPLP

extracts are reported in mg/L.

ND means not detected at or above the reporting limit/method detection limit; N/A means analyte not applicable to this analysis; %SS = Percent

Recovery of Surrogate Standard; DF = Dilution Factor

#) surrogate diluted out of range or surrogate coelutes with another peak.

a3) sample diluted due to high organic content.

Comments: a3

DHS ELAP Certification 1644 Angela Rydelius, Lab ManagerPage 10 of 22

Page 23: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

B3-1

Client Project ID: #91-02522-C;

Berkeley Transfer Station

Geosphere Consultants

Extraction Method: Analytical Method:

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Lab ID

Client ID

Matrix Soil

1110650-003A

Compound Concentration * Compound Concentration *Reporting

LimitDFReporting

LimitDF

Semi-Volatile Organics by GC/MS (Basic Target List)*

SW8270CSW3550B Work Order: 1110650

Date Sampled: 10/21/11

Date Received: 10/21/11

Date Extracted: 10/21/11

Date Analyzed: 10/28/11

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

Surrogate Recoveries (%)

Acenaphthene ND<16 50 0.33 Acenaphthylene ND<16 50 0.33

Acetochlor ND<16 50 0.33 Anthracene ND<16 50 0.33

Benzidine ND<80 50 1.6 Benzoic Acid ND<80 50 1.6

Benzo (a) anthracene ND<16 50 0.33 Benzo (b) fluoranthene ND<16 50 0.33

Benzo (k) fluoranthene ND<16 50 0.33 Benzo (g,h,i) perylene ND<16 50 0.33

Benzo (a) pyrene ND<16 50 0.33 Benzyl Alcohol ND<80 50 1.6

1,1-Biphenyl ND<16 50 0.33 Bis (2-chloroethoxy) Methane ND<16 50 0.33

Bis (2-chloroethyl) Ether ND<16 50 0.33 Bis (2-chloroisopropyl) Ether ND<16 50 0.33

Bis (2-ethylhexyl) Phthalate ND<16 50 0.33 4-Bromophenyl Phenyl Ether ND<16 50 0.33

Butylbenzyl Phthalate ND<16 50 0.33 4-Chloroaniline ND<33 50 0.66

4-Chloro-3-methylphenol ND<16 50 0.33 2-Chloronaphthalene ND<16 50 0.33

2-Chlorophenol ND<16 50 0.33 4-Chlorophenyl Phenyl Ether ND<16 50 0.33

Chrysene ND<16 50 0.33 Dibenzo (a,h) anthracene ND<16 50 0.33

Dibenzofuran ND<16 50 0.33 Di-n-butyl Phthalate ND<16 50 0.33

1,2-Dichlorobenzene ND<16 50 0.33 1,3-Dichlorobenzene ND<16 50 0.33

1,4-Dichlorobenzene ND<16 50 0.33 3,3-Dichlorobenzidine ND<33 50 0.66

2,4-Dichlorophenol ND<16 50 0.33 Diethyl Phthalate ND<16 50 0.33

2,4-Dimethylphenol ND<16 50 0.33 Dimethyl Phthalate ND<16 50 0.33

4,6-Dinitro-2-methylphenol ND<80 50 1.6 2,4-Dinitrophenol ND<80 50 1.6

2,4-Dinitrotoluene ND<16 50 0.33 2,6-Dinitrotoluene ND<16 50 0.33

Di-n-octyl Phthalate ND<16 50 0.33 1,2-Diphenylhydrazine ND<16 50 0.33

Fluoranthene ND<16 50 0.33 Fluorene ND<16 50 0.33

Hexachlorobenzene ND<16 50 0.33 Hexachlorobutadiene ND<16 50 0.33

Hexachlorocyclopentadiene ND<80 50 1.6 Hexachloroethane ND<16 50 0.33

Indeno (1,2,3-cd) pyrene ND<16 50 0.33 Isophorone ND<16 50 0.33

2-Methylnaphthalene ND<16 50 0.33 2-Methylphenol (o-Cresol) ND<16 50 0.33

3 &/or 4-Methylphenol (m,p-Cresol) ND<16 50 0.33 Naphthalene 17 50 0.33

2-Nitroaniline ND<80 50 1.6 3-Nitroaniline ND<80 50 1.6

4-Nitroaniline ND<80 50 1.6 Nitrobenzene ND<16 50 0.33

2-Nitrophenol ND<80 50 1.6 4-Nitrophenol ND<80 50 1.6

N-Nitrosodiphenylamine ND<16 50 0.33 N-Nitrosodi-n-propylamine ND<16 50 0.33

Pentachlorophenol ND<80 50 1.6 Phenanthrene ND<16 50 0.33

Phenol ND<16 50 0.33 Pyrene ND<16 50 0.33

1,2,4-Trichlorobenzene ND<16 50 0.33 2,4,5-Trichlorophenol ND<16 50 0.33

2,4,6-Trichlorophenol ND<16 50 0.33

%SS1: ---# %SS2: ---#

%SS3: ---# %SS4: ---#

%SS5: ---# %SS6: ---#

* water samples in µg/L, soil/sludge/solid samples in mg/kg, wipe samples in µg/wipe, product/oil/non-aqueous liquid samples and all TCLP & SPLP

extracts are reported in mg/L.

ND means not detected at or above the reporting limit/method detection limit; N/A means analyte not applicable to this analysis; %SS = Percent

Recovery of Surrogate Standard; DF = Dilution Factor

#) surrogate diluted out of range or surrogate coelutes with another peak.

a3) sample diluted due to high organic content.

Comments:

DHS ELAP Certification 1644 Angela Rydelius, Lab ManagerPage 11 of 22

Page 24: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

Client Project ID: #91-02522-C;

Berkeley Transfer Station

Geosphere Consultants

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Date Sampled: 10/21/11

Date Received 10/21/11

Date Extracted 10/21/11

Date Analyzed 10/25/11-10/26/11

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

1110650-001A 1110650-002A 1110650-003A

B1-1 B2-1 B3-1

Lab ID

Client ID

S S S

TOTAL TOTAL TOTAL

Matrix

Extraction Type

Reporting Limit for DF =1;

ND means not detected

above the reporting limit

S W

mg/Kg mg/L

1 11 1 1

Extraction Method:Analytical Method: SW6020 SW3050B Work Order: 1110650

Dilution Factor

ICP Metals, Concentration*

CAM / CCR 17 Metals*

Antimony 2.6 0.97 1.5 0.5 NA

Arsenic 12 8.6 9.1 0.5 NA

Barium 260 200 190 5.0 NA

Beryllium ND ND ND 0.5 NA

Cadmium ND ND 0.64 0.25 NA

Chromium 54 57 61 0.5 NA

Cobalt 9.0 13 9.1 0.5 NA

Copper 160 28 95 0.5 NA

Lead 350 39 82 0.5 NA

Mercury 31 0.39 1.9 0.05 NA

Molybdenum 1.4 ND 0.59 0.5 NA

Nickel 64 66 75 0.5 NA

Selenium ND ND ND 0.5 NA

Silver 0.63 ND ND 0.5 NA

Thallium ND ND ND 0.5 NA

Vanadium 100 47 46 0.5 NA

Zinc 450 85 140 5.0 NA

%SS: 103 108 103

Comments

*water samples are reported in µg/L, product/oil/non-aqueous liquid samples and all TCLP / STLC / DISTLC / SPLP extracts are reported in mg/L,

soil/sludge/solid samples in mg/kg, wipe samples in µg/wipe, filter samples in µg/filter.

# means surrogate diluted out of range; ND means not detected above the reporting limit/method detection limit; N/A means not applicable to this sample

or instrument.

TOTAL = Hot acid digestion of a representative sample aliquot.

TRM = Total recoverable metals is the "direct analysis" of a sample aliquot taken from its acid-preserved container.

DISS = Dissolved metals by direct analysis of 0.45 µm filtered and acidified sample.

%SS = Percent Recovery of Surrogate Standard

DF = Dilution Factor

DHS ELAP Certification 1644 Angela Rydelius, Lab Manager

Page 12 of 22

Page 25: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

Lab ID TPH(g) MTBE Benzene TolueneClient ID Ethylbenzene XylenesMatrix DF % SS

Gasoline Range (C6-C12) Volatile Hydrocarbons as Gasoline with BTEX and MTBE*

Client Project ID: #91-02522-C;

Berkeley Transfer Station

Geosphere Consultants

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Date Sampled: 10/21/11

Date Received: 10/21/11

Date Extracted: 10/21/11

Date Analyzed: 10/23/11-10/25/11

Work Order: 1110650Extraction method: SW5030B Analytical methods: SW8021B/8015Bm

Comments

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

NDB1-1 ND ND ND001A S ND ND 1 95

NDB2-1 2.1 ND 0.0078002A S 0.0059 0.042 1 121 d7

NDB3-1 4.2 ND 0.0099003A S 0.020 0.059 1 116 d7

DHS ELAP Certification 1644 Angela Rydelius, Lab Manager

Reporting Limit for DF =1;

ND means not detected at or

above the reporting limit

W

S

50 5.0 0.5 0.5 0.5 0.5

1.0 0.05 0.005 0.005 0.005 0.005

ug/L

mg/Kg

* water and vapor samples are reported in µg/L, soil/sludge/solid samples in mg/kg, wipe samples in µg/wipe, product/oil/non-aqueous liquid samples and all TCLP &

SPLP extracts in mg/L.

# cluttered chromatogram; sample peak coelutes w/surrogate peak; low surrogate recovery due to matrix interference; %SS = Percent Recovery of Surrogate Standard;

DF = Dilution Factor

The following descriptions of the TPH chromatogram are cursory in nature and McCampbell Analytical is not responsible for their interpretation:

d7) strongly aged gasoline or diesel range compounds are significant in the TPH(g) chromatogram

Page 13 of 22

Page 26: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

Lab ID ArsenicClient ID Matrix DF % SS

Metals*

Client Project ID: #91-02522-C;

Berkeley Transfer Station

Geosphere Consultants

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Date Sampled: 10/21/11

Date Received: 10/21/11

Date Extracted: 10/22/11-10/24/11

Date Analyzed: 10/25/11-10/26/11

Work Order: 1110650Extraction method: CA Title 22 Analytical methods: SW6020

Extraction Type Chromium Lead Comments

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

B1-1 0.31001A S 1 N/AWET 0.45 28

B2-1 0.27002A S 1 N/AWET 0.33 1.2

B3-1 0.30003A S 1 N/AWET 0.86 ND

DHS ELAP Certification 1644 Angela Rydelius, Lab Manager

Reporting Limit for DF =1;

ND means not detected at or

above the reporting limit

W

S

NA

0.1

NA

mg/L

*water samples are reported in µg/L, product/oil/non-aqueous liquid samples and all TCLP / STLC / DISTLC / SPLP extracts are reported in mg/L, soil/sludge/solid

samples in mg/kg, wipe samples in µg/wipe, filter samples in µg/filter.

# means surrogate diluted out of range; ND means not detected above the reporting limit/method detection limit; N/A means not applicable to this sample or instrument.

WET = Waste Extraction Test, i.e., STLC (Soluble Threshold Limit Concentration).

DI WET = Waste Extraction Test using DI water (DI STLC).

%SS = Percent Recovery of Surrogate Standard

DF = Dilution Factor

TOTAL

WET

NA

0.1

NA

0.1

Page 14 of 22

Page 27: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

Client Project ID: #91-02522-C;

Berkeley Transfer Station

Geosphere Consultants

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Date Sampled: 10/21/11

Date Received: 10/21/11

Date Extracted: 10/21/11

Date Analyzed: 10/28/11

Work Order: 1110650

Total Extractable Petroleum Hydrocarbons*

Extraction method: SW3550B Analytical methods: SW8015B

Lab IDTPH-Diesel TPH-Motor Oil

Client ID Matrix DF % SS(C10-C23) (C18-C36)

Comments

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

B1-1 120 3401110650-001A S 20 111 e7,e2

B2-1 130 8101110650-002A S 100 103 e7,e2

B3-1 140 3401110650-003A S 20 109 e7,e2,e6

DHS ELAP Certification 1644 Angela Rydelius, Lab Manager

Reporting Limit for DF =1;

ND means not detected at or

above the reporting limit

W

S

NA NA

1.0 5.0

ug/L

mg/Kg

* water samples are reported in µg/L, wipe samples in µg/wipe, soil/solid/sludge samples in mg/kg, product/oil/non-aqueous liquid samples in mg/L, and all DISTLC

/ STLC / SPLP / TCLP extracts are reported in µg/L.

# cluttered chromatogram resulting in coeluted surrogate and sample peaks, or; surrogate peak is on elevated baseline, or; surrogate has been diminished by dilution

of original extract; %SS = Percent Recovery of Surrogate Standard; DF = Dilution Factor

The following descriptions of the TPH chromatogram are cursory in nature and McCampbell Analytical is not responsible for their interpretation:

e2) diesel range compounds are significant; no recognizable pattern

e6) one to a few isolated peaks present in the THP(d/mo) chromatogram

e7) oil range compounds are significant

Page 15 of 22

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QC SUMMARY REPORT FOR SW6020

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

EPA Method: SW6020 Extraction: CA Title 22 Spiked Sample ID: N/A

Sample Spiked MS

% Rec. % Rec. % Rec. % Rec.

MSD LCS LCSDMS-MSD

% RPD

LCS-LCSD

% RPD

WorkOrder: 1110650W.O. Sample Matrix: Soil BatchID: 62048

MS / MSD

Acceptance Criteria (%)

LCS/LCSD

Analyte

QC Matrix: Soil

RPD RPDmg/L mg/L

Arsenic N/A 10 N/A N/A N/A 97.7 96.4 1.40 N/A 75 - 125N/A 20

Chromium N/A 10 N/A N/A N/A 95.1 95.3 0.168 N/A 75 - 125N/A 20

Lead N/A 10 N/A N/A N/A 97.7 97.7 0 N/A 75 - 125N/A 20

All target compounds in the Method Blank of this extraction batch were ND less than the method RL with the following exceptions:

NONE

Lab ID Date Sampled Date Extracted Lab ID Date Sampled Date ExtractedDate Analyzed Date Analyzed

BATCH 62048 SUMMARY

1110650-001A 10/22/11 10/25/11 6:55 AM10/21/11 7:30 AM 1110650-001A 10/22/11 10/26/11 2:47 AM10/21/11 7:30 AM

1110650-002A 10/22/11 10/25/11 7:01 AM10/21/11 8:10 AM 1110650-003A 10/22/11 10/25/11 7:07 AM10/21/11 9:10 AM

MS = Matrix Spike; MSD = Matrix Spike Duplicate; LCS = Laboratory Control Sample; LCSD = Laboratory Control Sample Duplicate; RPD = Relative Percent Deviation.

% Recovery = 100 * (MS-Sample) / (Amount Spiked); RPD = 100 * (MS - MSD) / ((MS + MSD) / 2).

MS / MSD spike recoveries and / or %RPD may fall outside of laboratory acceptance criteria due to one or more of the following reasons: a) the sample is inhomogenous AND contains significant concentrations of analyte relative to the amount spiked, or b) the spiked sample's matrix interferes with the spike recovery.

N/A = not applicable to this method.

NR = analyte concentration in sample exceeds spike amount for soil matrix or exceeds 2x spike amount for water matrix or sample diluted due to high matrix or analyte content.

DHS ELAP Certification 1644 QA/QC Officer

Page 16 of 22

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QC SUMMARY REPORT FOR SW8021B/8015Bm

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

EPA Method: SW8021B/8015Bm Extraction: SW5030B Spiked Sample ID: 1110631-008A

Sample Spiked MS

% Rec. % Rec. % Rec. % Rec.

MSD LCS LCSDMS-MSD

% RPD

LCS-LCSD

% RPD

WorkOrder: 1110650W.O. Sample Matrix: Soil BatchID: 62097

MS / MSD

Acceptance Criteria (%)

LCS/LCSD

Analyte

QC Matrix: Soil

RPD RPDmg/Kg mg/Kg

TPH(btex) ND 0.60 110 99.4 10.6 100 97 3.49 70 - 130 70 - 130£ 20 20

MTBE ND 0.10 113 114 1.16 114 118 3.60 70 - 130 70 - 13020 20

Benzene ND 0.10 108 108 0 108 110 1.90 70 - 130 70 - 13020 20

Toluene ND 0.10 96.3 93.8 2.66 96 97.7 1.75 70 - 130 70 - 13020 20

Ethylbenzene ND 0.10 97.6 96 1.65 98.5 99.3 0.892 70 - 130 70 - 13020 20

Xylenes ND 0.30 110 109 1.43 111 112 0.870 70 - 130 70 - 13020 20

%SS: 101 0.10 86 86 0 100 92 7.57 70 - 130 70 - 13020 20

All target compounds in the Method Blank of this extraction batch were ND less than the method RL with the following exceptions:

NONE

Lab ID Date Sampled Date Extracted Lab ID Date Sampled Date ExtractedDate Analyzed Date Analyzed

BATCH 62097 SUMMARY

1110650-001A 10/21/11 10/25/11 9:23 PM10/21/11 7:30 AM 1110650-002A 10/21/11 10/23/11 12:30 AM10/21/11 8:10 AM

1110650-003A 10/21/11 10/23/1110/21/11 9:10 AM

MS = Matrix Spike; MSD = Matrix Spike Duplicate; LCS = Laboratory Control Sample; LCSD = Laboratory Control Sample Duplicate; RPD = Relative Percent Deviation.

% Recovery = 100 * (MS-Sample) / (Amount Spiked); RPD = 100 * (MS - MSD) / ((MS + MSD) / 2).

MS / MSD spike recoveries and / or %RPD may fall outside of laboratory acceptance criteria due to one or more of the following reasons: a) the sample is inhomogenous AND contains significant concentrations of analyte relative to the amount spiked, or b) the spiked sample's matrix interferes with the spike recovery.

£ TPH(btex) = sum of BTEX areas from the FID.

# cluttered chromatogram; sample peak coelutes with surrogate peak.

N/A = not enough sample to perform matrix spike and matrix spike duplicate.

NR = matrix interference and/or analyte concentration in sample exceeds spike amount for soil matrix or exceeds 2x spike amount for water matrix or sample diluted due to high matrix or analyte content.

DHS ELAP Certification 1644 QA/QC Officer

Page 17 of 22

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QC SUMMARY REPORT FOR SW8081A/8082

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

EPA Method: SW8081A/8082 Extraction: SW3550B Spiked Sample ID: 1110650-003A

Sample Spiked MS

% Rec. % Rec. % Rec. % Rec.

MSD LCS LCSDMS-MSD

% RPD

LCS-LCSD

% RPD

WorkOrder: 1110650W.O. Sample Matrix: Soil BatchID: 62107

MS / MSD

Acceptance Criteria (%)

LCS/LCSD

Analyte

QC Matrix: Soil

RPD RPDmg/kg mg/kg

Aldrin ND<0.50 0.020 NR NR NR 125 125 0 70 - 130 70 - 13030 30

g-BHC ND<0.50 0.020 NR NR NR 88.5 87.8 0.871 70 - 130 70 - 13030 30

p,p-DDT ND<0.50 0.050 NR NR NR 88.3 86.6 1.89 70 - 130 70 - 13030 30

Dieldrin ND<0.50 0.050 NR NR NR 109 107 1.91 70 - 130 70 - 13030 30

Endrin ND<0.50 0.050 NR NR NR 130 127 2.02 70 - 130 70 - 13030 30

Heptachlor ND<0.50 0.020 NR NR NR 107 106 1.26 70 - 130 70 - 13030 30

%SS: 108 0.050 ---# ---# ---# 90 88 2.55 70 - 130 70 - 13030 30

All target compounds in the Method Blank of this extraction batch were ND less than the method RL with the following exceptions:

NONE

Lab ID Date Sampled Date Extracted Lab ID Date Sampled Date ExtractedDate Analyzed Date Analyzed

BATCH 62107 SUMMARY

1110650-001A 10/21/11 10/22/11 5:06 AM10/21/11 7:30 AM 1110650-002A 10/21/11 10/22/11 6:02 AM10/21/11 8:10 AM

1110650-003A 10/21/11 10/22/11 6:58 AM10/21/11 9:10 AM

MS = Matrix Spike; MSD = Matrix Spike Duplicate; LCS = Laboratory Control Sample; LCSD = Laboratory Control Sample Duplicate; RPD = Relative Percent Deviation.

% Recovery = 100 * (MS-Sample) / (Amount Spiked); RPD = 100 * (MS - MSD) / ((MS + MSD) / 2).

MS / MSD spike recoveries and / or %RPD may fall outside of laboratory acceptance criteria due to one or more of the following reasons: a) the sample is inhomogenous AND contains significant concentrations of analyte relative to the amount spiked, or b) the spiked sample's matrix interferes with the spike recovery.

N/A = not enough sample to perform matrix spike and matrix spike duplicate.

NR = analyte concentration in sample exceeds spike amount for soil matrix or exceeds 2x spike amount for water matrix or sample diluted due to high matrix or analyte content.

DHS ELAP Certification 1644 QA/QC Officer

Page 18 of 22

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QC SUMMARY REPORT FOR SW8260B

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

EPA Method: SW8260B Extraction: SW5030B Spiked Sample ID: 1110275-025A

Sample Spiked MS

% Rec. % Rec. % Rec. % Rec.

MSD LCS LCSDMS-MSD

% RPD

LCS-LCSD

% RPD

WorkOrder: 1110650W.O. Sample Matrix: Soil BatchID: 62025

MS / MSD

Acceptance Criteria (%)

LCS/LCSD

Analyte

QC Matrix: Soil

RPD RPDmg/Kg mg/Kg

tert-Amyl methyl ether (TAME) ND 0.050 75.4 73.9 2.02 74.9 74.8 0.0649 70 - 130 70 - 13030 30

Benzene ND 0.050 105 103 2.04 102 102 0 70 - 130 70 - 13030 30

t-Butyl alcohol (TBA) ND 0.25 90.1 95.7 5.99 96.9 94.4 2.68 70 - 130 70 - 13030 30

Chlorobenzene ND 0.050 110 109 0.653 106 108 1.07 70 - 130 70 - 13030 30

1,2-Dibromoethane (EDB) ND 0.050 98.9 98.3 0.602 97.8 100 2.41 70 - 130 70 - 13030 30

1,2-Dichloroethane (1,2-DCA) ND 0.050 99 95.9 3.24 95.1 96.4 1.38 70 - 130 70 - 13030 30

1,1-Dichloroethene ND 0.050 106 102 3.75 101 102 0.881 70 - 130 70 - 13030 30

Diisopropyl ether (DIPE) ND 0.050 93.6 91.7 2.13 92.2 91.5 0.773 70 - 130 70 - 13030 30

Ethyl tert-butyl ether (ETBE) ND 0.050 86.8 84.7 2.40 85.2 85.5 0.306 70 - 130 70 - 13030 30

Methyl-t-butyl ether (MTBE) ND 0.050 89.9 86.9 3.44 89.5 89.3 0.200 70 - 130 70 - 13030 30

Toluene ND 0.050 117 117 0 114 115 0.677 70 - 130 70 - 13030 30

Trichloroethene ND 0.050 103 101 1.95 99.7 101 1.55 70 - 130 70 - 13030 30

%SS1: 91 0.12 100 98 1.73 100 100 0 70 - 130 70 - 13030 30

%SS2: 101 0.12 116 120 3.22 120 120 0 70 - 130 70 - 13030 30

%SS3: 77 0.012 104 103 1.15 102 104 2.69 70 - 130 70 - 13030 30

All target compounds in the Method Blank of this extraction batch were ND less than the method RL with the following exceptions:

NONE

Lab ID Date Sampled Date Extracted Lab ID Date Sampled Date ExtractedDate Analyzed Date Analyzed

BATCH 62025 SUMMARY

1110650-001A 10/21/11 10/26/11 1:54 PM10/21/11 7:30 AM 1110650-002A 10/21/11 10/24/11 5:49 PM10/21/11 8:10 AM

1110650-003A 10/21/11 10/26/11 5:41 PM10/21/11 9:10 AM

MS = Matrix Spike; MSD = Matrix Spike Duplicate; LCS = Laboratory Control Sample; LCSD = Laboratory Control Sample Duplicate; RPD = Relative Percent Deviation.

% Recovery = 100 * (MS-Sample) / (Amount Spiked); RPD = 100 * (MS - MSD) / ((MS + MSD) / 2).

MS / MSD spike recoveries and / or %RPD may fall outside of laboratory acceptance criteria due to one or more of the following reasons: a) the sample is inhomogenous AND contains significant concentrations of analyte relative to the amount spiked, or b) the spiked sample's matrix interferes with the spike recovery.

N/A = not enough sample to perform matrix spike and matrix spike duplicate.

NR = analyte concentration in sample exceeds spike amount for soil matrix or exceeds 2x spike amount for water matrix or sample diluted due to high matrix or analyte content.

Laboratory extraction solvents such as methylene chloride and acetone may occasionally appear in the method blank at low levels.

DHS ELAP Certification 1644 QA/QC Officer

Page 19 of 22

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QC SUMMARY REPORT FOR SW8270C

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

EPA Method: SW8270C Extraction: SW3550B Spiked Sample ID: 1110648-001A

Sample Spiked MS

% Rec. % Rec. % Rec. % Rec.

MSD LCS LCSDMS-MSD

% RPD

LCS-LCSD

% RPD

WorkOrder: 1110650W.O. Sample Matrix: Soil BatchID: 62105

MS / MSD

Acceptance Criteria (%)

LCS/LCSD

Analyte

QC Matrix: Soil

RPD RPDmg/Kg mg/Kg

Acenaphthene ND<0.66 2 48.2 50.2 4.07 54 53.9 0.111 30 - 130 30 - 13030 30

4-Chloro-3-methylphenol ND<0.66 4 60.5 65.7 8.29 58.2 54.7 6.12 30 - 130 30 - 13030 30

2-Chlorophenol ND<0.66 4 74.1 77.7 4.68 76.4 72.7 5.02 30 - 130 30 - 13030 30

1,4-Dichlorobenzene ND<0.66 2 65.6 68.7 4.67 66.9 65.6 1.92 30 - 130 30 - 13030 30

2,4-Dinitrotoluene ND<0.66 2 51.7 55.2 6.58 60 58.9 1.87 30 - 130 30 - 13030 30

4-Nitrophenol ND<3.2 4 57.9 61.2 5.58 44.7 42.1 6.06 30 - 130 30 - 13030 30

N-Nitrosodi-n-propylamine ND<0.66 2 99.9 100 0.300 68 66.4 2.35 30 - 130 30 - 13030 30

Pentachlorophenol ND<3.2 4 41.9 42.9 2.55 30.4 32.2 5.81 30 - 130 30 - 13030 30

Phenol ND<0.66 4 66.3 63.3 4.66 69.4 66.2 4.68 30 - 130 30 - 13030 30

Pyrene ND<0.66 2 51.9 54.6 4.96 55 54.6 0.766 30 - 130 30 - 13030 30

1,2,4-Trichlorobenzene ND<0.66 2 65.6 69.4 5.54 66.3 65.6 1.00 30 - 130 30 - 13030 30

%SS1: 102 200 83 107 25.0 86 88 2.66 30 - 130 30 - 13030 30

%SS2: 73 200 64 65 1.30 92 90 1.80 30 - 130 30 - 13030 30

%SS3: 89 200 88 93 5.50 87 89 2.15 30 - 130 30 - 13030 30

%SS4: 79 200 79 81 2.98 81 84 3.26 30 - 130 30 - 13030 30

%SS5: 107 200 115 119 3.18 80 78 3.13 30 - 130 30 - 13030 30

%SS6: 74 200 73 76 4.09 80 82 2.56 30 - 130 30 - 13030 30

All target compounds in the Method Blank of this extraction batch were ND less than the method RL with the following exceptions:

NONE

Lab ID Date Sampled Date Extracted Lab ID Date Sampled Date ExtractedDate Analyzed Date Analyzed

BATCH 62105 SUMMARY

1110650-001A 10/21/11 10/28/11 5:39 AM10/21/11 7:30 AM 1110650-002A 10/21/11 10/28/11 8:08 AM10/21/11 8:10 AM

1110650-003A 10/21/11 10/28/11 6:54 AM10/21/11 9:10 AM

MS = Matrix Spike; MSD = Matrix Spike Duplicate; LCS = Laboratory Control Sample; LCSD = Laboratory Control Sample Duplicate; RPD = Relative Percent Deviation.

% Recovery = 100 * (MS-Sample) / (Amount Spiked); RPD = 100 * (MS - MSD) / ((MS + MSD) / 2).

MS / MSD spike recoveries and / or %RPD may fall outside of laboratory acceptance criteria due to one or more of the following reasons: a) the sample is inhomogenous AND contains significant concentrations of analyte relative to the amount spiked, or b) the spiked sample's matrix interferes with the spike recovery.

N/A = not enough sample to perform matrix spike and matrix spike duplicate.

NR = matrix interference and / or analyte concentration in sample exceeds spike amount for soil matrix or exceeds 2x spike amount for water matrix, sample diluted due to high matrix or analyte content, or MS/MSD samples diluted due to high organic content.

#) surrogate diluted out of range; & = low or no recovery of surrogate or target analytes due to matrix interference.

Laboratory extraction solvents such as methylene chloride and acetone may occasionally appear in the method blank at low levels.

DHS ELAP Certification 1644 QA/QC Officer

Page 20 of 22

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QC SUMMARY REPORT FOR SW6020

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

EPA Method: SW6020 Extraction: SW3050B Spiked Sample ID: 1110601-002A

Sample Spiked MS

% Rec. % Rec. % Rec. % Rec.

MSD LCS LCSDMS-MSD

% RPD

LCS-LCSD

% RPD

WorkOrder: 1110650W.O. Sample Matrix: Soil

BatchID: 62067

MS / MSD

Acceptance Criteria (%)

LCS/LCSD

Analyte

QC Matrix: Soil

Spiked

RPDRPDmg/Kg mg/Kg mg/Kg

Antimony 1.2 50 104 98.1 6.08 81.1 89 9.26 75 - 125 75 - 12510 20 20

Arsenic 29 50 111 99.8 6.65 89.4 96.8 7.88 75 - 125 75 - 12510 20 20

Barium 230 500 115 104 6.59 81.6 89.3 9.05 75 - 125 75 - 125100 20 20

Beryllium 0.72 50 105 97.7 7.23 88.6 95.2 7.16 75 - 125 75 - 12510 20 20

Cadmium 0.48 50 110 103 6.90 83.9 92.1 9.40 75 - 125 75 - 12510 20 20

Chromium 45 50 105 92.1 6.76 83.2 90.8 8.71 75 - 125 75 - 12510 20 20

Cobalt 12 50 103 94.7 6.69 89.6 97.1 8.10 75 - 125 75 - 12510 20 20

Copper 110 50 NR NR NR 88.9 96.9 8.66 75 - 125 75 - 12510 20 20

Lead 69 50 107 94 5.52 85.3 91.7 7.23 75 - 125 75 - 12510 20 20

Mercury 0.22 1.25 92 86.2 5.39 81.5 81 0.640 75 - 125 75 - 1250.25 20 20

Molybdenum 0.65 50 106 100 6.00 80.7 87.9 8.54 75 - 125 75 - 12510 20 20

Nickel 44 50 115 103 6.30 87.1 92.5 6.00 75 - 125 75 - 12510 20 20

Selenium 0.92 50 111 104 6.46 88.8 96 7.84 75 - 125 75 - 12510 20 20

Silver 48 50 104 93.2 5.37 85.1 92.9 8.81 75 - 125 75 - 12510 20 20

Thallium ND 50 107 101 5.45 84.4 90.3 6.80 75 - 125 75 - 12510 20 20

Vanadium 76 50 NR NR NR 84.1 90.6 7.44 75 - 125 75 - 12510 20 20

Zinc 160 500 112 102 7.15 98.5 94.4 4.24 75 - 125 75 - 125100 20 20

%SS: 116 500 118 111 6.05 90 94 3.41 70 - 130 70 - 130500 20 20

All target compounds in the Method Blank of this extraction batch were ND less than the method RL with the following exceptions:

NONE

Lab ID Date Sampled Date Extracted Lab ID Date Sampled Date ExtractedDate Analyzed Date Analyzed

BATCH 62067 SUMMARY

1110650-001A 10/21/11 10/25/11 10:17 AM10/21/11 7:30 AM 1110650-001A 10/21/11 10/26/11 3:54 AM10/21/11 7:30 AM

1110650-002A 10/21/11 10/25/11 10:23 AM10/21/11 8:10 AM 1110650-002A 10/21/11 10/26/11 3:42 AM10/21/11 8:10 AM

1110650-003A 10/21/11 10/25/11 10:48 AM10/21/11 9:10 AM 1110650-003A 10/21/11 10/26/11 3:48 AM10/21/11 9:10 AM

DHS ELAP Certification 1644 QA/QC Officer

MS = Matrix Spike; MSD = Matrix Spike Duplicate; LCS = Laboratory Control Sample; LCSD = Laboratory Control Sample Duplicate; RPD = Relative Percent Deviation.

% Recovery = 100 * (MS-Sample) / (Amount Spiked); RPD = 100 * (MS - MSD) / ((MS + MSD) / 2).

MS / MSD spike recoveries and / or %RPD may fall outside of laboratory acceptance criteria due to one or more of the following reasons: a) the sample is inhomogenous AND contains significant concentrations of analyte relative to the amount spiked, or b) the spiked sample's matrix interferes with the spike recovery.

N/A = not applicable to this method.

NR = analyte concentration in sample exceeds spike amount for soil matrix or exceeds 2x spike amount for water matrix or sample diluted due to high matrix or analyte content.

Page 21 of 22

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QC SUMMARY REPORT FOR SW8015B

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

EPA Method: SW8015B Extraction: SW3550B Spiked Sample ID: 1110634-014A

Sample Spiked MS

% Rec. % Rec. % Rec. % Rec.

MSD LCS LCSDMS-MSD

% RPD

LCS-LCSD

% RPD

WorkOrder: 1110650W.O. Sample Matrix: Soil BatchID: 62099

MS / MSD

Acceptance Criteria (%)

LCS/LCSD

Analyte

QC Matrix: Soil

RPD RPDmg/Kg mg/Kg

TPH-Diesel (C10-C23) ND 40 117 117 0 116 121 3.91 70 - 130 70 - 13030 30

%SS: 95 25 96 96 0 82 90 10.1 70 - 130 70 - 13030 30

All target compounds in the Method Blank of this extraction batch were ND less than the method RL with the following exceptions:

NONE

Lab ID Date Sampled Date Extracted Lab ID Date Sampled Date ExtractedDate Analyzed Date Analyzed

BATCH 62099 SUMMARY

1110650-001A 10/21/11 10/28/11 12:22 PM10/21/11 7:30 AM 1110650-002A 10/21/11 10/28/11 12:22 PM10/21/11 8:10 AM

1110650-003A 10/21/11 10/28/11 2:51 PM10/21/11 9:10 AM

MS = Matrix Spike; MSD = Matrix Spike Duplicate; LCS = Laboratory Control Sample; LCSD = Laboratory Control Sample Duplicate; RPD = Relative Percent Deviation.

% Recovery = 100 * (MS-Sample) / (Amount Spiked); RPD = 100 * (MS - MSD) / ((MS + MSD) / 2).

MS / MSD spike recoveries and / or %RPD may fall outside of laboratory acceptance criteria due to one or more of the following reasons: a) the sample is inhomogenous AND contains significant concentrations of analyte relative to the amount spiked, or b) the spiked sample's matrix interferes with the spike recovery.

N/A = not enough sample to perform matrix spike and matrix spike duplicate.

NR = analyte concentration in sample exceeds spike amount for soil matrix or exceeds 2x spike amount for water matrix or sample diluted due to high matrix or analyte content.

DHS ELAP Certification 1644 QA/QC Officer

Page 22 of 22

Page 35: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

November 01, 2011

Dear Roger:

WorkOrder: 1110651

Client Project ID: #91-02522-C; Berkeley Transfer

Station

Geosphere Consultants

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Date Sampled: 10/21/11

Date Received: 10/21/11

Date Reported: 11/01/11

Date Completed: 10/28/11

Analytical Report

All analyses were completed satisfactorily and all QC samples were found to be within our control limits.

If you have any questions or concerns, please feel free to give me a call. Thank you for choosing

McCampbell Analytical Laboratories for your analytical needs.

Best regards,

Enclosed within are:

2) A QC report for the above sample,

4) An invoice for analytical services.

3) A copy of the chain of custody, and

#91-02522-C; Berkeley Transfer Station,1) The results of the analyzed sample from your project:1

Angela Rydelius

Laboratory Manager

McCampbell Analytical, Inc.

The analytical results relate only to the items tested.

Page 1 of 18

Page 36: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

Page 2 of 18

Page 37: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

McCampbell Analytical, Inc.

1534 Willow Pass Rd

Pittsburg, CA 94565-1701

(925) 252-9262

CHAIN-OF-CUSTODY RECORD Page

Lab ID Matrix Collection Date Hold

Requested Tests (See legend below)

Report to:

Roger Wilcox

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

925-314-7180 FAX: 925-855-7140

PO:

10/21/2011

Client ID

ProjectNo: #91-02522-C; Berkeley Transfer Station

WorkOrder: 1110651

1 of 1

Date Printed:

Date Received: 10/21/2011

1 2 3 4 5 6 7 8 9 10 11 12

Geosphere Consultants

Bill to:

Jennifer Janeson

Geosphere Consultants

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Requested TAT: 5 days

ClientCode: GCSR

Email: [email protected]

EDF Fax Email HardCopy ThirdParty

[email protected]

Excel J-flagWriteOn

cc:

WaterTrax

C1110651-001 Water 10/21/2011 7:301-1 G D A E B F E

Prepared by: Maria Venegas

NOTE: Soil samples are discarded 60 days after results are reported unless other arrangements are made (Water samples are 30 days). Hazardous samples will be returned to client or disposed of at client expense.

Comments:

8260B_W 8270D_W CAM17(T)MS_W G-MBTEX_W PH_W

TPH(DMO)_W TSS_W

1 2 3 4 5

6 7 8 9 10

Test Legend:

TURBIDITY_W

11 12

Page 3 of 18

Page 38: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

Sample Receipt Checklist

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

Client Name: Geosphere Consultants

WorkOrder N°: 1110651

Date and Time Received: 10/21/2011 2:50:53 PM

Checklist completed and reviewed by: Maria Venegas

Matrix: Water Carrier: Client Drop-In

Shipping container/cooler in good condition? Yes No

Custody seals intact on shipping container/cooler? Yes No NA

Samples Received on Ice? Yes No

Chain of custody present? Yes No

Chain of custody signed when relinquished and received? Yes No

Chain of custody agrees with sample labels? Yes No

Samples in proper containers/bottles? Yes No

Sample containers intact? Yes No

Sufficient sample volume for indicated test? Yes No

All samples received within holding time? Yes No

NAContainer/Temp Blank temperature

Yes No No VOA vials submittedWater - VOA vials have zero headspace / no bubbles?

Metal - pH acceptable upon receipt (pH<2)? Yes No NA

* NOTE: If the "No" box is checked, see comments below.

Cooler Temp: 20.2°C

Chain of Custody (COC) Information

Yes NoSample IDs noted by Client on COC?

Yes NoDate and Time of collection noted by Client on COC?

Yes NoSampler's name noted on COC?

Sample Receipt Information

Sample Preservation and Hold Time (HT) Information

Sample labels checked for correct preservation? Yes No

Project Name: #91-02522-C; Berkeley Transfer Station

(Ice Type: BLUE ICE )

Client contacted: Date contacted: Contacted by:

Comments:

Page 4 of 18

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1-1

Client Project ID: #91-02522-C;

Berkeley Transfer Station

Geosphere Consultants

Extraction Method: Analytical Method:

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Lab ID

Client ID

Matrix Water

1110651-001C

Compound Concentration * Compound Concentration *Reporting

LimitDFReporting

LimitDF

Volatile Organics by P&T and GC/MS (Basic Target List)*

SW8260BSW5030B Work Order: 1110651

Date Sampled: 10/21/11

Date Received: 10/21/11

Date Extracted: 10/24/11

Date Analyzed: 10/24/11

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

Surrogate Recoveries (%)

Acetone ND 1.0 10 tert-Amyl methyl ether (TAME) ND 1.0 0.5

Benzene ND 1.0 0.5 Bromobenzene ND 1.0 0.5

Bromochloromethane ND 1.0 0.5 Bromodichloromethane ND 1.0 0.5

Bromoform ND 1.0 0.5 Bromomethane ND 1.0 0.5

2-Butanone (MEK) ND 1.0 2.0 t-Butyl alcohol (TBA) ND 1.0 2.0

n-Butyl benzene ND 1.0 0.5 sec-Butyl benzene ND 1.0 0.5

tert-Butyl benzene ND 1.0 0.5 Carbon Disulfide ND 1.0 0.5

Carbon Tetrachloride ND 1.0 0.5 Chlorobenzene ND 1.0 0.5

Chloroethane ND 1.0 0.5 Chloroform ND 1.0 0.5

Chloromethane ND 1.0 0.5 2-Chlorotoluene ND 1.0 0.5

4-Chlorotoluene ND 1.0 0.5 Dibromochloromethane ND 1.0 0.5

1,2-Dibromo-3-chloropropane ND 1.0 0.2 1,2-Dibromoethane (EDB) ND 1.0 0.5

Dibromomethane ND 1.0 0.5 1,2-Dichlorobenzene ND 1.0 0.5

1,3-Dichlorobenzene ND 1.0 0.5 1,4-Dichlorobenzene ND 1.0 0.5

Dichlorodifluoromethane ND 1.0 0.5 1,1-Dichloroethane ND 1.0 0.5

1,2-Dichloroethane (1,2-DCA) ND 1.0 0.5 1,1-Dichloroethene ND 1.0 0.5

cis-1,2-Dichloroethene ND 1.0 0.5 trans-1,2-Dichloroethene ND 1.0 0.5

1,2-Dichloropropane ND 1.0 0.5 1,3-Dichloropropane ND 1.0 0.5

2,2-Dichloropropane ND 1.0 0.5 1,1-Dichloropropene ND 1.0 0.5

cis-1,3-Dichloropropene ND 1.0 0.5 trans-1,3-Dichloropropene ND 1.0 0.5

Diisopropyl ether (DIPE) ND 1.0 0.5 Ethylbenzene ND 1.0 0.5

Ethyl tert-butyl ether (ETBE) ND 1.0 0.5 Freon 113 ND 1.0 10

Hexachlorobutadiene ND 1.0 0.5 Hexachloroethane ND 1.0 0.5

2-Hexanone ND 1.0 0.5 Isopropylbenzene ND 1.0 0.5

4-Isopropyl toluene ND 1.0 0.5 Methyl-t-butyl ether (MTBE) ND 1.0 0.5

Methylene chloride ND 1.0 0.5 4-Methyl-2-pentanone (MIBK) ND 1.0 0.5

Naphthalene ND 1.0 0.5 n-Propyl benzene ND 1.0 0.5

Styrene ND 1.0 0.5 1,1,1,2-Tetrachloroethane ND 1.0 0.5

1,1,2,2-Tetrachloroethane ND 1.0 0.5 Tetrachloroethene ND 1.0 0.5

Toluene ND 1.0 0.5 1,2,3-Trichlorobenzene ND 1.0 0.5

1,2,4-Trichlorobenzene ND 1.0 0.5 1,1,1-Trichloroethane ND 1.0 0.5

1,1,2-Trichloroethane ND 1.0 0.5 Trichloroethene ND 1.0 0.5

Trichlorofluoromethane ND 1.0 0.5 1,2,3-Trichloropropane ND 1.0 0.5

1,2,4-Trimethylbenzene ND 1.0 0.5 1,3,5-Trimethylbenzene ND 1.0 0.5

Vinyl Chloride ND 1.0 0.5 Xylenes, Total ND 1.0 0.5

%SS1: 99 %SS2: 108

%SS3: 107

* water and vapor samples are reported in µg/L, soil/sludge/solid samples in mg/kg, product/oil/non-aqueous liquid samples and all TCLP & SPLP extracts are

reported in mg/L, wipe samples in µg/wipe.

ND means not detected above the reporting limit/method detection limit; N/A means analyte not applicable to this analysis; %SS = Percent Recovery of Surrogate

Standard; DF = Dilution Factor

# surrogate diluted out of range or coelutes with another peak; &) low surrogate due to matrix interference.

b1) aqueous sample that contains greater than ~1 vol. % sediment

Comments: b1

DHS ELAP Certification 1644 Angela Rydelius, Lab ManagerPage 5 of 18

Page 40: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

1-1

Client Project ID: #91-02522-C;

Berkeley Transfer Station

Geosphere Consultants

Extraction Method: Analytical Method:

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Lab ID

Client ID

Matrix Water

1110651-001G

Compound Concentration * Compound Concentration *Reporting

LimitDFReporting

LimitDF

Semi-Volatile Organics by GC/MS (Basic Target List)*

SW8270CSW3510C Work Order: 1110651

Date Sampled: 10/21/11

Date Received: 10/21/11

Date Extracted: 10/21/11

Date Analyzed: 11/01/11

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

Surrogate Recoveries (%)

Acenaphthene ND 1.0 10 Acenaphthylene ND 1.0 10

Acetochlor ND 1.0 10 Anthracene ND 1.0 10

Benzidine ND 1.0 50 Benzoic Acid ND 1.0 50

Benzo (a) anthracene ND 1.0 10 Benzo (b) fluoranthene ND 1.0 10

Benzo (k) fluoranthene ND 1.0 10 Benzo (g,h,i) perylene ND 1.0 10

Benzo (a) pyrene ND 1.0 10 Benzyl Alcohol ND 1.0 50

1,1-Biphenyl ND 1.0 10 Bis (2-chloroethoxy) Methane ND 1.0 10

Bis (2-chloroethyl) Ether ND 1.0 10 Bis (2-chloroisopropyl) Ether ND 1.0 10

Bis (2-ethylhexyl) Phthalate ND 1.0 20 4-Bromophenyl Phenyl Ether ND 1.0 10

Butylbenzyl Phthalate ND 1.0 10 4-Chloroaniline ND 1.0 20

4-Chloro-3-methylphenol ND 1.0 10 2-Chloronaphthalene ND 1.0 10

2-Chlorophenol ND 1.0 10 4-Chlorophenyl Phenyl Ether ND 1.0 10

Chrysene ND 1.0 10 Dibenzo (a,h) anthracene ND 1.0 10

Dibenzofuran ND 1.0 10 Di-n-butyl Phthalate ND 1.0 10

1,2-Dichlorobenzene ND 1.0 10 1,3-Dichlorobenzene ND 1.0 10

1,4-Dichlorobenzene ND 1.0 10 3,3-Dichlorobenzidine ND 1.0 20

2,4-Dichlorophenol ND 1.0 10 Diethyl Phthalate ND 1.0 10

2,4-Dimethylphenol ND 1.0 10 Dimethyl Phthalate ND 1.0 10

4,6-Dinitro-2-methylphenol ND 1.0 50 2,4-Dinitrophenol ND 1.0 50

2,4-Dinitrotoluene ND 1.0 10 2,6-Dinitrotoluene ND 1.0 10

Di-n-octyl Phthalate ND 1.0 10 1,2-Diphenylhydrazine ND 1.0 10

Fluoranthene ND 1.0 10 Fluorene ND 1.0 10

Hexachlorobenzene ND 1.0 10 Hexachlorobutadiene ND 1.0 10

Hexachlorocyclopentadiene ND 1.0 50 Hexachloroethane ND 1.0 10

Indeno (1,2,3-cd) pyrene ND 1.0 10 Isophorone ND 1.0 10

2-Methylnaphthalene ND 1.0 10 2-Methylphenol (o-Cresol) ND 1.0 10

3 &/or 4-Methylphenol (m,p-Cresol) ND 1.0 10 Naphthalene ND 1.0 10

2-Nitroaniline ND 1.0 50 3-Nitroaniline ND 1.0 50

4-Nitroaniline ND 1.0 50 Nitrobenzene ND 1.0 10

2-Nitrophenol ND 1.0 50 4-Nitrophenol ND 1.0 50

N-Nitrosodiphenylamine ND 1.0 10 N-Nitrosodi-n-propylamine ND 1.0 10

Pentachlorophenol ND 1.0 50 Phenanthrene ND 1.0 10

Phenol ND 1.0 10 Pyrene ND 1.0 10

1,2,4-Trichlorobenzene ND 1.0 10 2,4,5-Trichlorophenol ND 1.0 10

2,4,6-Trichlorophenol ND 1.0 10

%SS1: 98 %SS2: 59

%SS3: 100 %SS4: 55

%SS5: 100 %SS6: 74

* water samples in µg/L, soil/sludge/solid samples in mg/kg, wipe samples in µg/wipe, product/oil/non-aqueous liquid samples and all TCLP & SPLP

extracts are reported in mg/L.

ND means not detected at or above the reporting limit/method detection limit; N/A means analyte not applicable to this analysis; %SS = Percent

Recovery of Surrogate Standard; DF = Dilution Factor; #) surrogate diluted out of range or surrogate coelutes with another peak.

b1) aqueous sample that contains greater than ~1 vol. % sediment

Comments: b1

DHS ELAP Certification 1644 Angela Rydelius, Lab ManagerPage 6 of 18

Page 41: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

Client Project ID: #91-02522-C;

Berkeley Transfer Station

Geosphere Consultants

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Date Sampled: 10/21/11

Date Received 10/21/11

Date Extracted 10/21/11

Date Analyzed 10/25/11

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

1110651-001D

1-1

Lab ID

Client ID

W

TOTAL

Matrix

Extraction Type

Reporting Limit for DF =1;

ND means not detected

above the reporting limit

S W

mg/kg µg/L

1 120

Extraction Method:Analytical Method: E200.8 E200.8 Work Order: 1110651

Dilution Factor

ICP-MS Metals, Concentration*

CAM / CCR 17 Metals*

Antimony ND<10 NA 0.5

Arsenic 99 NA 0.5

Barium 5500 NA 5.0

Beryllium 10 NA 0.5

Cadmium ND<5.0 NA 0.25

Chromium 440 NA 0.5

Cobalt 360 NA 0.5

Copper 320 NA 0.5

Lead 710 NA 0.5

Mercury 30 NA 0.025

Molybdenum ND<10 NA 0.5

Nickel 990 NA 0.5

Selenium ND<10 NA 0.5

Silver ND<3.8 NA 0.19

Thallium ND<10 NA 0.5

Vanadium 670 NA 0.5

Zinc 820 NA 5.0

%SS: 108

Comments a12,b1

*water samples are reported in µg/L, product/oil/non-aqueous liquid samples and all TCLP / STLC / DISTLC / SPLP extracts are reported in mg/L,

soil/sludge/solid samples in mg/kg, wipe samples in µg/wipe, filter samples in µg/filter.

# means surrogate diluted out of range; ND means not detected above the reporting limit/method detection limit; N/A means not applicable to this sample

or instrument; %SS = Percent Recovery of Surrogate Standard; DF = Dilution Factor

TOTAL = Hot acid digestion of a representative sample aliquot.

TRM = Total recoverable metals is the "direct analysis" of a sample aliquot taken from its acid-preserved container.

DISS = Dissolved metals by direct analysis of 0.45 µm filtered and acidified sample.

a12) reporting limit raised due to high non-reported metals content.

b1) aqueous sample that contains greater than ~1 vol. % sediment

DHS ELAP Certification 1644 Angela Rydelius, Lab Manager

Page 7 of 18

Page 42: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

Lab ID TPH(g) MTBE Benzene TolueneClient ID Ethylbenzene XylenesMatrix DF % SS

Gasoline Range (C6-C12) Volatile Hydrocarbons as Gasoline with BTEX and MTBE*

Client Project ID: #91-02522-C;

Berkeley Transfer Station

Geosphere Consultants

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Date Sampled: 10/21/11

Date Received: 10/21/11

Date Extracted: 10/26/11

Date Analyzed: 10/26/11

Work Order: 1110651Extraction method: SW5030B Analytical methods: SW8021B/8015Bm

Comments

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

ND1-1 ND ND ND001A W ND ND 1 111 b1

DHS ELAP Certification 1644 Angela Rydelius, Lab Manager

Reporting Limit for DF =1;

ND means not detected at or

above the reporting limit

W

S

50 5.0 0.5 0.5 0.5 0.5

1.0 0.05 0.005 0.005 0.005 0.005

µg/L

mg/Kg

* water and vapor samples are reported in ug/L, soil/sludge/solid samples in mg/kg, wipe samples in µg/wipe, product/oil/non-aqueous liquid samples and all TCLP &

SPLP extracts in mg/L.

# cluttered chromatogram; sample peak coelutes w/surrogate peak; low surrogate recovery due to matrix interference. %SS = Percent Recovery of Surrogate Standard;

DF = Dilution Factor

The following descriptions of the TPH chromatogram are cursory in nature and McCampbell Analytical is not responsible for their interpretation:

b1) aqueous sample that contains greater than ~1 vol. % sediment

Page 8 of 18

Page 43: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

Client Project ID: #91-02522-C;

Berkeley Transfer Station

Geosphere Consultants

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Date Sampled: 10/21/11

Date Received: 10/21/11

Date Extracted: 10/21/11

Date Analyzed: 10/21/11

Analytical Method:

pH*

SM4500H+B

Lab ID Matrix DFClient ID

Work Order: 1110651

pH Comments

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

1-1 7.25 @ 24.2°C 11110651-001E W b1

DHS ELAP Certification 1644 Angela Rydelius, Lab Manager

W

S

* According the formal method, this is "field test" with a 15 minute Hold Time. However, as this is unrealistically short for commercial environmental

analysis, MAI has designated a 24 hour hold time for aqueous samples.

DF = Dilution Factor

b1) aqueous sample that contains greater than ~1 vol. % sediment

±0.05, pH units @ °C

NA

Method Accuracy and Reporting Units

Page 9 of 18

Page 44: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

Client Project ID: #91-02522-C;

Berkeley Transfer Station

Geosphere Consultants

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Date Sampled: 10/21/11

Date Received: 10/21/11

Date Extracted: 10/21/11

Date Analyzed: 10/25/11

Work Order: 1110651

Total Extractable Petroleum Hydrocarbons*

Extraction method: SW3510C Analytical methods: SW8015B

Lab IDTPH-Diesel TPH-Motor Oil

Client ID Matrix DF % SS(C10-C23) (C18-C36)

Comments

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

1-1 110 ND1110651-001B W 1 79 e2,b1

DHS ELAP Certification 1644 Angela Rydelius, Lab Manager

Reporting Limit for DF =1;

ND means not detected at or

above the reporting limit

W

S

50 250

NA NA

µg/L

mg/Kg

* water samples are reported in µg/L, wipe samples in µg/wipe, soil/solid/sludge samples in mg/kg, product/oil/non-aqueous liquid samples in mg/L, and all DISTLC

/ STLC / SPLP / TCLP extracts are reported in µg/L.

# cluttered chromatogram resulting in coeluted surrogate and sample peaks, or; surrogate peak is on elevated baseline, or; surrogate has been diminished by dilution

of original extract; %SS = Percent Recovery of Surrogate Standard; DF = Dilution Factor

The following descriptions of the TPH chromatogram are cursory in nature and McCampbell Analytical is not responsible for their interpretation:

b1) aqueous sample that contains greater than ~1 vol. % sediment

e2) diesel range compounds are significant; no recognizable pattern

Page 10 of 18

Page 45: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

Client Project ID: #91-02522-C;

Berkeley Transfer Station

Geosphere Consultants

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Date Sampled: 10/21/11

Date Received: 10/21/11

Date Extracted: 10/24/11

Date Analyzed: 10/24/11

Analytical Method:

Total Suspended Solids*

SM2540D

Lab ID Matrix DFClient ID

Work Order: 1110651

Total Suspended Solids Comments

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

1-1 29,600 501110651-001F W b1

DHS ELAP Certification 1644 Angela Rydelius, Lab Manager

W

S

* water samples reported in mg/L.

DF = Dilution Factor

b1) aqueous sample that contains greater than ~1 vol. % sediment

1.0 mg/L

NA

Reporting Limit for DF = 1; ND means not detected at or above the

reporting limit

Page 11 of 18

Page 46: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

Client Project ID: #91-02522-C;

Berkeley Transfer Station

Geosphere Consultants

2001 Crow Canyon Road, Suite 100

San Ramon, CA 94583

Client Contact: Roger Wilcox

Client P.O.:

Date Sampled: 10/21/11

Date Received: 10/21/11

Date Extracted: 10/21/11

Date Analyzed: 10/21/11

Analytical Method:

Turbidity

SM2130B

Lab ID Matrix DFClient ID

Work Order: 1110651

Turbidity Comments

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

1-1 11000 101110651-001E W g1,b1

DHS ELAP Certification 1644 Angela Rydelius, Lab Manager

W

S

DF = Dilution Factor

b1) aqueous sample that contains greater than ~1 vol. % sediment

g1) presence of debris / coarse sediment that was allowed to settle prior to Turbidity measurement

0.1 NTU

NA

Reporting Limit for DF = 1; ND means not detected at or above the

reporting limit

Page 12 of 18

Page 47: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

QC SUMMARY REPORT FOR SW8021B/8015Bm

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

EPA Method: SW8021B/8015Bm Extraction: SW5030B Spiked Sample ID: 1110623-007A

Sample Spiked MS

% Rec. % Rec. % Rec. % Rec.

MSD LCS LCSDMS-MSD

% RPD

LCS-LCSD

% RPD

WorkOrder: 1110651W.O. Sample Matrix: Water BatchID: 62085

MS / MSD

Acceptance Criteria (%)

LCS/LCSD

Analyte

QC Matrix: Water

RPD RPDµg/L µg/L

TPH(btex) ND 60 96.1 94.5 1.77 96.6 93.6 3.21 70 - 130 70 - 130£ 20 20

MTBE ND 10 98.5 103 4.05 93.9 95.9 2.05 70 - 130 70 - 13020 20

Benzene ND 10 115 120 4.00 114 117 2.20 70 - 130 70 - 13020 20

Toluene ND 10 102 106 3.25 102 104 1.64 70 - 130 70 - 13020 20

Ethylbenzene ND 10 105 107 2.51 103 104 0.672 70 - 130 70 - 13020 20

Xylenes ND 30 118 122 2.85 117 117 0 70 - 130 70 - 13020 20

%SS: 107 10 106 109 2.28 103 108 4.61 70 - 130 70 - 13020 20

All target compounds in the Method Blank of this extraction batch were ND less than the method RL with the following exceptions:

NONE

Lab ID Date Sampled Date Extracted Lab ID Date Sampled Date ExtractedDate Analyzed Date Analyzed

BATCH 62085 SUMMARY

1110651-001A 10/26/11 10/26/11 5:29 AM10/21/11 7:30 AM

MS = Matrix Spike; MSD = Matrix Spike Duplicate; LCS = Laboratory Control Sample; LCSD = Laboratory Control Sample Duplicate; RPD = Relative Percent Deviation.

% Recovery = 100 * (MS-Sample) / (Amount Spiked); RPD = 100 * (MS - MSD) / ((MS + MSD) / 2).

MS / MSD spike recoveries and / or %RPD may fall outside of laboratory acceptance criteria due to one or more of the following reasons: a) the sample is inhomogenous AND contains significant concentrations of analyte relative to the amount spiked, or b) the spiked sample's matrix interferes with the spike recovery.

£ TPH(btex) = sum of BTEX areas from the FID.

# cluttered chromatogram; sample peak coelutes with surrogate peak.

N/A = not enough sample to perform matrix spike and matrix spike duplicate.

NR = matrix interference and/or analyte concentration in sample exceeds spike amount for soil matrix or exceeds 2x spike amount for water matrix or sample diluted due to high matrix or analyte content, or inconsistency in sample containers.

DHS ELAP Certification 1644 QA/QC Officer

Page 13 of 18

Page 48: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

QC SUMMARY REPORT FOR SW8260B

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

EPA Method: SW8260B Extraction: SW5030B Spiked Sample ID: 1110636-010B

Sample Spiked MS

% Rec. % Rec. % Rec. % Rec.

MSD LCS LCSDMS-MSD

% RPD

LCS-LCSD

% RPD

WorkOrder: 1110651W.O. Sample Matrix: Water BatchID: 62086

MS / MSD

Acceptance Criteria (%)

LCS/LCSD

Analyte

QC Matrix: Water

RPD RPDµg/L µg/L

tert-Amyl methyl ether (TAME) ND 10 85.6 87.8 2.42 72.3 82.3 12.9 70 - 130 70 - 13030 30

Benzene ND 10 106 106 0 89.2 102 13.3 70 - 130 70 - 13030 30

t-Butyl alcohol (TBA) ND 50 89.9 97.2 7.77 74.6 85.6 13.7 70 - 130 70 - 13030 30

Chlorobenzene ND 10 107 107 0 94 104 10.5 70 - 130 70 - 13030 30

1,2-Dibromoethane (EDB) ND 10 102 104 2.48 86.1 98.7 13.7 70 - 130 70 - 13030 30

1,2-Dichloroethane (1,2-DCA) ND 10 104 103 0.192 86.5 97.7 12.2 70 - 130 70 - 13030 30

1,1-Dichloroethene ND 10 113 110 3.02 84.6 94.3 10.8 70 - 130 70 - 13030 30

Diisopropyl ether (DIPE) ND 10 113 114 0.893 84.2 95.5 12.6 70 - 130 70 - 13030 30

Ethyl tert-butyl ether (ETBE) ND 10 93.7 94 0.258 78.8 90.7 14.1 70 - 130 70 - 13030 30

Methyl-t-butyl ether (MTBE) ND 10 108 110 1.42 75.4 86.5 13.0 70 - 130 70 - 13030 30

Toluene ND 10 106 107 1.11 91.4 102 10.5 70 - 130 70 - 13030 30

Trichloroethene ND 10 103 101 2.00 85 96.7 12.8 70 - 130 70 - 13030 30

%SS1: 104 25 114 112 1.12 102 103 0.432 70 - 130 70 - 13030 30

%SS2: 108 25 111 111 0 108 107 0.911 70 - 130 70 - 13030 30

%SS3: 111 2.5 103 102 1.04 104 105 1.37 70 - 130 70 - 13030 30

All target compounds in the Method Blank of this extraction batch were ND less than the method RL with the following exceptions:

NONE

Lab ID Date Sampled Date Extracted Lab ID Date Sampled Date ExtractedDate Analyzed Date Analyzed

BATCH 62086 SUMMARY

1110651-001C 10/24/11 10/24/11 2:00 PM10/21/11 7:30 AM

MS = Matrix Spike; MSD = Matrix Spike Duplicate; LCS = Laboratory Control Sample; LCSD = Laboratory Control Sample Duplicate; RPD = Relative Percent Deviation.

% Recovery = 100 * (MS-Sample) / (Amount Spiked); RPD = 100 * (MS - MSD) / ((MS + MSD) / 2).

MS / MSD spike recoveries and / or %RPD may fall outside of laboratory acceptance criteria due to one or more of the following reasons: a) the sample is inhomogenous AND contains significant concentrations of analyte relative to the amount spiked, or b) the spiked sample's matrix interferes with the spike recovery.

N/A = not enough sample to perform matrix spike and matrix spike duplicate.

NR = analyte concentration in sample exceeds spike amount for soil matrix or exceeds 2x spike amount for water matrix or sample diluted due to high matrix or analyte content.

# surrogate diluted out of range or coelutes with another peak; &) low surrogate due to matrix interference.

Laboratory extraction solvents such as methylene chloride and acetone may occasionally appear in the method blank at low levels.

DHS ELAP Certification 1644 QA/QC Officer

Page 14 of 18

Page 49: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

QC SUMMARY REPORT FOR SW8270C

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

EPA Method: SW8270C Extraction: SW3510C Spiked Sample ID: N/A

Sample Spiked MS

% Rec. % Rec. % Rec. % Rec.

MSD LCS LCSDMS-MSD

% RPD

LCS-LCSD

% RPD

WorkOrder: 1110651W.O. Sample Matrix: Water BatchID: 62049

MS / MSD

Acceptance Criteria (%)

LCS/LCSD

Analyte

QC Matrix: Water

RPD RPDµg/L µg/L

Acenaphthene N/A 50 N/A N/A N/A 56.5 58 2.62 N/A 30 - 130N/A 20

4-Chloro-3-methylphenol N/A 100 N/A N/A N/A 62.9 64.2 1.96 N/A 30 - 130N/A 20

2-Chlorophenol N/A 100 N/A N/A N/A 80.6 81.8 1.48 N/A 30 - 130N/A 20

1,4-Dichlorobenzene N/A 50 N/A N/A N/A 63.6 65.2 2.49 N/A 30 - 130N/A 20

2,4-Dinitrotoluene N/A 50 N/A N/A N/A 68.5 71.1 3.74 N/A 30 - 130N/A 20

4-Nitrophenol N/A 100 N/A N/A N/A 50.5 51.2 1.30 N/A 30 - 130N/A 20

N-Nitrosodi-n-propylamine N/A 50 N/A N/A N/A 82.4 84.7 2.74 N/A 30 - 130N/A 20

Pentachlorophenol N/A 100 N/A N/A N/A 50.3 54.8 8.51 N/A 30 - 130N/A 20

Phenol N/A 100 N/A N/A N/A 75.5 75.9 0.588 N/A 30 - 130N/A 20

Pyrene N/A 50 N/A N/A N/A 62 64.3 3.58 N/A 30 - 130N/A 20

1,2,4-Trichlorobenzene N/A 50 N/A N/A N/A 63.8 65.2 2.23 N/A 30 - 130N/A 20

%SS1: N/A 5000 N/A N/A N/A 110 109 0.958 N/A 30 - 130N/A 20

%SS2: N/A 5000 N/A N/A N/A 107 105 1.56 N/A 30 - 130N/A 20

%SS3: N/A 5000 N/A N/A N/A 104 104 0 N/A 30 - 130N/A 20

%SS4: N/A 5000 N/A N/A N/A 96 98 1.09 N/A 30 - 130N/A 20

%SS5: N/A 5000 N/A N/A N/A 94 93 0.827 N/A 30 - 130N/A 20

%SS6: N/A 5000 N/A N/A N/A 117 116 0.679 N/A 30 - 130N/A 20

All target compounds in the Method Blank of this extraction batch were ND less than the method RL with the following exceptions:

NONE

Lab ID Date Sampled Date Extracted Lab ID Date Sampled Date ExtractedDate Analyzed Date Analyzed

BATCH 62049 SUMMARY

1110651-001G 10/21/11 11/01/11 10:24 AM10/21/11 7:30 AM

MS = Matrix Spike; MSD = Matrix Spike Duplicate; LCS = Laboratory Control Sample; LCSD = Laboratory Control Sample Duplicate; RPD = Relative Percent Deviation.

% Recovery = 100 * (MS-Sample) / (Amount Spiked); RPD = 100 * (MS - MSD) / ((MS + MSD) / 2).

MS / MSD spike recoveries and / or %RPD may fall outside of laboratory acceptance criteria due to one or more of the following reasons: a) the sample is inhomogenous AND contains significant concentrations of analyte relative to the amount spiked, or b) the spiked sample's matrix interferes with the spike recovery.

N/A = not enough sample to perform matrix spike and matrix spike duplicate.

NR = analyte concentration in sample exceeds spike amount for soil matrix or exceeds 2x spike amount for water matrix or sample diluted due to high matrix or analyte content.

Laboratory extraction solvents such as methylene chloride and acetone may occasionally appear in the method blank at low levels.

DHS ELAP Certification 1644 QA/QC Officer

Page 15 of 18

Page 50: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

QC SUMMARY REPORT FOR E200.8

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

EPA Method: E200.8 Extraction: E200.8 Spiked Sample ID: 1110486-002A

Sample Spiked MS

% Rec. % Rec. % Rec. % Rec.

MSD LCS LCSDMS-MSD

% RPD

LCS-LCSD

% RPD

WorkOrder: 1110651W.O. Sample Matrix: Water BatchID: 62006

MS / MSD

Acceptance Criteria (%)

LCS/LCSD

Analyte

QC Matrix: Water

RPD RPDµg/L µg/L

Antimony ND 10 102 105 2.61 102 99.2 2.46 70 - 130 85 - 11520 20

Arsenic 2.2 10 103 108 3.68 105 106 0.473 70 - 130 85 - 11520 20

Barium 35 100 96.4 98.7 1.73 99.3 96.4 2.92 70 - 130 85 - 11520 20

Beryllium ND 10 102 104 1.84 108 105 3.11 70 - 130 85 - 11520 20

Cadmium ND 10 101 103 1.57 105 101 3.11 70 - 130 85 - 11520 20

Chromium 1.8 10 90.2 92.5 2.10 111 109 1.27 70 - 130 85 - 11520 20

Cobalt ND 10 94.2 96.2 2.09 101 98.6 2.73 70 - 130 85 - 11520 20

Copper 29 10 NR NR NR 112 109 2.72 70 - 130 85 - 11520 20

Lead ND 10 108 107 1.02 106 104 1.62 70 - 130 85 - 11520 20

Mercury ND 0.25 98.8 103 3.93 103 102 0.894 70 - 130 85 - 11520 20

Molybdenum 3.2 10 101 101 0 102 98.8 2.75 70 - 130 85 - 11520 20

Nickel 1.9 10 95.4 96.4 0.868 109 109 0 70 - 130 85 - 11520 20

Selenium 0.64 10 104 110 5.74 108 108 0 70 - 130 85 - 11520 20

Silver ND 10 107 109 1.86 111 109 2.36 70 - 130 85 - 11520 20

Thallium ND 10 102 104 2.42 104 101 3.52 70 - 130 85 - 11520 20

Vanadium 3.1 10 103 107 2.35 107 104 2.37 70 - 130 85 - 11520 20

Zinc ND 100 102 103 1.68 108 105 3.00 70 - 130 85 - 11520 20

%SS: 111 750 107 108 0.742 108 104 3.86 70 - 130 70 - 13020 20

All target compounds in the Method Blank of this extraction batch were ND less than the method RL with the following exceptions:

NONE

Lab ID Date Sampled Date Extracted Lab ID Date Sampled Date ExtractedDate Analyzed Date Analyzed

BATCH 62006 SUMMARY

1110651-001D 10/21/11 10/25/11 11:49 PM10/21/11 7:30 AM

MS = Matrix Spike; MSD = Matrix Spike Duplicate; LCS = Laboratory Control Sample; LCSD = Laboratory Control Sample Duplicate; RPD = Relative Percent Deviation.

% Recovery = 100 * (MS-Sample) / (Amount Spiked); RPD = 100 * (MS - MSD) / ((MS + MSD) / 2).

MS / MSD spike recoveries and / or %RPD may fall outside of laboratory acceptance criteria due to one or more of the following reasons: a) the sample is inhomogenous AND contains significant concentrations of analyte relative to the amount spiked, or b) the spiked sample's matrix interferes with the spike recovery.

N/A = not applicable to this method.

NR = matrix interference and/or analyte concentration in sample exceeds spike amount for soil matrix or exceeds 2x spike amount for water matrix or sample diluted due to high matrix or analyte content.

DHS ELAP Certification 1644 QA/QC Officer

Page 16 of 18

Page 51: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

QC SUMMARY REPORT FOR WET CHEMISTRY TESTS

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

Method Name: SM4500H+B

WorkOrder: 1110651Matrix: W

BatchID: 62008

Test Method: SM4500H+B (pH)

Lab ID Sample DF Dup / Ser. Dil. DF Precision Acceptance Criteria

Units: ±, pH units @ °C

1110651-001E 7.25 @ 24.2°C 1 7.29 @ 24.3°C 1 0.04 0.05

Lab ID Date Sampled Date Extracted Lab ID Date Sampled Date ExtractedDate Analyzed Date Analyzed

BATCH 62008 SUMMARY

1110651-001E 10/21/11 10/21/11 7:00 PM10/21/11 7:30 AM

Method Name: SM2540D

WorkOrder: 1110651Matrix: W

BatchID: 62000

Test Method: SM2540D (TSS)

Lab ID Sample DF Dup / Ser. Dil. DF % RPD Acceptance Criteria (%)

Units: mg/L

1110651-001F 29,600 50 29,600 50 0.203 <15

Lab ID Date Sampled Date Extracted Lab ID Date Sampled Date ExtractedDate Analyzed Date Analyzed

BATCH 62000 SUMMARY

1110651-001F 10/24/11 10/24/11 2:05 PM10/21/11 7:30 AM

Method Name: SM2130B

WorkOrder: 1110651Matrix: W

BatchID: 62079

Test Method: SM2130B (Turbidity)

Lab ID Sample DF Dup / Ser. Dil. DF % RPD Acceptance Criteria (%)

Units: NTU

1110651-001E 11,000 10 11,000 10 0 <10

Lab ID Date Sampled Date Extracted Lab ID Date Sampled Date ExtractedDate Analyzed Date Analyzed

BATCH 62079 SUMMARY

1110651-001E 10/21/11 10/21/11 4:10 PM10/21/11 7:30 AM

Dup = Duplicate; Ser. Dil. = Serial Dilution; MS = Matrix Spike; RD = Relative Difference; RPD = Relative Percent Deviation.

Precision = Absolute Value (Sample - Duplicate)

RPD = 100 * (Sample - Duplicate) / [(Sample + Duplicate) / 2]

%RPD is calculated using results of up to 10 significant figures, however the reported results are rounded to 2 or 3 significant figures. Therefore there may be a slight discrepancy between the %RPD displayed above and %RPD calculated using the reported results. MAI considers %RPD based upon more significant figures to be more accurate.

DHS ELAP Certification 1644 QA/QC Officer

Page 17 of 18

Page 52: ...- Geologic Unit - Franciscan Complex - Geologic Unit - Hillslope Deposits - Approximate Boring Location Geologic Cross Section A A’ A’A A ’ B-3 Figure 2 Berkeley Transfer

QC SUMMARY REPORT FOR SW8015B

McCampbell Analytical, Inc.1534 Willow Pass Road, Pittsburg, CA 94565-1701

Toll Free Telephone: (877) 252-9262 / Fax: (925) 252-9269

http://www.mccampbell.com / E-mail: [email protected]"When Quality Counts"

EPA Method: SW8015B Extraction: SW3510C Spiked Sample ID: N/A

Sample Spiked MS

% Rec. % Rec. % Rec. % Rec.

MSD LCS LCSDMS-MSD

% RPD

LCS-LCSD

% RPD

WorkOrder: 1110651W.O. Sample Matrix: Water BatchID: 62030

MS / MSD

Acceptance Criteria (%)

LCS/LCSD

Analyte

QC Matrix: Water

RPD RPDµg/L µg/L

TPH-Diesel (C10-C23) N/A 1000 N/A N/A N/A 125 119 4.89 N/A 70 - 130N/A 30

%SS: N/A 625 N/A N/A N/A 83 96 14.3 N/A 70 - 130N/A 30

All target compounds in the Method Blank of this extraction batch were ND less than the method RL with the following exceptions:

NONE

Lab ID Date Sampled Date Extracted Lab ID Date Sampled Date ExtractedDate Analyzed Date Analyzed

BATCH 62030 SUMMARY

1110651-001B 10/21/11 10/25/11 7:34 AM10/21/11 7:30 AM

MS = Matrix Spike; MSD = Matrix Spike Duplicate; LCS = Laboratory Control Sample; LCSD = Laboratory Control Sample Duplicate; RPD = Relative Percent Deviation.

% Recovery = 100 * (MS-Sample) / (Amount Spiked); RPD = 100 * (MS - MSD) / ((MS + MSD) / 2).

MS / MSD spike recoveries and / or %RPD may fall outside of laboratory acceptance criteria due to one or more of the following reasons: a) the sample is inhomogenous AND contains significant concentrations of analyte relative to the amount spiked, or b) the spiked sample's matrix interferes with the spike recovery.

N/A = not enough sample to perform matrix spike and matrix spike duplicate.

NR = analyte concentration in sample exceeds spike amount for soil matrix or exceeds 2x spike amount for water matrix or sample diluted due to high matrix or analyte content.

DHS ELAP Certification 1644 QA/QC Officer

Page 18 of 18