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3333 UNION AVE (3)
Central ir®nmental Enviro , ' f x t Consultant June 21, 2007 a Syr � III�II�IIIIIIIIIIIII 57 IE Mr. Munther Hawatmeh 2698 Mt Vernon Avenue ,Bakersfield, California 93306 BASELINE ENVIRONMENTAL ASSESSMENT WORK PLAN FOR THE ARCO AM/PM MINI MARKET NUMBER 3090 3333 UNION AVENUE, BAKERSFIELD,CALIFORNIA Dear Mr. Hawatmeh: The following work plan outlines Central Sierra Environmental, LLC's (CSE's) proposed methodology for conducting a Baseline Environmental Assessment (BEA) at the above-referenced site. CSE proposes to advance six soil borings adjacent to the USTs and dispensers and analyze soil samples for gasoline hydrocarbons during this environmental assessment. The BEA is being performed in association with the purchase of the property by Mr. Munther Hawatmeh from BP West Coast Products LLC (BP). The BEA is intended to establish baseline environmental conditions to satisfy the due diligence requirements for the eligibility of the buyer to seek reimbursement as a B Class claimant from the SWRCB/UST Cleanup Fund (USTCF) for any potential future investigation and/or cleanup cost that may be required by the Bakersfield Fire Department.Hazardous Materials Division (BFDHMD). 1. PURPOSE AND SCOPE: The purpose of this work plan is to outline the methodology to be followed for the assessment of the potential gasoline hydrocarbons in the soil at the subject site. The proposed scope of work for this project includes the following major tasks: • develop a work plan and worker health and safety plan for the BEA at the ARCO AM/PM Mini Market No. 3090; • advance two slant-drilled soil borings to a depth of 40 fbg with bottom hole locations beneath the east and west ends of the UST cluster, and four slant-drilled soil borings with bottom hole locations with bottom hole locations beneath the east and west dispensers on the north and south dispenser islands; • analyze soil (samples for TPH as gasoline, BTEX, MTBE, TBA, DIPE, ETBE, TAME, EDB, and 1,2-DCA; and • prepare a Baseline Environmental Assessment Report documenting the drilling activities, sample results, data analysis, conclusions, and recommendations for any further action that may be necessary. 58 IE 1400 Easton Drive, Suite 132, Bakersfield, California 93309 (661) 325-4862 — Fax (661) 325-5126, eensenv @aol.eom x Mr. Munther Hawatmeh June 21, 2007- Page 2 2. SITE DESCRIPTION: ARCO AM/PM Mini Market No. 3090 is located at 3333 Union Avenue, Bakersfield, Kern County, California (see Figure 1 — Site Location Map). The site is located in northeast quarter of the northeast quarter of Section 19, Township 29 South, Range 28 East, Mount Diablo Base and Meridian. The site is zoned C-2 for medium commercial use by the City of Bakersfield Planning Department. Commercial businesses flank Union Avenue and 34th Street. The site is an approximately 0.9-acre parcel developed with the 2,750 square foot market building and the retail vehicle fueling facilities (see Figure 2 — Aerial Plot Plan). The retail vehicle fueling facility consists of four 10,000-gallon double-walled fiberglass USTs and four multiple product dispensers (MPDs) on two dispenser islands (see Figure 3 - Plot Plan). 3. SITE MAPS: Site maps are included as Figures 1 through 3. 4. TOPOGRAPHY, GEOLOGY, AND HYDROGEOLOGY: The site is located at an elevation of 440 feet above MSL, and the topography slopes to the west, toward the ancient Kern and Buena Vista lakes (see Figure 1). The subject site is located on the eastern flank of the San Joaquin Valley and west of the southern Sierra Nevada. The surface of the San Joaquin Valley is composed primarily of unconsolidated Pleistocene (1.6 million to 11,000 years ago) and Recent (11,000 years ago to the present) alluvial sediments. Beneath the alluvial sediments are older, predominantly lake-bed deposits. These lie unconformably on Mio-Pliocene marine sediments, which extend to a crystalline basement at a depth of approximately 20,000 fbg. At the subject site, surface deposits consist of Quaternary (recent) unconsolidated alluvium overlying Quaternary (Pleistocene) nonmarine sediments. Geologic deposits in the study area include Pleistocene alluvial sediments that form a homocline dipping gently to the west-southwest. The deposits are alluvium consisting of indurated and dissected fan deposits (California Division of Mines and Geology, 1965, Geologic Map of California, Bakersfield Sheet). The alluvium consists of silty sands and fine-grained to coarse-grained sands, with intervals of finer grained, sandy silts and minor development of clay overbank deposits. Surface soils are classified by the Soils Conservation Services as Chanac loam with moderate permeability. The site is located in the southern portion of the San Joaquin Valley, with the Sierra Nevada Mountains 10 miles to the east, the San Emigdio Mountains 30 miles to the south, and the Temblor Mountains 40 miles to the west. In the region of the Kern Bluff Oil Field, the Tertiary, sedimentary sequence from top to bottom is non-marine Quaternary and Pleistocene Kern River Formation alluvium, marine Pliocene San Joaquin and Etchegoin formations, marine Upper Miocene Reef Ridge Formation, marine Middle Miocene Fruitvale Formation, marine Lower Miocene Round Mountain, Olcese, and Freeman-Jewett formations, marine Oligocene Vedder Formation, and marine Eocene Tumey and Kreyenhagen formations. The subject site is in an area of extensive plio-pleistocene faulting. These include the San Andreas Fault, 50 miles to the west. Oil is produced in faulted traps within the Kern Bluff Oil Field. Mr. Munther Hawatmeh June 21, 2007 - Page 3 The site is located in the southern portion of the Great Valley geomorphic province. The Great Valley is a north-south-trending valley, approximately 400 miles long by 50 miles wide, the southern portion of which is known as the San Joaquin Valley. Surface water and groundwater in the San Joaquin Valley are derived predominantly from the Sierra Nevada to the east and are transported by five major rivers, the closest to the site being the Kern River. The Kern River is located approximately one mile north of the site. The concrete-lined East Side and Kern Island canals are located 200 feet west of the site. The depth to the regional, unconfined aquifer is in excess of 150 fbg, and the groundwater gradient is to the southwest, toward the ancient Kern and Buena Vista lake beds (Kern County Water Agency (KCWA), 2005, 2003 Water Supply Report, May 2005). Perched groundwater at depths as shallow as 20 fbg is known to be present flanking the current course of the Kern River, one mile north of the site, but is not known to extend to the site (KCWA, 2005). No water wells are located on the site. There are several municipal water supply wells within a mile of the site. The groundwater is considered to be potable and suitable for beneficial uses. 5. TANK HISTORY: The site was developed in 1950 as a Standard Oil Company (Chevron) Service Station. The site was acquired by ARCO in 1973 and was redeveloped with the installation of two 10,000-gallon single-walled steel USTs, one 8,000-gallon single-walled steel UST, and nine single product dispensers (SPDs) on three dispenser islands. In 1988 the southern dispenser island was removed. In 1993, the fueling facilities were replaced by the four 10,000-gallon double-walled fiberglass USTs, four MPDs on two dispenser islands, and double-walled fiberglass product pipelines, which are present today(see Figure 3). 6. PREVIOUS WORK: In 1988 a petroleum release was discovered in association with remodeling of the dispensing facilities to remove the third (southern) dispenser island. TPH as gasoline and benzene were detected at maximum concentrations of 875 mg/kg and 32.55 mg/kg, respectively, in soil sample B-1-2', collected from 2 feet below the western SPD on the southern dispenser island. Based upon the laboratory results of the soil samples collected from beneath the SPDs, the Kern County Department of Environmental Health Services (KCDEHS) issued an Unauthorized Release Report (URR), dated April 41 1988, and required the performance of subsurface investigation activities (see Attachment 1 for a Summary of Previous Work). During 1989 and 1990, four soil borings were drilled to a maximum depth of 20 fbg in and around the area of the western SPDs on the central and southern dispenser island. TPH as gasoline and benzene were detected at maximum concentrations of 604 mg/kg and 0.67 mg/kg, respectively, in soil sample TB-3-10', collected from a depth of 10 fbg in the soil boring drilled adjacent to the western SPD on the central dispenser island. Based upon the results of a risk assessment that indicated a depth to groundwater of approximately 200 fbg, the KCDEHS issued the site a No Further Action (NFA) determination in its letter dated February 14, 1991. There is no record that cleanup activities were performed in association with this petroleum release (see Attachment 1). Mr. Munther Hawatmeh June 21, 2007- Page 4 In 1993 the fueling facilities were entirely replaced with the installation of the four 10,000-gallon double-walled fiberglass USTs, four MPDs on two dispenser islands, and double-walled fiberglass product pipelines, which are currently present. TPH as gasoline and benzene were detected at maximum concentrations of 11,000 mg/kg and 24 mg/kg, respectively, in soil sample T3E-2', collected from 2 feet below the invert at the eastern end of the southern UST. Based upon the laboratory results of the soil samples, the BFDHMD issued a second URR, dated August 12, 1993, and required the performance of additional subsurface investigation activities (see Attachment 1). From 1993 through 1995, ten soil borings were drilled to a maximum depth of 90 fbg in and around the area of the former USTs. TPH as gasoline was detected at a maximum concentration of 6,300 mg/kg in soil sample B-6-15', collected from a depth of 15 fbg in the soil boring drilled adjacent to the eastern end of the southern UST and benzene was detected at a maximum concentration of 10 mg/kg in soil sample B-10-55', collected from a depth of 55 fbg in the soil boring drilled adjacent to the eastern end of the southern UST. TPH as gasoline and BTEX were detected to a maximum depth of 80 fbg in the ten soil borings. Based upon the results of a second risk assessment, the BFDESD issued the site a NFA determination in its letter dated November 14, 1995. There is no record that cleanup activities were performed in association with the second petroleum release (see Attachment 1). Because the service station is within 1,000 feet of a public water well, an Enhanced Leak Detection (ELD) test was performed in September 2004 to evaluate both the liquid and vapor tightness of the fueling facilities. The secondary containment for two of the four USTs failed the ELD and a third URR was filed on September 27, 2004. Repairs were made to the secondary containment and the site passed an ELD retest. There are no records that BFDHMD has required the performance of any subsurface investigation or cleanup activities in association with this URR (see Attachment 1). Based upon the previous soil sampling, TPH as gasoline and benzene were detected at maximum concentrations of 875 mg/kg and 32.55 mg/kg, respectively, in the area of the dispenser islands and 11,000 mg/kg and 24 mg/kg, respectively, in the area of the former USTs, with TPH as gasoline and BTEX detected to a maximum depth of 80 fbg. There are no records of cleanup activities being performed, no records that soil samples have been analyzed for MTBE or other oxygenates and lead scavengers, and no records of any drilling and soil sampling being performed in the vicinity of the four existing USTs, which were installed in 1993. 7. STRATEGY AND PROCEDURES FOR CONDUCTING A BASELINE ENVIRONMENTAL ASSESSMENT: The intent of this work plan is to present the methodologies to be used to conduct a BEA at the subject site. CSE proposes to accomplish this by drilling six soil borings (B-1 through B-6) and analyzing soil samples for TPH as gasoline, BTEX, MTBE, TBA, DIPE, ETBE, TAME, EDB, and 1,2-DCA(see Figure 3 for the proposed soil boring locations). M' Mr. Munther Hawatmeh June 21, 2007 - Page 5 8. DESCRIPTION OF WORK TO BE PERFORMED: Prior to any intrusive methods being conducted at the site, Dig Alert(800-642-2444)will be utilized to map out the underground structures. Based on the clearances obtained, CSE will site the soil borings in safe locations. Drilling A total of six soil borings will be advanced during this BEA. Two soil borings (B-1 and B-2) will be slant-drilled to 40 fbg to bottom hole locations beneath the east and west ends of the fuel tank cluster and four soil borings (B-3 through B-6) will be slant-drilled to 20 fbg to bottom hole locations beneath the east and west MPDs on the two dispenser islands (see Figure 3). Soil samples will be collected at 5-foot intervals. During the drilling process, soil cuttings, as well as each soil sample, will be field- screened for VOCs using a PID calibrated to 100 ppmv isobutylene, and observations will be made for the visual identification of any soil staining or discoloration. Soils will be classified according to the Unified Soil Classification System by an experienced environmental geologist under the direct supervision of a State of California registered geologist, and all data will be recorded on logs of exploratory borings. Soil samples will be wrapped in Teflon TM, followed by close-fitting plastic caps, and held at a temperature of 4°C while in the field and in transit to the laboratory. Soil sampling equipment will be decontaminated between sampling attempts using a non-phosphate, soap and water wash; a tap-water rinse; and a distilled, deionized water rinse. Upon the completion of drilling the soil borings will be backfilled with cement and bentonite grout and the asphalt surface patched (see Attachment 2 for the Soil Boring and Sampling Procedures). Chemical Analysis of Samples The soil sample from each soil boring exhibiting the highest concentration through field screening using the PID will be submitted for laboratory analysis. The samples will be submitted to a California certified laboratory where they will be analyzed for TPH as gasoline using EPA Method 8015 (M), and BTEX, MTBE, TBA, DIPE, ETBE, TAME, EDB, and 1,2-DCA using EPA Method 82608. Report Preparation Upon completion of the'site assessment activities, a BEA Report will be prepared, which will be sent to BFDHMD and BP. The report will contain a summary of the sampling activities, required permits, a site map showing sample locations, description of methodologies used, certified laboratory reports and chain-of-custody documents, conclusions, and recommendations. 9. EQUIPMENT DECONTAMINATION PROCEDURES: Sampling equipment will be decontaminated using a non-phosphate, soap and water wash; a tap water rinse; and a distilled, deionized water rinse. The drill augers will be pressure washed between sampling locations. Plastic sheeting will be placed beneath the drill rig during drilling activities to prevent hydraulic fluids and lubricants from impacting the surface at the site. The contractor shall clean rigs, equipment, tools, and materials before leaving 1 * Mr. Munther Hawatmeh June 21, 2007 - Page 6 the work area to such a degree that will prevent site-derived materials from spreading outside of the work area. 10. WASTE DISPOSAL PROCEDURES: All drill cuttings and sample spoils that exhibit discoloration, odors, or elevated field-screening readings will be segregated and containerized in 55-gallon, Department of Transportation (DOT) - approved drums pending laboratory analytical results. Uncontaminated soil cuttings will be used as grading fill at the site. Munther Hawatmeh will arrange for the rinsate and impacted drill cuttings to be disposed of off-site at an appropriate licensed facility. 11. EMERGENCY OR INTERIM CLEANUP: Not applicable. 12. WORK SCHEDULE: Work will begin within 5 days subsequent to the acceptance of this work plan by the BFDHMD. The BFDHMD will be notified at least 48 hours before any on-site work commences. A Baseline Environmental Assessment Report will be submitted to the BFDHMD approximately 30 days after commencement of the work. 13. SITE SAFETY PLAN: A worker health and safety plan developed by CSE for UST site investigations outlines the procedures for conducting all on-site work. Site-specific information is provided on the cover page of the worker health and safety plan (see Attachment 3 for the Worker Health and Safety Plan). All work will be conducted in accordance with all regulatory requirements as defined by the California State Water Resources Control Board's LUFT Field Manual and the BFDHMD guidance documents. Mr. Munther Hawatmeh June 21, 2007 - Page 7 Central Sierra Environmental, LLC, trusts that you will find this Baseline Environmental Assessment Work Plan to your satisfaction. If you have any questions or require additional information, please contact Mr. Mark R. Magargee at(661) 325-4862 or at e-mail address censenv @aol.com. Respectfully submitted, DER D Mark R'' Magargee, PG, CH No�$ Consulting Hydrogeologist Central Sierra Environmental, LLC. MRM/jlt Enclosures: Figure 1 - Site Location Map Figure 2 - Aerial Plot Plan Figure 3 - Plot Plan Attachment 1 - Summary of Previous Work Attachment 2 - Soil Boring and Sampling Procedures Attachment 3 - Worker Health and Safety Plan Appendix 1 - Material Safety Data Sheet cc: Mr. Howard Wines III, BFDHMD Mr. Jack Oman, BP Ms. Jenine Hinkle, BP TOPO! map printed on 06/21/07 from "Untitled,tpo" 119001,000, w WGS84 119000.000' W 6 251 4� 10'Ll --1116 . 7 A �j 24 a A ? z O 0 (D FOUR C� �/ 0'7 �-7 0 No "fit LO (Y) v COA Palk 'Dau;zy Museum SITE LOCATION n', -Ldh fell g t N MY --T.-bt INN T z z A 0 O 0 —2 - JAI N :�d jum 0 Lo (Y) �-Oh 424 -430 MR. 1 32 !241 ts On MIER :a-+. . .............. C Vmil ............ 119001,000, w WGS84 119-00.000- W T11 'M11 0 •5 — I MILE 140 ZT0 1Ekf 0 low IMI(TERS Map created with TOPOND @2003 National Geographic(w-ww.nationalgeographic.cortvtopo) LEGEND MR. MUNTHER HAWATMEH ARCO AM/PM MINI MARKET NO.3090 3333 UNION AVENUE BAKERSFIELD, CALIFORNIA N FIGURE 1 - SITE LOCATION MAP USGS OILDALE 7.5 MINUTE SERIES QUADRANGLE CENTRAL SIERRA ENVIRONMENTAL, LLC ��- �^ s�r���� �/',�,�,�y"�•v. ��d fig' 4�� . �� f�":� vt t i �,,,.�1.,.'�' ax 4 - "'x't;; a,. _,�,'� lh � -.fi K�? �`�;��!h-a��r uh`�t�X+q�av���r r, �r ��-•,,,a '°'a"y �.f"r,.f v ..; :.c.*r�a'�a,'ri'+'��#'.se �a�t .� '"� �w;,tY.• �„' :_5. _ aakk"gt� g, ^ 34th STREET a. fi A•a�aY ��� �����s Zr F f� y�ty��r ; �- ::•.r "H ,� Nr,���� � `r i rte` + ✓'`" i' %�.'� - i� �e "''tf' z �c w i G a A a E ,, m � � CANOPY :tr t AND : � a DISPENSER . ,w � ., '�i .. 3 6. '� � _�,! •: ```'''�Sys'•+i ,.p�Ye � �ti".i � ,.f � EXISTING USTS��FORMER US X ' 0--l-®r�- a�;, a"'r.�• � d �+ �4�..x"�' R t� �x t�1 -��' Ke "� ''�`�'ui t"`�r -`su1 t�4 4 •. „. f >� s :''i`,�,- k" �'? 3"4!' Lu MINI i � t O r �•, i 'r IMARKETI = r ti k� H '�} :.'. 3 a,;7- r �S,Est r, - w ;-�+ ii 4 ,,..fi' .i �t� .n.�tx-m�'x?.a?.a'" w- �- '� �,�•�.x x .;y ll 045-6 ai d+SS., k 51}+ i g n ; �" .. '� rr" �� ��} rid`i 'fk'ti"r � nun .'!. #,� �+<".fE��� ����sa.a4�;,1,�°ct• .��+ L 4"�l•#"x.� ,!�J;�J�� , ct �� LEGEND MR. MUNTHER HAWATMEH ARCO AM/PM MINI MARKET NO.3090 3333 UNION AVENUE BAKERSFIELD, CALIFORNIA FIGURE 2-AERIAL PLOT PLAN CENTRAL SIERRA ENVIRONMENTAL, LLC 3 a i I "Yma owltdf _ IOrOY,yY JMIf4U._ � w•o+1aY 0 t Y + 1 ♦ tlr115d7 Y 7 1 Y • 1 A tltl OJt/+ E,,,4y�I.r .O JNII SIYI � I.O�I Ylt NVIY l� Y low P JruSSI � d B-4 X lN3n3SV3 B-6 .0—.0 V rvw+INgJ B_7 - p+YOli 7 ' rlt rr B-1 �" z 4 < CD �yp� 7A wti t t`•-t•�•f• f St7 A l a3dOad ' Il..} 03AOadYllNn •i i w1Y �''^ +� IN/KODN} ��•���� Jlli 1) I Intl � ! JMISRI - rn.+,t' - I,w SDatlE JNI SnII 7, ,svJ Y ]111 Rt^ I Q trove +„ p•etSdt 333 90t — b anoalru as nv� 11rsn v7ln ��_Y u}. �lll I x]011 7rOJ •YICr}ACA tlL♦Y JMItd} JNItd} Yll1/A�YlV JMISd} �LL 1 � i LEGEND MR. MUNTHER HAWATMEH PROPOSED SOIL BORINGS ARCO AM/PM MINI MARKET NO.3090 3333 UNION AVENUE BAKERSFIELD, CALIFORNIA FIGURE 3-PLOT PLAN CENTRAL SIERRA ENVIRONMENTAL, LLC y ATTACHMENT 1. SUMMARY OF PREVIOUS WORK &60 d 3,1 1-- ,�.cce4 n I j Mr•I -- ZLA r ►N' E " t15 REMWE EAST '.?-IMP r-----!X:57:t4G C01¢. i offer'_. �c•tc 1u.6� I I ISV�nO".•S _V._L ,(A ! p(I;bES4,3 To'lE!MIN s�Noltl°/� OISTAXDAW5.o i�Tal i , _ ``' Ap1AGEhi1. DISTP+G PUMP!SLAT+D--1 • i -;::p1�:8.- G °.a�;:2 I .j c W C"' T :o(lfpNlN It �I r --- -------- �_ ---- �- lu F—SN-D CZLNTEi1 I I �p_' _ �`+ %% \\ I�I I `. 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M AT '?O'E4agti';F�.sx N A pO lei i NN , �- NE fi4ltl(I,lly fscES'qq'.9•w,y �) cx 57,16 �c%l'�i Ems\--�--- - `� -.� i '�/ RE1✓�'1C" V_ /.d• �>LZI•�ILILC I 4.T-=2 v . FxIST. APti�na�M rAISTI SIO KK �x� E9 CIS I!:G�P°!41U1 t�. 9 /.S PhEC� N 0 R T 'H U N 1 0 N A V E • pee "fie ia'= A�w LAM E:^ b [DSme .vwo•a Ent. [nsTwc .•avo.a b aa ^ gds• I N V5l I mn: a4L�I a a W 1 I C JD D I ra N I DD OOI C Q 0 a o I v, ajo Blm z I 1 ' I ° V C I r o; I I D I 1 —°—— R F o� •-------•-------------------------------•------•--- 1 aay x rn 4 y C7 r1 Z O Z o v [o 1 1 SITE PLAN (AS BUILT) ARCO Products Company (ID o�.:.rw.�uawnes:erw(.wewe 5 UNION AVE 0 34 TH ST Retai!Marketing • Design 8 Engineering. t BAKERSFIELD CA 1055 West Sevevth P.O. BOX 2570,Los Angeles. CA. 90051-0570 N O R T H U N 1 0 N A V E Ax i�' _ s,� postut—wwo.o I wsn+e r WN.L. i/ eosewe wA•o.a a lAll! - HE • " M, ♦P€` I 1^� tN �•p Rn i Itp - ® g_t 'EE 1:E'.4EEE'.E'T:l•: It Ax I N . - � m I ' I eoe®oeeoee ee see e e j,� � x r r 3 i 1'1!rrt � re•r 1 1111+l+1f�{l lit}U ,if I rrjt �r {,y� .4�j;� � ,, t!��l�thrl it 1.i::��i:. 1 +�;il� •��t'. i a M y.;B 1} ! Ef i i it g° `� !`i;�6ii,rJ1�ii�� •��!!'S� i t9i��}t�;` i! F ILA � sib r1rS;ILi:�141 ; 1ir"i ;i::: a c D 1 +I ♦ {1 l) ��1 1 1`.! ijf�r.)i 11� •t�i� + I��y`i I {' 6 i s1�i.rt ,tI �r.: ��� ! Iq Ir�r }i►�+ 1•'`i �hll1 _ �. ......, e5. l`, 1 i;�i�•1 1 } j p' 4:i•�•�' ' ! irt:ri I'+! '1 if p 14i I SITE PLAN — TANK REPLACEME:: AR':O Products Compar- CD 3333-UNION AVE O 34 TH ST Reta6 Merheft' • Deem i-Env:,eer, I ?=+ SAKERSiIELD CA' 1055'West.SsiLit ` P.O. BOX 25M tics.Angeles,'CA- 80051-0576 ► I ® V-1 I V-1 (7.5') I ♦ V_7 8 � I o e FORMER I h PUMP ISLAND 1 i--- r ♦ V-2 �a 9. B-1 ♦ V-6 ` I I ' � J 4 i ♦ V-3 ♦v-4 ♦V-5 m ° ♦ v-8 a 0 TM LEGEND U ♦ VZV ®PROBE LOCATION; V-1 (7.5') 0 5 INDICATES SOIL SAMPLE ALSO TAKEN AND THE DEPTH SAMPLED Feet AT. ° SOIL SAMPLE LOCATION, MARCH 17, 1988 SITE EXPLORATION PLAN ARC® Station #3080 Bakersfield, CA 0 M c C L i L L A " ° a a a 8 PLATE 1 f M 8 R1 c Sample Organic Vapor VZV® No. Sample No. Depth, ft Concentration, ppm* Remarks VZV-V-1 1 2 0.5 Draws vapor easily VZV-V-1 2 4 25 Draws vapor easily VZV-V-1 3 6 20 Draws vapor easily VZV-V-1 4 8 750 Draws very slowly VZV-V-1 5 10 1100 Draws well VZV-V-1 6 . 12 1100 Slow/no draw I VZV-V-1 7 16 1300 Slow/no draw VZV-V-1 8 18 1100 Refusal VZV-V-2 1 2 90 Good draw VZV-V-2 2 4 ,`, Q 320 Good draw VZV-V-2 3 6—� S 700 Good draw VZV-V-2 4 8 —— 1500 Good draw VZV-V-2 5 9.5 920 Refusal ------------------------ *NOTE: Detection Limit = 0.5 ppm. SUMMARY OF VZV® SOIL GAS TEST RESULTS ARCO Station No. 3090, BAKERSFIELD McClelland Engineers PLATE 2a 81608A/D-1 a Sample Organic Vapor VZV® No. Sample No. Depth, ft Concentration, ppm* Remarks . VZV-V-3 1 2 20 Good draw VZV-V-3 2 4 4 Good draw I VZV-V-3 3 6 3 Good draw VZV-V-3 4 8 6 Good draw VZV-V-3 5 10 8 Good draw VZV-V-4 1 3 @ No draw VZV-V-4 2 6 2 Very low draw VZV-V-4 3 9 4 Very low draw VZV-V-5 1 3 @ No draw VZV-V-5 2 6 * No draw No draw from 5.5 ft to 14 ft VZV-V-6 1 3 2 VZV-V-6 2 6 12 Very low draw VZV-V-6 3 9 14 Very low draw ------------------------ *NOTE: Detection Limit = 0.5 ppm. @ - No data SUMMARY OF VZV® SOIL GAS TEST RESULTS ARCO Station No. 3090, BAKERSFIELD McClelland Engineers PLATE 2b 81608A/E-1 Sample Organic Vapor VZVe No. Sample No. Depth, ft Concentration, ppm* Remarks VZV-V-7 1 3 4 VZV-V-7 2 6 7 VZV-V-7 3 7.5 12 VZV-V-8 1 3 7 VZV-V-8 2 6 6 I VZV-V-8 3 9 7 VZV-V-9 1 4 5,000 to 10,000 Diluter malfunction, OVA reading estimated VZV-V-9 2 5 5,000 to 10,000 Diluter malfunction, OVA reading estimated VZV-V-9 3 10 3 Very low draw No draw at 6 ft, 7 ft, 8 ft, 9 ft. ------------------------ *NOTE: Detection Limit = 0.5 ppm. SUMMARY OF VZV® SOIL GAS TEST RESULTS ARCO Station No. 3090, BAKERSFIELD' McClelland Engineers PLATE 2c 81608A/F-1 Total Petroleum Hydrocarbons BTXE, in ppm (EPA 8020) (EPA 8015) Sample ID Feet in ppm Benzene Toluene X lens Benzene I V-1 (7.5) 7.5 ' ``,. ND ND ND ND ND V-2 (6) 6 C.3L J ND ND ND ND ND i V-2 (8) 8 _ ND ND ND ND ND i Detection Limits 0.10 0.10 0.10 0.10 0.10 ------------------------ Analysis by BC Laboratory, Bakersfield LABORATORY CHEMICAL TEST RESULTS ON SOIL ARCO Station No. 3090, BAKERSFIELD McClelland Engineers PLATE 3 ` 81608A/G-1 I PLANTER 8}= 1 i EXTENT OF FORMER T8-4 EXCAVATION W EXPLANATION TB-2 BUILDING •TB-1 • • LOCATION OF TEST BORING • T--• TB-3 0 A PLANTER J j I a B-4 Qo g_) ® PREVIOUS SOIL SAMPLING LOCATION &N g_2 N g_S a A I B-B � L J o B-6 B-9 A B-10 a PARKING 0 10 20 40 FEET TRASH i 11 I I SCALE BIN I 11 II UNDERGROUND STORAGE TANKS II �I 1 1 II II I 1 11 1 II I PLANTER I PLANTER PLANTER BORING LOCATION MAY ARCED STATION 3090 UNION AVENUE 3333 UNION AVENUE BAIENSFIELD. CALIF MIA REFERENCE: PROVIOEO BY CLIENT I DRAAAsy: E$ 1 DAT& /sr/t• /A0,AWIM 0480-04 Sao ov:a w5l mvr0: I/II/to 1 DWSA., FIGURE 2 C- NOTE: CROSS-SECTION EXTENDS 109' BEYOND PROPERTY LINE vLgNTER Z3-- 1 ® I i I � I TB-4 W EXPLANATION m 1 � C' N TB-1 TB-3 ® LOCATION OF TEST BORING BUILDING a TB-2 r^ B-4 1 PLANTER 1 B-1 i c B-7 C A PREVIOUS SOIL SAMPLING LOCATION � I � 4 a a i•i B-2 s • B-5 C • g_g / Q � 1 I w 1 IB-3 L J � • 8-6 � • B-9 •8-10 1 n PARKING I 0 10 20 40 FEET r__f�--it--� TRASH I II II I SCALE BIN I II I. I UNDERGROUND STORAGE TANKS I II II L__Jj II I 1 II I I II i PLANTER I PLANTER / PLANTER —_ _-/// �I• CROSS-SECTION INDEX MAP ARCO STATION 3090 3333 UNION AVENUE 1 UNION AVENUE BAKERSFIELD, CALIFORNIA REFERENCE: PROVEIDED BY CLEINT ORASNST: ES DATE: /z t/+• M0_.0480-062 cHRID nEVU[o orawo_ FIGURE 5 S 1 C ImII laol m a45) ImII °~° C' ND gip.' v `726.4 SILT, CLAYEY �• F.. SILT :: .784I NO NO ND CLAYEY, ND SILTY EXPLANATION Sano ND No — — �,P�'� CLAYEY, SILTY SAND AREAS WHERE PLANS INDICATE P PRODUCT LINES LOCATION NO TPH NOT DETECTED u fPH CONCENTRATION IN wkq I , • J BORINGS COMPLETED BY B_4 PREVIOUS CONSULTANT 1 D- —— LITHOLOGIC CHANGE AREA OF SOIL CONTAINING TPH AT A CONCENTRATION Ij EXCEEDING 100 mg/kq VE NIICAL SCALE INCH =EET ' HORIZONTAL SCALE i INCH = ;J FEET CROSS-SECTION C-C'-C• ARCO STATION 0 3090 I UNION AVENUE AND 34TH STREET 8AKERSFIELD, CALIFORNIA DRAWN BY: Es I DATE: Yc I PMACT ND:0480-062 cm'DEr: MM I REVISED: I DwOND: FIGURE 6 BTXE, in ppm (EPA 8020) Total Petroleum Hydrocarbons Total Ethyl Sample I.D. Feet (EPA 8015) in ppm Benzene Toluene Xylenes Benezene B-1 2 44 3 879 32.55 153.33 173.98 25.23 6 7 37 8 3a 4.45 13.52 65.20 7.61 B-2 2 ND ND ND ND ND 6 ND ND ND ND ND B-3 2 ND ND ND ND ND 6 ND ND ND ND ND B-4 2 13D ND ND ND ND 6 -fl¢r1.�2 1013 0.26 3.13 22.06 1.98 B-5 2 ND ND ND ND ND 6 ND ND ND ND ND B-6 2 ND ND ND ND ND 6 ND ND ND ND ND B-7 2 ND ND ND ND ND 6 ND ND ND ND ND B-8 2 ND ND ND ND ND 6 ND ND ND ND ND B-9 2 ND ND ND ND ND 6 ND ND ND ND ND B-10 2 ND ND ND ND ND 6 ND ND ND ND ND ----------------- ------- ------- ------- ------- Detection Limits: 0.10 0.10 0.10 0.10 0.10 LABORATORY CHEMICAL TEST RESULTS ON SOIL ARCO Station 3090, Bakersfield 81608A/B- Plate 2 TABLE I Results of Laboratory Analysis Performed an Samples Collected by McClelland Engineers ,' .. ... Total Wa�rolwrt� SampFs Hyelcarbans Banrart� Tolwrta Ethy117tsM Xr(irt� Numt .�pth( l Em siE ( ►g/ 93.....:: Im91 4)....:;. E f # ,::.. {!�"�/ksI B-1 2 445.13 33.55 153.33 173.98 25.23 6 784.37 4.45 13.52 6520 7.61 B-2 2 ND<0.10 ND<0.10 ND<0.10 ND<0.10 ND<0.10 6 ND<0.10 ND<0.10 ND<0.10 ND<0.10 ND<0.10 ' B,3 2 ND<0.10 ND<0.10 ND<0.10 ND<0.10 ND<0.10 6 ND<0.10 ND<0.10 ND<0.10 ND<0.10 ND<0.10 B-4 2 ND<0.10 ND<0.10 ND<0.10 ND<0.10 ND<0.10 6 161.92 0.26 3.13 22.06 1.98 B-5 2 ND<0.10 ND<0.10 ND<0.10 ND<0.10 ND<0.10 6 ND<0.10 ND<0.10 ND<0.10 ND<0.10 ND<0.10 8-6 2 ND<0.10 ND<0.10 ND<0.10 ND<0.10 ND<0.10 6 ND<0.10 ND<0.10 ND<0.10 ND<0.10 ND<0.10 8-7 2 ND<0.10 ND<0.10 ND<0.10 ND<0.10 ND<0.10 6 ND<0.10 ND<0.10 ND<0.10 ND<0.10 ND<0.10 B-8 2 ND<0.10 ND<0.10 ND<0.10 ND<0.10 ND<0.10 6 ND<0.10 ND<0.10 ND<0.10 ND<0.10 ND<0.10 B-9 2 ND<0.10 ND<0.10 ND<0.10 ND<0.10 ND<0.10 1 6 ND<0.10 ND<0.10 ND<0.10 ND<0.10 ND<0.10 B-10 2 ND<0.10 ND<0.10 ND<0.10 ND<0.10 ND<0.10 6 ND<0.10 ND<0.10 ND<0.10 ND<0.10 ND<0.10 V-1 7.5 ND<0.10 ND<0.10 ND<0.10 ND<0.10 ND<0.10 V-2 6 ND<0.10 ND<0.10 ND<0.10 ND<0.10 ND<0.10 a ND<0.10 ND<0.10 ND<0.10 ND<0.10 ND<0.10 i i 0480.062-201 TABLE 3 Results of Analysis for Samples Collected On October 4, 1989 and October 3, 1990 ................ .. . ......... XxNno .. ......... Owl., v TB-1-15 15 ND<5 ND<0.02 ND<0.02 ND<0.02 ND<0.02 TB-1-20 20 ND<5 ND<0.02 ND<0.02 ND<0.02 ND<0.02 TB-2-10 10 ND<5 ND<0.02 ND<0.02 ND<0.02 ND<'0.02 TS-2-15 Is ND<5 ND<0.02 ND<0.02 ND<0.02 ND<0.02 TB-3-10 10 604 0.67 2.13 3.26 19.40 TB-3-20 20 ND<5 ND<0.02 ND<0.02 ND<0.02 ND<0.02 TS-4-5 5 ND<I ND<0.50 ND<0.50 ND<0.50 ND<0.50 TS-4-10 10 ND<1 ND<0.50 ND<0.50 ND<0.50 ND<0.50 TB-445 15 ND<I ND<0.50 ND<0.50 ND<0.50 ND<0.50 04804X2-201 Sheet I of 3 ENSR CONSULTING & ENGINEERING SUBSURFACE EXPLORATION LITHOLOGIC LOG OF 9-1 Client : ARCO Station 3090 DRILLING AND SAMPLING INFORMATION Project Name : Site Assessment Date Started : 10-02-89 Date Completed : 10-02-89 Project Location 3333 union Avenue. Bakersfield. CA Method : t1SA Total Depth : 23 Feet Job Number 0480-062-,000 Boring No WELL COMPLETION INFORMATION Logged By : A. Marrow Screen DIG length Approved By : K. Pitchford, C.E.C. Slat.Size : Type : Drilled By : Consolidated Testing Casing ON Length I Y DESCRIPTION _ 391- " �P=° W 09 pO c7 C J SURFACE ELEVATION : 410 Feet 0 - 8 aggregate base and asphalt ' Sandy Clayey SILT (SC\SM) light brown, moderately dense damp. no odor 5 SILT (ML) light brown, dense, dump, no odor 5 SS 1.2 r 30 9: ' IO Clayey SILT (ML) light brawn, moderately dense, damp, no odor 10 1.1 1 9: lower 3' gravel 5 cm diameter quartzite 111 15 gravels Interbedded with clay layers ' Silty course clayey SAND (SC\SM) with gravel up to 5 cm in 15 SS 1.2 S 28 9:4 diameter, moderately dense, damp, no odor 20 continued SC\SM with gravel 20155 1 L 11 5 15 ' attempted to sample at 23 feet sampler bounced 25 from refusal could not drill ahead T.D. 23 feet no groundwater encountered 30 ' 35 40 45 50 ' 55 SAMPLER TYPE BORING METHOD SS — DRIVEN SPLIT SPOON RC — ROCK CORE HSA — HOLLOW STEM AUGER DC — DRYING CASING ST - PRESSED SHELBY TUBE Cr - CONTINUOUS TUBE CFA - CONTINUOUS FUGHT AUGERS MO - MUD DRILLING i EmuSheet , of ENSR. CONSULTING & ENGINEERING SUBSURFACE EXPLORATION LITHOLOGIC LOG OF. B-2 Client : ARCO Station 3090 DRILLING AND SAMPLING INFORMATION Project Name : Site Assessment Date Started : 10-02-89 Date Completed : 10-02-89 Project Location .: 3333 Union Avenue. Bakersfield. CA Method : MSA Total Depth : 21 feet .lob Number : 0480-062-000 Boring No 8-2 WELL COMPLETION INFORMATION Logged By : A. Marrow Screen Dia Length Approved By K. Pitchford. C.E.G. Slat Slze Type Drilled By : Consolidated Testing Casing Dio Length W DESCRIPTION Z J,yW c W ra SURFACE ELEVATION 410 feet v, 0-8' aggragate base and asphalt SILT (ML) light brown, damp, moderately dense, no odor 111 111 5 7 SILT (ML) light brown, very dense, darn P. no odor s Ss 1.s a 1:2 111 111 111 to SILT (ML) tight brown, moderately dense, damp, no odor, 10 SS 1.5 R 5 1:3 111 i 111 i 111 ' t5 SILT (ML) light brown, moderately dense, damp. 151SS11.11 A 0 1:4 111 bottom 2` gravel 4 - 5 em in diameter I 111 20 continued '(ML) with gravel 20 SS 0 1 R 0 2'1 ° No recovery at 20 feet (rock fragments in sampler) Auger refused at 21 feet ' T.D. 21 feet 25 No groundwater encountered 30 35-� 40 45 50 I 55 7 :AMPLER TYPE SORNG METHOD SS - CRlv£N SPLIT SPOON RC - ROCK CORE NSA - HOLLOW STEM AUGER DC - DRIVING CASING jr - PRESSED SHELBY TUBE Cr - CONrWIJOUS TUBE CFA - CONTINUOUS FLIGHT AUGERS MD - MUD DRILLING Sheet I of 1 ENSR CONSULTING & ENGINEERING SUBSURFACE EXPLORATION LITHOLOGIC LOG OF. B-3 Client : ARCO Station 3090 DRILLING AND SAMPLING INFORMATION j Project Name : SITE ASSESSMENT Date Started 10-02-89 Dote Completed : 10-02-89 Project Location 3333 Union Avenue. Bakersfield. CA Method : MSA Told Depth : 22 feet Job Number : 0480-062-000 Boring- No : 8-3 WELL COMPLETION' INFORMATION Logged By : A. Morrod Screen Dia Length Approved By : K. Pitchford, C.E.G. Slot Size : Type : Drilled By : Consolidated Testing Casing Did Length W DESCRIPTION �Z W � o 2 W � w V F a.J r a ail 2 SURFACE ELEVATION : 410 feet C„ aWC Asphalt and aggragate base top 6 Silty fine SAND (SM) blue - green, damp, no odor, sheen in headspoce 5 7 ' Sandy fine SILT (ML) blue - green, loose, damp, 5 SS 1.2 "' 7 Il 55::: hydrocarbon odor ' 10 Clayey silty SAND (SC\SM) light brown, damp, loose, 101 SIS 1.1 �z {Dd 3: very strong gasoline odor gasoline odor in cuttings - ' t5 Clayey silty SAND (SC\SM) tight brown, damp, moderately dense, 15 SS 1.2 :qR 7 3:2 •. hydrocarbon odor, minor grovel 3 cm wedged in sampler gravel in cuttings - r20 poorly graded SAND (SP) some sits and gravel, damp, slight 1.0 =' T.D.'22 feet no groundwater encountered 25 30 M 3S� r 40 45 ' 50 r js J SAMPLOR TYPE BORING METHOD SS - CRlvN SPOT SPOON RC - ROCK CORE MSA - -GLLOW STEM AUGER OC - -RMNG CASING ;T - PRESSED SHELBY TUBE CT - CONTINUOUS TUBE CFA - CONTINUOUS FLIGHT AUGERS MO - MUD ORILUNG 1 INK Sheet lot 1 1 ENSR CONSULTING & ENGINEERING SUBSURFACE EXPLORATION LITHOLOGIC LOG OF B-4 Client : ARCO DRILUNG AND SAMPLING INFORMATION 1 Project Name : SITE ASSESSMENT STATION # 3090 Date Started : 10/2/90 Date Completed : 10/2/90 Project Location : 3,333 UNION AVENUE. BAKERSFIELD. CA Method : MSA Total Depth : 20 FEET Job Number : 0480-062 Boring No : 9-4 WELL COMPLETION INFORMATION Logged By : A. MORROW Screen Dia Length Approved By M. DONOVAN, R.G. Slot Size : Type : Drilled By : CONSOLIDATED TESTING Casing Dia Length is DESCRIPTION psi SURFACE ELEVATION . 410 FEET, U.S.G.S. OILDATE. CA Asphlt and aggragate base tap 6 Silty fine SAND (SC\SM) red to brown, damp, firm, ' no stain or odor 5 5 SS 1.5 3 ZO CLAYEY SILTY SAND (SC\SM) red to brown, dry, ' hard to dense, no stain or odor III t1� 10 same as 5 to 10' with 3 to 596, 1.5 pebbles 10 SS 1.5 ' granodiorite/granite ' III 15 met refusal at 20' attempted sample 1 SS 1.5 501• 4 1111 , ' retrevial but recovered nothing oil 20 20 SS 0 50+ - 4 I Bottom o boring a feet. No groundwater encountered. 25 30 ' 35 i 40 45 1 50 1 55 SAMPLER TYPE BORING METHOD SS — ORNEN SPLIT SPOON RC — ROCK CORE NSA — HOLLOW STEM AUGER DC — DRYING CASING ST — PRESSED SHELBY TUBE CT — CONTINUOUS TUBE CFA — CONTINUOUS FLIGHT AUGERS NO — MUD DRILLING 1 - 1 N _ 3gth SI DEWgLK ST REST --PPROgCH PLANTER -- f 780 D2 x PLANTER 18 PUMP x = ISLANDS a ' 2,000 � x 11 a 2,000 2.2 a- x' x 3,640 EASEMENT W 1 x ,700 W - --1 L_ C�. Tl--_ ��d0 — T2 x� a v� 1,800 L______ 3 r - 73 7,900 J '^ -- N S 11 000 t 9,200 � FORMER UNDERGROUND GASOLINE ' STORAGE TANKS = ARCO STATION v BUILDING 0 NO. 3090 a TRASH LEGEND ENCLOSURE — - - — PROPERTY LINE ' 4.1oo-, -TPHG CONCENTRATION IN 2-FOOT SAMPLE 11'800 SAMPLE LOCATION I -TPHG CONCENTRATION IN 6-FOOT SAMPLE ' NOTE: NONDETECT SAMPLES ARE NOT ANNOTATED. N/S = NO SAMPLE i EIG ROUNDWATER 0 FEET ao TPHG IN SOIL TECHNOLOGY SCALE CLIENT: FILE: PROJECT NO.: PM PE/RG ' ARCO PRODUCTS COMPANY C:\ARCO\3090\SM 022504584 ARCO FACILITY NO. 3090 REV. LOCATION: 1 FIGURE: 34TH STREET AND UNION AVENUE DES. DET. JDATE: 7 BAKERSFIELD, CALIFORNIA JP AJK 8/11/93 I i ' XI X2 X3 X1 ' ( S P 2 0 X2 Xg 16 6 ' 21 X2 X3 X� X XB X15 X 9 14 ' So X4 X11 x 1 SP X12 X13 1 2 ' X3 SP5 X X3X X SP4 SP6 X4 X ' 1 X X2 X3 0 XI 2 ' SP7 X i 1 � I . i EE GROUNDWATER SOIL PILE SAMPLES TECHNOLOGY CLIENT: FILE: PROJECT NO.: PM PE/RG ARCO PRODUCTS. COMPANY C:\ARCO\3090\SM 022504584 ARCO FACILITY NO. 3090 REV. LOCATION: 1 FIGURE: 34TH STREET AND UNION AVENUE DES. DET. DATE: 6 BAKERSFIELD, CALIFORNIA JP AJK 8/11/93 DE 5' 0' 5' 20' 38.5' 47.5' 50' 55' 6 ' 70 75' TP 210 <1.0 <1.0 <1.0 <1.0 :SL <10 <1.0 <1.0 <1.0 <1.0 <1.0 34th STREET H <O:ID <0:°2 <O 02 <0.02 <OB:D2 <0.02 <O.02 <°:02 <D:o2 0:080 <°:02 <0.09 B 0.21 <0.02 <0.02 <0.02 <0.02 70.02 70.02 SO.OZ 70.02 70.02 <0.02 <0.02 x <0.30 <0.02 <0.02 10.02 70.02 70.02 70.02 70.02 70.02 0.13 1002 <0.02m. Sidetralk - - Approach I Planter I ' D 0' 15 2 ' 0' 4 0' 55' 71.0 I Boo 1,200 1 500 450 <1.0 <1.0 <1.0 I Planter B 70.02 70.02 0.30 70.02 70.02 70.02 <0.02 70.02 70.02 1 f<0.02 <0.02 010 O B 70.02 27 31 18 1 3.0 70.02 <0.02 <0.02 I ' x <0.02 200 190 120 22 .053 <0.02 .032 OEM I 5' 10' 15' 0' 25' 30' 35' 40' Pump Islands 0 0 5 0 0 < 0 < 0 510 710 0 W A NAA .03 NA NA Na NA 70.380 Bel 1 ' ' B NA NA 4.0 NA NA NA.Lt .008 (Angle) fs]NA A 6B NA NA NA .012 C 9 2 1 Q TP < 0 <10 <10 <10 <10 I z B A NA 0.00 NA 0.00 I NA o_oo A o.OD ( B2 1 or z NA I NA 1<0.0151 NA tCO.01 - 0 1 'mod I L DZ TP <1 0 6 300 1 500 1.500 1.200 680 380 3400 310 I B3 L o B (B7 ' 70.02 2.3 0.7 70.02 <O.OZ 1 0.11<0.02 O.D661 0.0931 --- < . 1 .0 o B10 <0.02 270 83 31 5 0 9.8 8.5 6.4 <0.02 1 ADC 45 42 1 BI 6 0 0 TP <10 I <10 2,100 1 Boo 1 900 2_z00 1-1&01 1 000 H9 NA NA NA NA NA O.BZ NA 0.55 Brj A I NA 1 4 E NA I NA NA I NA rN►AA NA N 180 ARCO STATION BUILDING C ' D <1.0 < .01 <1.0 <1.0 I<1.0 I NO. 3090 0. B <0.02 <0.02 <0.02 <O.OZ <0.08 002 ° 0 0 2 K0,0Z I d <0.02 70.°2 i<O.Oz 70.02 70.°2 70.02 <0.02 70.02 70.02 70.02 0 5' D' 5' 60' 8 0' TPHE 71.0 <00 73.0 71.0 73.0 71.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 71.0 <1.0 <I.0 <I.0 70.02 70.02 70.02 10.02 <0.02 <O.o2 70.02 10.02 <0.02 <0.02,<0.02 70.02 70.02 10.02 70.02 <0.02 -W02 < <0.02 < .02 10.02 <0.02 <0.02 <0.0 <0.02 <0.02 <0.0 700E <0.0 < . < . 2 <0602 ' E <0.02 <0.02 <0.02 <0.02 1<0.02 <0.02 <0.02 <0.021<0.02 <0.021<0.021<0.02 70.02 70.02 <0.02 70.02 70.02 <0.02 <0.02 <0.02 10.02 <0.02 <0.02 <0.02 1 50.02 10.02 1<0.02 1 70.02 50.02 I<O.Oz <o.OZ <O.Oz DUTHI 4 0 5 5 BO TP 2 100 2 500 3 800 <1' 7.1 2.0 1.0 <1.0 71.0 <1.0 B 13.4 4.6 10 70.02 0.27 0.26 0.031 0.085 <0.02 <0.02 ' LEGEND 0 290 90 D.14 0.68 0. 0 Om 16 E 56 72 110 70.°2 0.021 0.070 10.02 °.021 70.°2 <0.02 B9 Denotes Approximate Location x 400 470 700 0.11 0.16 0.42 0.19 0.13 <0.02 <0 OR • of Soil Boring Ds o 5 TPH9 <1.0 U.0 71.0 <1.0 <1.0 ' B10(P) Denotes Approximate Location B <o.DZ <D.oz 52.02 <0.02 <0.0z of Pro osed Soil Boring <o.o <0.0z <°.°z 5<11022 <°.D P g <o.0z <0.0z H.DZ <o.Dz x 70.02 70.02 70.02 <0.02 70.02 MTH E A GROUND S RPACE feet ' TPHff I To etro eum Hvdrocarbous m B Benzene o uene a E lbensUne North lens I , 0 20 40 HYDROCARBON CONCENTRATION MAP ' SECOR International Incorporated ARCO STATION NO. 3090 3333 UNION AVENUE 5401 California Ave., Suite 300, Bakersfield, CA 93309 (805)634-9541 BAKERSFIELD, CALIFORNIA CAD FILE: - 3090BYDS PROJECT N0. DATE: FIGURE:NO600-006-02 8/16/95 3 34th STREET t Sidewalk— — APProach I Planter IPlanter O I I Pump I A Islands � B4 I �°. ' I I (Angl I ¢ w a z w o o I z I _ O I 0 0 BB `n z B5 9 � I ARCO STATION A9 ' BUILDING cc NO. 3090 a LEGEND ' B9 Denotes Approximate Location 0 Of Soil Boring A A' Cross Section Line ' North ' 0 20 40 SITE PLAN SECOR International Incorporated ARCO STATION NO. 3090 3333 UNION AVENUE ' 5401 California Ave., Suite 300, Bakersfield, CA 93309 (605)634-9541 BAKERSFIELD, CALIFORNIA CAD FILE: PROJECT N0. DATE: FIGURE: 30901NDX N0600-006-02 5/25/95 2 1 A A' NORTHWEST SOUTHEAST B-4 B-8 B-1 B-9 0 (1/23/95) (4/26/95) (8/4/93) (4/26/95) SM <1.0 GM/SM <0.02 GM/SM <1.0 I <10 <1.0 1,900 <0.02 NA ML <0.02 5C/CL <0.02200 <1.0 , <10 <1.0 0:30 ? GP <0.02 NA <0.02 SC/CL <1.0 2,100 <1.0 <0.02 NA <0.02 20'- <0 02 <1.0 SC/CL 1,600 <1.0 SW/SP <0.02 <0.02 1N,A 00 ML <0.02 450 _ ? GP <0.01.0 > 0'.820 <0.02 � SW/SP 1,400 <1.0 ' <0.02 <1.0 NA <0.02 40' 1,000 ? <1.0 <0.02 <0.02 0.55-•� <0.02 TD=55' GM <1.0 GM TD=40' ? <1.0 SW SP <0.02 7 ? SW/SP <0.02 SW/Sp <0.02 <0.02 S <1.0 SK ' CL <1.0 <0- ` <0.02 ' 60' <0.02 <0.02 SIP/SP <1.0 SW/SP <1.0 <0.02 <0.02 ' <1.0 <1.0 <0.02 <0.02 < • CL ? <1.0 CL <0.02 <0.02 Z1.0 SW/SP <1.0 80' SW/SP <0.02 <0.02 <1.0 <1.0 <0.02 <0.02 TD=85' TD=86' 100' ' LEGEND NOTES: GP GRAVELS 1. GROUND SURFACE NOT ADJUSTED TO DEPICT SM SILTY SANDS ACTUAL ELEVATIONS. ' SP POORLY GRADED SANDS 2. ANGLE'BORING B-4 PROJECTED INTO CROSS SC CLAYEY SANDS SECTION A - A' BY: ML SILTS TAN a= TAN 6 SINE A CL CLAYS TAN a= TAN 6 SINE 32 = ' TAN at= 48' FROM HORIZONTAL � LITHOLOGIC BOUNDARY AND 42' FROM VERTICAL ? QUERY MARKS lDEPTH OF BORING SOIL SAMPLE LOCATION WITH TPH TPHG AS GASOLINE CONCENTRATIONS IN BENZ mg/kg OVER BENZENE ' CONCENTRATIONS IN mg/kg HORIZONTAL SCALE IN FEET: 20 0 20 40 ' VERTICAL SCALE IN FEET: 20 0 20 40 CROSS-SECTION A - A' SECOR International Incorporated ARCO STATION NO. 3090 3333 UNION AVENUE E alifornia Ave., Suite 300, Bakersfield, CA 93309 (805)634-9541 BAKERSFIELD, CALIFORNIA ILE: PROJECT N0. DATE: FIGURE: 3090CSA N0600-006-02 5/25/95 3 ' 1 Table 4. Analytical results (in mg/kg) of soil samples from beneath dispensers, tanks and piping. Sample No. Benzene Toluene Ethyl- Xylenes TPHG benzene Ti E-2' <0.005 0.020 0.0067 0.085 <1.0 T1 E-6' <0.005 0.0064 0.0094 0.048 <1.0 T1 W-2' <0.005 53 24 450 T 1 W-6' 1.9 64 23 240 1,700 ' T2E-2' <0.005 <0.005 <0.005 <0.005 <1.0 T2E-6' 0.0058 0.0052 <0.005 0.025 <1.0 T2W-2' 12 230 68 580 4,100 "1"11 T2W-6' 2.8 88 28 250 1,800 ' T3E-2' 24 1,200 360 2,600 11,000 Z f ' T3E-6' 21 1,000 320 2,200 9,200 T3W-2' 16 600 180 1,600 ,900 ' D1 W2' 6.9 220 65 500 2000 p,sft-4%01- DiW6' 2.0 39 24 210 2000 0 � ' D1 E2' 0.030 0.024 0.36 0.75 11 D1 E6' 0.013 0.012 0.011 0.083 2.2 D2W2' 0.65 2.9 2.5 39 ' D2W6' 0.017 0.010 0.014 0.17 18 try D2E2' 0.064 0.22 0.034 0.16 <1 D2E6' 0.057 0.23 0.037 0.18. <1 P1-2' <0.005 <0.005 <0.005 <0.015 <10 ' P1-6' <0.005 <0.005 <0.005 <0.015 <10 P2-2' <0.005 <0.005 <0.005 <0.015 <10 I P2-6' <0.005 <0.005 <0.005 <0.015 <10 j P3-2' <0.005 <0.005 <0.005 <0.015 <10 i' P3-6' <0.005 <0.005 <0.005 <0.015 <10 P4-2' <0.005 <0.005 <0.005 <0.015 <10 P4-6' <0.005 <0.005 <0.005 <0.015 <10 P5-2' <0.005 <0.005 <0.005 <0.015 <10 ' P5-6' <0.005 <0.005 <0.005 <0.015 <10 Tank Removal Report ARCO Facility No.3090 GROUNDWATER December 13.1993 TECHNOLOGY tTable 2. Tank information summary. Tank Number Capacity (gallons) Product Stored Composition T1 8,000 Regular Unleaded Fiberglass T2 8,000 Medium-Grade Fiberglass Unleaded T3 6,000 Super Unleaded Fiberglass Table 3. Analytical results (in mg/kg) of soil characterization samples. Sample No. Benzene Toluene Ethyl- Xylenes TPHG benzene tSP1 <0.050 <0.050 <0.050 <0.050 <1.0 SP2 <0.050 <0.050 <0.050 <0.050 <1.0 SP3 <0.050 <0.050 <0.050 <0.050 <1.0 SP4 <0.050 <0.050 <0.050 0.080 12 ' SP5 <0.050 <0.050 <0.050 <0.050 <1.0 SP6 <0.050 >0.050 <0.050 <0.050 <1.0 SP7 <0.050 <0.050 <0.050 <0.050 <1.0 SP8 <0.050 <0.050 <0.050 <0.050 <1.0 SP9 <0.050 <0.050 <0.050 <0.050 1.1 SP1 <0.050 <0.050 <0.050 3.3 320 Will <0.050 <0.050 <0.050 <0.050 <1.0 1 SP12 <0.050 <0.050 <0.050 <0.050 <1.0 I SP13 <0.050 <0.050 <0.050 <0.050 <1.0 SP14 <0.050 <0.050 <0.050 <0.050 <1.0 ' SP15 <0.050 <0.050 <0.050 <0.050 <1.0 SP16 <0.050 <0.050. <0.050 <0.050 <1.0 SP2-1 <0.050 <0.050 <0.050 <0.050. 4.1 SP2-2 <0.050 <0.050 <0.050 <0.050 <1.0 ' SP2-3 <0.050 <0.050 <0.050 0.20 7.5 SP3-1 <0.050 <0.050 <0.050 <0.050 <1.0 ' SP3-2 <0.050 <0.050 <0.050 0.17 2.6 SP4-1 <0.050 <0.050 <0.050 0.36 1.0 Tank Removal Report ARCO Facility No.3090 ILL19GROUNDWATER December 13.1993 p� � pq 1 TECHNOLOGY Table 3. Analytical results (in mg/kg) of soil characterization samples. SP4-2 <0.050 <0.050 0.46 7.6 310 SP43 <0.050 <0.050 <0.050 <0.050 <1.0 SP5-1 <0.050 <0.050 <0.050 <0.050 <1.0 P5-2 <0.050 <0.050 <0.050 0.46 130 SP5-3 <0.050 <0.050 <0.050 <0.050 <1.0 SP5-4 <0.050 <0.050 <0.050 <0.050 <1.0 ' SP5-5 <0.050 <0.050 <0.050 <0.050 1.0 SP6-1 <0.050 <0.050 <0.050 <0.050 <1.0 SP6-2 <0.050 <0.050 <0.050 <0.050 <1.0 SP6-3 <0.050 <0.050 <0.050 <0.050 <1.0 SP7-1 <0.050 <0.050 <0.050 <0.050 <1.0 SP7-2 <0.050 <0.050 <0.050 <0.050 <1.0 i Tank Removal Report ARCO Facility No.3090 GROUNDWATER December 13,1993 TECHNOLOGY TABLE I SOIL SAMPLE ANALYTICAL RESULTS ARCO SERVICE STATION NO. 3090 3333 UNION AVENUE BAKERSFEE ID, CALIFORNIA . ............ ...... ..... -------------- .............. I ........ B-1-5' 08/04/93 <16 NA NA. NA NA B-1-10' 08/04/93 <10 NA NA NA NA B-1-15' 08/04/93 2,100 NA NA NA NA B-1-20' 08/04193 1,600 NA NA NA NA B-1-25'. 08/04/93 1,900 NA NA NA NA B-1-31' 08104193 2,200 0.82 45 34 250 B-1-35' 08/04/93 1,400 NA NA NA NA B-1-40' 08/04/93 1,000 6.55 28 22 160 B-2-5' 08/04/93- 130 NA NA NA NA B-2-10' 08/04/93 <10 NA NA NA NA B-2-15' 08/04193 540 0.035 3.5 4 68 B-2-20!- 08/04193 19 NA NA NA NA B-2-25' 08/04/93 <10 NA NA 'NA NA B-2-30' 08/04/93 <10 NA NA NA NA B-2-35' 08/04/93 <10 NA , NA NA NA B-2-40' 08/04/93 <10 <0.005 <0:038 <0.008 0.12 B-3-5' 08/04/93 <10 NA NA NA NA B-3-10' 03/04/93 <10 NA NA NA NA B-3-15' 08/04/93 <10 <0.005 <0.005 <0.005 <0.005 B-3-21' 08/04/93 <10 NA NA NA NA B-3-25' 08/04/93 <10 <0.005 0.007 <0.005 4C0.015 B-4-5' 01/23/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-4-10' 01/23/95 1,900 <0.02 20 27 200 B-4-15' 01/23/95 1,200 0.30 48 31 190 B-4-25' 01/231/95 1,300 <0.02 12 16 120 B-4-40' 01/23195 450 <0.02 1.1 3.0 22 B-4-45' 01/23/95 <1.0 <0.02 0.17 <0-02 0.053 B-4-50' 01/23/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-4-55' 01/23/95, <1.0 <0-02 <0.02 <0.02 <0.02 B-5-5' 05/03/95 <1.0 <0.02 <0.62 <0.02 <0.02 B-5-10' 05/03/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-5-15' 05/03/95 <1.0 <0.02 <0.02 <M02 <0.02 B-5-20' 05/03/95 <1-0 <0.02% <0.02 <0.02 <0.02 B-5-25' 05/03/95 <1.0 <0.02 <0.02 <0.02 <0.02 Notes: Mg/Kg-milligrams per kilograms TPHg-Total Petroleum Hydrocarbons as gasoline NA-Not analyzed TABLE I SOEL SAMPLE ANALYTICAL RESULTS ARCO SERVICE STATION NO. 3090 3333 UNION AVENUE BAKERSFIELD, CALIFORNIA -:X . . . ... .. .... .. .. .... .............V--L1----';:*" .................. .. . ............... 0 ...... TO " N B-6-10' 05/03195 <1.0 <0.02 <0.02 <0.02 -<0.02 B-6-15' 05/03/95 6,300 2.3 550 270 1,800 B-6-20' 05/03/95 1,500 0.73 140 63 380 B-6-25' 05/03195 1,500 <0.02 41 31 250 B-6-30' 02/03/95 1,200 <0.02 17 15 130 B-6-35' 05/03/95 680 01.14 11 10 67 B-6-40' 05/03/95 390 <0.02 2.4 3.6 29 B-6-50' 05/03/95 340 0.066 8.0 8.5 45 B-6-55' 05103/95 310 0.093 9.5 8.4 42 -B-7-5' 05/03/95 <1.0 <0.02 <0.02 <0.02 <0.021 B-1-10, 05/03/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-7-15' 05/03/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-7-20' 05/03/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-7-25' 05103/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-8-5' 04/26/95 210 <0.10 <0.10 0.21 <0.30 B-8-10' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-8-15' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 1 B-8-20' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-8-38.5' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-8-47.5' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-8-50' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-8-55' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02. B-8-60' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-8-65' 04/26/95 <1.0 0.033 0.080 <0.02 0.13 B-8-70' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-8-75' 04/26/95 <1.0 <0.02 <0.02 <0.02 <U. B-8-80' 04/26/95 <1.0 <0.02 <0.02 <O.Crl 0.18 B-8-85' 04/26195 <L0 <0.02 <0.02 <0.02'1<00.0022 Notes: Mg/Kg-milligrams per kilograms TPHg-Total Petroleum Hydrocarbons as gasoline NA-Not analyzed TABLE 1 SOIL SAMPLE ANALYTICAL RESULTS ARCO SERVICE STATION NO. 3090 3333 UNION AVENUE EAKERSF'IELID, CALIFORNIA bi Ail :... >>;:SAMPLE:::.::>;::: Z� :.... B-9-5' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-940' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-9-15' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-9-20' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-9-25' 04/26/95 <1.0 <0.02 <0.02 . <0.02 <0.02 B-9-35' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-9-40' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-9-45' 04/26195 <1.0 <0.02 <0.02 <0.02 <0.02 B-9-50'. 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-9-55' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-9-60' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-9-65' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-9-70' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-9-75' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-9-80' 04/26/95 <1.0 <0.02 <0.02 <0.02 <0.02 B-9-85' 04126195 <1.0 <0.02 <0.02 <0.02 <0.02 13-10-4S' 08/02/95 2,100 3.4 72 58 400 B-10-50' 08/02/95 2,500 4.8 140 72 470 B-10-55' 08/02/95 3,800 10 290 110 700 ' B-10.60' 08102195 <1.0 <0.02 0.09 <0.02 0.11 B-10-65' 08/02/95 7.1 0.27 0.14 0.02 0.16 B-10-70' 08/02/95 2.0 0.26 0.68 0.07 0.42 B-10-75' 08/02/95 1.0 0.03 0.10 <0.02 0.13 B-10-80' 08/07195 <1.0 0.08 0.16 0.02 0.13 B-10-85' 08/02/95 <1.0 <0.02 <0.02 <0.02 <0.02 ' B-10-90' 08/02/95 <1.0 <0.02 <0.02 <0.02 <0.02 Notes: Mg/Kg-milligrams per kilograms TPHg-Total Petroleum Hydrocarbons as gasoline NA-Not analyzed i t Drilling Log ❑� GROUNDWATER Soil Boring B1 TECHNOLOGY Project ARCO Service Station No. 3090 owner ARCO Products ComDanv See Site Map Location BakerStield, CA Project No. 022504584 Date drilled 814193 For Boring Location Surface Elev. Total Hole Depth 41 ft. Diameter .6 ft. COMMENTS: Top of Casing Water Level Initial Static Screen:Dia Length Type/Size Boring located near me south Casing: Dia Length Type edge or tanks. Filter Pack Material Rig/Core Type Moplle B-80 Drilling Company Consolidated restr'no Method 7"Hollow Stem Aucer Permit tf Driller A/Avila Log By Steonan Bork Checked By Jonathan Parker License No.RC, 4728 Description 1 a� a a�u a o Texture, Structure) cv a a E ;� t`o� to (Color, M Oct Nmx Trace < 10%. Little 10% to 20%. Some 20% to 35%, And 35% to 50% 0 last AS Asphaltic concrete and aggregate base. 2 4 SM 4.0 3t-5' SAND, fine to medium grained, silty (15%), poorly graded, medium 6 5 dense, moderate brown, damp, no petroleum odor. 9 ' 1� S I 10 6.5 91-t0' SILT, fine sandy, very dense, moderate brown, damp, a some moderate cementation, trace fine rounded gravel, no 21 petroleum odor. ' 12 32 ML ' 14 5012 B1-15' SILT, fine sandy, dense, moderate brown, damp, 16 o strong gasoline odor. ' zo 18 20 5a67 81-20' SC S AN D, fine to coa r se grained, clayey (2Q%). fin e gravelly ( Q , 12 Z.. poorly graded, subrounded, dense, moderate brown, damp, strong 13 . . . gasoline odor. 22 zs 24 SP- 08/30/19931itnlog-mar92 Page: I of 2 Drilling Log ❑❑❑ GROUNDWATER Soil Boring B1 TECHNOLOGY ARCO Service Station No. 3090 ARCO Products Comoanv Pro iect Owner Location Bakersfield. CA Project No. 022504584 Date drilled 814193 Description a� n vo' C e 0 � U E z 0 a v 2-'o N (Color, Texture, Structure) 1 m °°C N Trace < 10%, Little 10% to 20%, Some 20% to 35%. And 35% to 50% cn,mx o 24 ' 5475 B1-25' SAND, fine to coarse grained, fine gravelly (10X), poorly graded, 26 t0 subrounded, dense, moderate brown, damp, strong gasoline odor. Ifi 21 ' 28 ' 30 6474 BI-31' SAND, fine to coarse grained, fine gravelly (15%), coarse gravelly 32 30 (15%), poorly graded, subrounded, very dense, moderate brown, ' 45 damp, no recovery at 30' due to coarse gravel, strong gasoline odor. $P 34 6722 BI-35' 1 SAND, fine to coarse grained, fine gravelly (15%), coarse gravelly 36 3s( 15X), poorly graded, subrounded, very dense, moderate brown, 35 damp, strong gasoline odor. 38 40 7208 31-40' j: . SAND, fine to coarse grained, fine gravelly (15%). coarse gravelly 33 ! (15%), poorly graded, rounded, very dense• moderate brown, damp, ' 50 some cobbles from 38 to 40 feet, strong gasoline odor. 42 I ' 44 ' 46 ' 48 50 I 52 54 56 08/30/1993 iitntog-mar92 Page: 2 of 2 Drilling Log ❑00 GROUNDWATER Soil Boring B2 TECHNOLOGY Project ARCO Service Station No. 3090 Owner ARCO Products COmpany See Site Map Location Bakersfield, CA Project No. 022504584 Date drilled 814193 For Boring Location Surface Elev. Total Hole Depth 4r ft. Diameter .s ft. COMMENTS: Top of Casing Mater Level Initial Static Screen: Dia Length Type/Size Boring rocarea north or tank Casing: Dia Length Type rill Ports. Filter Pack Material Rig/Core Type Mobile 8-80 Drilling Company Consolidated Testing Method 7"Hollow Stem Auger Permit # Driller Al Avita Log By Stephan Bork Checked By Jonathan Parker License No.RC, 4728 `� ° Description ar oa a+ o' t� to v n�u ao E ;m �� rn (Color, Texture. Structure) Nan Trace < 10%, Little 10% to 20%. Some 20% to 35%. And 35% to 50% ' -2 ` C As Asphaltic concrete and aggregate base. 2 4 Sr+ ' 889 82-5' SAND, fine grained, silty (20%), poorly graded, Icose, dark olive 6 3 brown, damp, strong degraded gasoline odor. s 8 7 10 122 82-1 p SP SAND, fine to coarse grained, fine gravelly (<10%), coarse gravelly ll (<10%), medium dense, moderate brown, damp, trace silt, faint 5 degraded gasoline odor, ' 12 14 6031 B2-15' sr+ SAND, fine to coarse grained, silty (15%), poorly graded, dense, 16 15 moderate brown, damp, some cemented nodules, moderate degraded 17 33 gasoline odor. 18 20 315 82-20' Sc SAND, fine to coarse grained, clayey (I SX). fine g r ave y (206 ). 31 coarse gravelly OOV, poorly graded, subrounded, very dense, 41 moderate brown, damp, *insufficient recovery for proper PID 40 22 reading, moderate degraded gasoline odor. 2 SP 4 08/30/1993lithlog-mar92 Page: 1 of 2 I ' �❑® Drilling Log 000 GROUNDWATER Soil Boring B2 TECHNOLOGY Project ARCO Service Station No. 3090 owner ARCO Products Companv Location Bakersfield, CA Project No. 022504584 Date drilled 814193 N w t Description a� oa a,°° rn rJ o-- o_a E s v m° to (Color, Texture, Structure) M.2 ? Trace < 10%. Little t0% to 20%. Some 20% to 35%, and 35% to 50% 24 ' 583 B2-25' SAND fine to coarse grained, fine gravelly (<10%), coarse gravelly 26 15 (<10%), poorly graded, subrounded, dense, moderate brown, damp, t5 strong degraded gasoline odor. 20 ' 28 30 509 B2-30' SAND, fine to coarse grained, tine gravelly (15'6), coarse gravelly (15%), poorly graded, subrounded, dense, moderate brown, damp, strong degraded gasoline odor. 32 is t6 SP 34 464 B2-35' SAND, fine to coarse grained, fine gravelly (15X), coarse gravelly (15%), poorly graded, subrounded, very dense, moderate brown, 36 damp, abundant cobbles at 37 to 39 feet.strong degraded gasoline ' • • • odor. 38 ' 40— 606 82-40' t:.:...:' SAND, fine to coarse grained, fine gravelly (15%), coarse gravelly (15%), poorly graded, subrounded, very dense, moderate brown, damp, some cobbles, strong degraded gasoline odor. ' 42 ' 44 46 48 50 52 54 56 08/30/1993litnlog-mar92 Page: 2 of 2 Drilling Log GROUNDWATER Soil Boring 63 TECHNOLOGY 1 Project ARCO Service Station No. 3090 Owner ARCO Products COmDanv See Site Map For Boring Location Location Bakersfield. CA Project No. 0225045,84 Date drilled 814193 Surface Elev. Total Hole Depth 27.5 ft. Diameter .6 ft. COMMENTS: Tap of Casing water level Initial Static Screen: Dia length Type/Size Boring located west or the middle Casing:Dia Length Type tank. Filter Pack Material Rig/Core Type Mobile B-80 Drilling Company Consolidated Testing Method 7"Hollow Stem Aucer Permit g ' Driller Al Avila Log By Stephan Bork Checked By Jonathan Parker License No.RG 4728 `1 y� Description aF a o V o o_ n v 0 O,o E T m rn (Color, Texture, Structure) Nmx Trace < 10%, Little 10% to 20%. Some 20% to 35%, And 3S% to 50% -2 AS Asphaltic concrete and aggregate base. 2 ' SM 4 SAND, fine to medium grained, silty 05%), poorly graded, ' subrounded, medium dense, moderate brown, damp, trace coarse sand 5.0 B3-5 and fine gravel• no petroleum odor. 6 i 11 O°� GP PEA gravel, tank backfill. ' 8 ML SILT, very fine to fine grained, silty, moderate olive brown, damp, no petroleum odor. SM "AND, fine to coarse grained, silty (20%), poorly graded, subrounded, dense, moderate olive brown, damp, no petroleum odor. 10 7.0 93-10' f SP AND, fine to coarse grained, fine gravelly (15%), coarse gravelly 22 ;- (10%), poorly graded, subangular, very dense, light brown, 42 no petroleum odor. ' ao 12 1 . sM AND, very fine to medium grained, silty (20%), poorly graded, subrounded, dense. moderate brown, damp, no petroleum odor. ' 14 SAND, fine to coarse grained, silty (15%), clayey. (10%), poorly SM graded, subrounded, dense, no petroleum odor. 7.0 83-15' 16 t7 SAND, fine to coarse grained, clayey, poorly graded, subrounded, ' zs Sc dense, moderate brown, damp, clay content varies from 15 to 30%, trace silt. no petroleum odor. 18 SC 20 SAND, fine to coarse grained, clayey (15%), fine gravelly (1501), coarse gravelly (15%), poorly graded, subangular, very dense, 3.0 82 7-21' moderate brown, damp, no petroleum odor. 22 io 51 j SP 24 08/30/1993 fithlog-Mar92 Page'. i of 2 ❑❑® Drilling Log GROUNDWATER Soil Boring B3 TECHNOLOGY Project ARCO Service Station No. 3090 owner ARCO Products Comoanv Location Bakersfield. CA Project No. 022504584 Date drilled 814193 C E (D o, r o� Description a. a o v (Color, Texture, Structure) 1D °c p N Trace < tO%. Lithe 10% to 20%. Some 20% to 3S%. And 35% to 50% cn FOR t 24 2.0 83-25' SAND, medium to coarse grained, fine gravelly (10%), coarse gravelly 26 za SP (<10%), poorly graded, subrounded, very dense, moderate brown, 36 . . . . damp, no petroleum odor. Abundant cobbles at 27 feet. ' 28 . ' 30 32 34 36 ' 38 i40 ' 42 ' 44 ' 46 48 50 52 54 56 08/30/1993 iftniog-marW Page: 2 of 2 SEC®R 2824 Camino Dos Rios, Suite 101 Newbury Park, California 91320 1 Phone: (805) 498-0556 Fax: (805) 498-6337 Page 1 of 2 Project: PN#: Boring/Well: ARCO Facilti No. 3090 N0600-006-01 B4 Location: Well Construction Data 3333 Union Avenue Bakersfield CA. Date Started: Date Completed: Screen: 23 JAN 95 23 JAN 95 NA From: - To: Logged By: Checked By: Pack: J. Cooper J. Bollier NA From: - To: Drilling Co.: Driller: Seal: . Melton R. Walton Bentonite chip =From: .5 - To: 60 Method: Equipment: Grout: Hollow Stem Auqer CME 75 / PID Concrete From: 0 - To: .5 Boring Depth: Ground Surface Elevation: Inner Casing: 60.0 NA NA Initial GW Level: GW Level: Time/Date: Outer Casing/Stick Up: ' Q NA = NA NA m m o, CL CL E E E o a E o Description Remarks Well o f0 f9 m Constructio ' to ch z J 1 0 5 2 10.4 SM SILTY SAND Moderate yellow brown,moist, loose, 20% 5 ' 2 silt, very fine grained,moderate hydrocarbon odor 3 — — — — — — — — — — — — — — 10 8 1263 CL SANDY CLAY Moderate reddish brown,slightly moist, 10 20 medium stiff, 20%sand,moderate plasticity,strong 22 hydrocarbon odor 15 13 2100 15 ' 32 — — — — — — — — — — — — — — ' 20— -no recovery 20 OM 25 20 1900 SW GRAVELLY SAND Moderate yellow brown,slightly moist, 25 n a 25 'dense, fine to coarse grained sand, well graded,slight Y 25 hydrocarbon odor a 0 U m m 30 30 Continued Next Page n SEC®R 2824 Camino Dos Rios, Suite 101 Newbury Park, California 91320 Phone: (805) 498-0556 Fax: (805) 498-6337 Page 2 of 2 Project: PN#: Boring/Well: ARCO Faciltiy No. 3090 N0600-006-01 B4 Location: SIR!:l'i�'�i���iilll�i�� 4�il�l.�i��� �i���'i�'I)it����i :� 3333 Union Avenue Bakersfield CA. m a� a E E E o f o Description Remarks Well o M cn :3 m a �_ Constructio OZ J -no recovery ' 35 -no recovery 35 40 80 900 ' 40 - - - — — — — — — — — — — — — — — 45 80 36 • GP GRAVEL Moderate yellow brown,slightly moist,dense, 45 • 20% fine grained sand,poorly graded, clasts approximately 5cm,slight hydrocarbon odor t 50 80 30 ; SW GRAVELLY SAND Moderate yellow brown,slightly moist, 50 ' fine to medium grained, well graded,clasts approximately 1 cm, very slight hydrocarbon odor ' 55 80 13 SW GRAVELLY SAND Orangish brown,moist,fine to medium 55 ;• grained, well graded,trace clay,iron oxide staining,no ' hydrocarbon odor 60 O 80 -no recovery, auger refusal ' Total depth 60 feet. 0 m n a u a 0 U N N } a I ' n SEC®� 2824 Camino Dos Rios, Suite 101 Newbury Park, California 91320 Phone: (805) 498-0556 Fax: (805) 498-6337 Page 1 of 1 Project: PN#: Boring/Well: ARCO Facilti No. 3090 N0600-006-01 B5 Location: Well Construction Data 3333 Union Avenue Bakersfield CA. Date Started: Date Completed: Screen: 23 JAN 95 23 JAN 95 NA ®From: - To: Logged By: Checked By: Pack: J. Cooper J. Bollier NA OFrom: - To: Drilling Co.: Driller: Seal: Melton R. Walton Bentonite chip ®From: .5 - To: 25 Method: Equipment: Grout: Hollow Stem Auqer CME 75 /PID Concrete ° ° From: 0 - To: .5 Boring Depth: 25 0 Ground Surface Elevation: Inner Casing: NA NA Initial GW Level: GW Level: Time/Date: Outer Casing/Stick Up: ' Q NA NA NA 2 m CL E E E o E o Description Remarks Well o M o = m a 75; Construction t ' Z .J 0 0 ea o sa t 5 3 0 SM SILTY SAND Moderate yellow brown,slightly moist, 20% 5 ' 3 sift, loose, very fine grained, well graded, no hydrocarbon odor 4 10 10 0 -as above,no hydrocarbon odor ' 15 15 13 0 -as above,40% silt,fine grained,no hydrocarbon odor 25 35 _ _ _ _ _ _ _ _ _ _ _ _ _ _ 20 7 0 CL SANDY CLAY Moderate yellow brown,slightly moist, 20% 20 14 sand,moderate plasticity,no hydrocarbon odor 50 SW GRAVELLY SAND Moderate yellow brown,slightly moist, o25 14 0 dense,fine to medium grained, clasts approximately 2«n.no ' < 20 ydrocarbon odor a 20 Total depth 25 feet. 0 0 N } Q 1 M SEC®� 2824 Camino Dos Rios, Suite 101 Newbury Park, California 91320 Phone: (805) 498-0556 Fax: (805) 498-6337 Page 1 of 2 Project: PN#: Boring/Well: ARCO Facilti No. 3090 N0600-006-01 86 Location: Well Construction Data 3333 Union Avenue Bakersfield CA. Date Started: Date Completed: Screen: 23 JAN 95 24 JAN 95 NA' ff�From: - To: Logged By: Checked By: Pack: J. Cooper J. Bollier NA From: - To: Drilling Co.: Driller: Seal: Melton R. Walton Bentonite chip =From: .5 -To: 55 Method: Equipment: Grout: 1177-4-7-7 Hollow Stem AUqer CME 75 / PID Concrete 61.1�-' From: 0 - To: .5 Boring Depth: 55.0 Ground Surface Elevation: Inner Casing: NA NA Initial GW.Level: GW Level: Time/Date: Outer Casing/Stick Up: a NA T I NA NA CL a a.0 o f o Description Remarks Well o cn cn Z —�° a � p Constructio J ' 0 0 •e .o 5 SM SILTY SAND Moderate yellow brown,slightly moist, 10% 5 silt,loose,very fine grained,no hydrocarbon odor — — — — — — — — — — — — — — 10 - 10 470 •1 • GP GRAVEL 1/flinch clasts, 5%fine grained sand,poorly 10 ' 6 graded,moderate hydroca=ban=do= — — — — — — 15 5 330 SM SILTY SAND Moderate yellow brown,slightly moist, 10% 15 6 silt, loose,fine grained.strong hydrocarbon odor 8 ' 20 19 550 CL SANDY CLAY Moderate yellow brown,moist,medium stiff, 20 32 10%sand,moderate plasticity,strong hydrocarbon odor ' — — — — — — — — — — — — — — 0 25 18 160 SW SAND Orangish brown,slightly moist,medium dense,fine 25 < 24 •; to medium grained, well graded,strong hydrocarbon odor a f 30 30 Continued Next Page I I r ' r SEC®R 2824 Camino Dos Rios, Suite 101 Newbury Park, California 91320 Phone: (805) 498-,0556 Fax: (805) 498-6337 Page 2 of 2 Project: PN#: Boring/Well: ARCO Facilti No. 3090 N0600-006-01 66 Location: 3333 Union Avenue Bakersfield CA. CL I 1 n:: r ill r l i 11 a s. E E E o °E c Description Remarks Well o cn cn :3 FO Constructio Z J 20 280 SW GRAVELLY SAND Light yellowish brown,slightly moist, 50 dense,fine to medium grained, clasts approximately 5cm, ; strong hydrocarbon odor — — _ — — — — _ _ 35 12 SPA SILTY SAND Moderate yellow brown,slightly moist, 35 30 medium dense,very fine to fine grained, well graded,clast approximately 1 cm,moderate hydrocarbon odor ! ' 40 50 SW GRAVELLY SAND Moderate yellow brown, slightly moist, 40 dense, fine to medium grained, well graded,strong hydrocarbon odor 45 50 no recovery 45 50 O -no recovery 50 55 •• SW GRAVELLY SAND Orangish brown,slightly moist,dense, 250 • well graded,fine to medium grained, clasts approximately 2cm, i rang hydrocarbon odor Total depth 55 feet. 1 0 0 n a Y 0 r 1 U N } Q ,1 SEC®R 2824 Camino Dos Rios, Suite 101 Newbury Park, California 91320 Phone: (805) 498-0556 Fax: (805) 498-6337 Page 1 of 1 Project: PN#: Boring/Well: ARCO Faciltiv No. 3090 N0600-006-01 B7 Location: Well Construction Data 3333 Union Avenue Bakersfield CA. Date Started: Date Completed: Screen: 24 JAN 95 24 JAN 95 NA ®From: To: Logged By: Checked By: Pack: J. Cooper J. Bollier NA From: - To: Drilling Co.: Driller: Seal: Melton R. Walton Bentonite chip =From-. .5.- To: 25 Method: Equipment: Grout: Hollow Stem Auqer CME 75 / PID Concrete L.:.: From: 0 - To: .5 Boring Depth: Ground Surface Elevation: Inner Casing: 25.0 NA NA Initial GW Level: NA iGW Level: Time/Date: NA Outer Casing/Stick Up: NA CL CL M aai E E E o a E o Description Remarks Well o o fn :3 m Construction Z J O 0 s v s e 5 2,0 ML CLAYEY SILT Moderate yellowish brown,dry, 20% clay, 5 ' moderate plasticity,no hydrocarbon odor — — — — — — — — — — — — — — 1 '0— 17 0 SM SILTY SAND Light yellow brown,dry,40%sift,very fine 10 37 grained,no hydrocarbon odor 15 5 0 ML SANDY SILT Moderate yellow brown,slightly moist, 10% 15 8 sand,moderate clay,low plasticity,no hydrocarbon odor 7 — — — — — — — — — — — — — — ' 20 10 0 CL SANDY CLAY Moderate yellow brown,slightly moist, 10% 20 22 sand,moderate plasticity,no hydrocarbon odor 24 SW GRAVELLY SAND Moderate yellow brown, dry to slightly 0 25 19 0 PP,os fine to medium grained, well graded, clasts 22 roximately 2cm,no hydrocarbon odor N 25 Total depth 25 feet. 0 0 U y I � Q SEC®� 2824 Camino Dos Rios, Suite 101 Newbury Park, California 91320 Phone: 18051498-0556 Fax: (805) 498-6337 Page 1 of 3 Project: PN#: Boring/Well: i ARCO Facilti No. 3090 N0600-006-01 68 Location: 3333 Union Avenue Bakersfield CA. Well Construction Data Date Started: Date Completed: Screen: 26 JAN 95 26 JAN 95 NA ®From: To: Logged By: Checked By: Pack: J. Cooper J. Bollier NA OFrom: To: Drilling Co.: Driller: Seal: Drill Line D.L.S. Bentonite chip ®From: .5 - To: 85 Method: Equipment: Grout: a Hollow Stem Aucier CME 75 / PID Concrete From: 0 - To: .5 Boring Depth: Ground Surface Elevation: Inner Casing: 85.0 NA NA Initial GW Level: GW Level: Time/Date: Outer Casing/Stick Up: 2 NA i NA NA CL CL E E E o o f o Description Remarks Well p M 3 m a E Construction Z J O 0 .o • e a s s 1 . 5 20 142 • 1 GM GRAVELLY SILT Olive gray, 20% pea size gravel,slightly 5 33 • 1 moist,medium stiff,low plasticity,slight hydrocarbon odor 38 — — — — — — — — — — — — — . 1 . 10 15 0.8 •= GP GRAVEL moderate yellowish brown,slightly moist,medium 1 ' 20 •• grained sand, clasts approximately t cm�no hydrocarbon odor 21 �1 . ' 15 9 1.3 CL SANDY CLAY Moderate yellow brown,slightly moist, 10% 15 24 very fine sand,moderate plasticity,no hydrocarbon odor ' 33 ' 20 O 80/1" 24 -light brown,slightly moist, 10%silt,moderate plasticity,no 20 i hydrocarbon odor, 0 25— 13 0 no recovery 25 ' m 31 N c 40 O r U U) 30 30 Continued Next Page SAC® 2824 Camino Dos Rios, Suite 101 Newbury Park, California 91320 E1 Phone: (805) 498-0556 Fax: (805) 498-6337 I Page 2 of 3 Project: PN#:, Boring/Well: ARCO Facilti No._3090 N0600-006-01 B8 Location: ai u,i ihi i +r' I lilli�u i l II'I{��lu , t• s II I'�lii� ,.,m. i u,dilutl„i :.Ili i�lYll Irllll 3333 Union Avenue Bakersfield CA. E E E o a E c Description Remarks Well f1) N 7 in i CDnstructlD Z J O6013” 0 -no recovery ' 35 O 5014" 0 -no recovery 35 — — — — — — — — — — — — — — ' 40 16 3.2 SW SAND Yellow brown, dry, dense,fine grained,no 40 5012" hydrocarbon odor — — — — — — — — — — — — — — , o 0 o CJ 00 45 30 4.9 ) O GW SILTY GRAVEL Dark yellow brown,dry,dense,40%silt. 45 50 0.C clasts approximately 2cm SP SAND Moderate yellow brown,dry,dense, fine grained, poorly,graded,slight hydrocarbon odor r 50 30 16 1 GM SANDY'GRAVEL Moderate yellow brown,dry,dense, 10% 50 50 sand, clasts approximately 5cm,very slight hydrocarbon odor 55 50 24 • ' • GM GRAVELLY SILT Moderate yellow brown, slightly moist, 55 iron oxide staining,very slight hydrocarbon odor ' — — — — — — — — — — — — — — ' 60 50 270 SP SAND Light brown,dry, dense, very fine to medium grained, 60 poorly graded,slight hydrocarbon odor 1 0 65 35 280 65 ' a 55 Y Q O r U N Obi 70 70 Continued Next Page i 2824 Camino Dos Rios, Suite 101 Newbury Park, California 91320 SEC®R ' Phone: (805) 498-0556 Fax: (805) 498-6337 Page 3 of 3 Project: PN#: Boring/Well: ARCO Facilti No. 3090 N0600-006-01 88 Location: y u'il I iII, s utu'io liiiry,; Ili rf jr iininl tr 5 3333 Union Avenue Bakersfield CA. 47) cn a� a� E E E o a E o Description Remarks Well o � m Constructio Z M 30 430 -as above,slight hydrocarbon odor 55 ' 75 13 217 CL CLAY Light olive gray,slightly moist,stiff, 5% sand, 75 24 moderate to plasticity,slight hydrocarbon odor 25 ' 80 15 240 SP PID SA Yellowish gray,slightly moist,very fine grained,no gD 50 hydrocarbon odor 85 104 Total depth 85 feet. I I 0 1 0 0 a N Q O r ' U N Q 5EC® 2824 Camino Dos Rios, Suite 101 Newbury Park, California 91320 Phone: (805) 498-0556 Fax: (805) 498-6337 Page 1 of 3 Project: PN#: Boring/Well: ARCO:Facilti No. 3090 N0600-006-01 B9 Location: Well Construction Data 3333 Union Avenue Bakersfield CA. Date Started: Date Completed: Screen: 26 JAN 95 26 JAN 95 NA ®From: - To: Logged By: Checked By: Pack: J. Cooper J. Bollier NA OFrom: - To: - Drilling Co.: Driller: Seal: Drill Line D.L.S. Bentonite chip ®From: .5 - To 85 Method: Equipment: Grout: r77—17-1 Hollow Stem Au a CME 75 /PID Concrete From: 0 - To: .5 Boring Depth: 86 0 Ground Surface Elevation: Inner'Casing: NA NA Initial GW Level: NA GW Level: Time/Date: NA Outer Casing/Stick Up: NA 1, 7 CO a E E E o f o Description Remarks Well a ` Construction (n to z J . 5 1g 0 LIL SILT Moderate yellow brown,dry, 10% sand, low plasticity, 5 29 no hydrocarbon odor 30 10 50/6 0 -as above, no hydrocarbon odor 10 ' 15 15 8 0 -as above,no hydrocarbon odor 23 1 27 , 20 20 11 0 -as above, no hydrocarbon odor 20 23 I c 25 ' m 25 o 50/6 0.1 I -as above,no hydrocarbon odor a N Y a O ' U m I f 30 I 30 Continued Next Page 2824 Camino Dos Rios, Suite 101 Newbury Park, California 91320 SECOR Phone: (805) 498-0556 Fax: (805)498-6337 1 Page 2 of 3 Mat Project: PN#: Boring/VVell: ARCO Facilti No. 3090 N0600-006-01 B9 Location: I ! twll I nib au�� 3333 Union Avenue Bakersfield CA. , s I,Ilrll , 1 „r; hF u, i..: CI a a.0 3: 0 E o Description Remarks Well o D —�° a Y p Constructio 27 I -no recovery 50 35 50 0.2 SP SAND Pate yellow brown,dry, 35 y y,poorly graded,very fine to medium grained,no hydrocarbon odor 40 50 1.0 -as above,no hydrocarbon odor 40 45 is 0 -as above,very fine grained,no hydrocarbon odor 45 50 50 50 3.5 CL SANDY CLAY Moderate brown,slightly moist, 5% very fine 50 grained sand,moderate plasticity,no hydrocarbon odor 55 50 0 -as above,no hydrocarbon odor 55 60 27 56 SUN SAND Pale yellow brown,dry,dense,very fine to fine 60 50 ; grained, well graded, very slight hydrocarbon odor 0 65 12 55 -as above,light brown, well graded,slight hydrocarbon odor 65 a 28 N a 35 0 f 70 70 Continued Next Page h' ! SEC®R 2824 Camino Dos Rios, Suite 101 Newbury Park, California 91320 Phone: (805) 498-0556 Fax: (805) 498-6337 Page 3 of 3 Project: PN#: Boring/Well: ARCO Facilti No. 3090 N0600-006-01 B9 Location: G o 3333 Union Avenue Bakersfield CA. llhi 31 t s ,I hl i a� a� CL E E E o o f a Description Remarks well o sn in n Constructio Z J 27 100 -as above,pale brown,very slight hydrocarbon odor so, 75 16 185 -as above,slight hydrocarbon odor 75 24 36 80 127 80 85 31 201 -as above,slight hydrocarbon odor,auger refusal at 86 feet 85 ' bu Total depth 86.0 feet. 0 LO0 n a Y a O H N 0 a m i I' t PROJECT: ARCD PRODUCTS COMPANY, ARCO STATION NO. 3090, 3333 UNION AVE., BAKERSFIELD, CA. LOG OF BORING/WELL PAGE 1 OF 3 BORING LOCATION: SOUTH EDGE OF UST BASIN. BETWEEN B6 AND 81 PROJECT NO.: N0600-006-05 ��® SUBCONTRACTOR AND EQUIPMENT: VERDE DRILLING, BK-81 LOGGED BY: J. COOPER SAMPLING METHOD: HSA, MOD CA. SPLIT SPOON MONITORING DEVICE: MINIRAE PID START DATE TIME: 8/2/95, 9:25om FINISH DATE TIME: 8/2/95, 12:20 m FIRST WATER (BGS): N/A STABILIZED WATER LEVEL (BGS): N/A SURFACE ELEVATION: N/A CASING TOP ELEVATION: N/A SECOR TOTAL WELL DEPTH: N/A BORING DIAMETER: B" International Incorporated R.G. APPROVAL: J. BOLLIER, RG NO. 6099 BORING DEPTH: 91.5' J a ° va E n > c to LITHOLOGIC DESCRIPTION BORING ABANDONMEN a 6j (soil classification, color, moisture, density, grain size/plasticity, other) WELL CONSTRUCTION DETAILS N Z 0 \ a V M O En CL 0 6' ASPHALT AT GRADE ; ' CONCRETE HAND AUGER, POST HOLE DUG TO 5' 4. 2 1 4 12 7.6 ML JJU- YELLOW BROWN, SLIGHTLY MOIST, SOFT, 9 NO HYDROCARBON ODOR t0 6 -------------------------------- B ' 5 5.2 10 GW GRAVELt YELLOW BROWN, SLIGHTLY MOIST, LOOSE, 11,C CLASTS, NO HYDROCARBON ODOR 5 10 -------------------------------- 12 i 14 BENTONITE ' SEAL B 375 ML j&YELLOW BROWN, SLIGHTLY MOIST, SOFT, MODERATE HYDROCARBON ODOR 10 15 16 -------------------------------- i 18 14 590 20 CL GRAVELLY CLAY: LIGHT BROWN, MOIST, Z07" GARVEL. 1" CLASTS, MEDIUM STIFF, MODERATE HYDROCARBON ODOR 20 28 COBBLES AT 20' - 22' -------------------------------- 22 i ' 24 i5 849 SM SILTY SAND: LIGHT BROWN, SLIGHTLY MOIST, VERY FINE TO MEDIUM GRAINED, ' TRACE SILT, MODERATE HYDROCARBON ODOR 23 2 25 6 ' 28 30 30BBBIOA PROJECT: ARCO STATION N0. 3090, 3333 UNION AVENUE, BAKERSFIELD, CA. LOG OF BORING/WELL- PAGE 2 OF 3 BORING LOCATION: SOUTH EDGE OF UST BASIN, BETWEEN 86 AND 81 ® PROJECT NO.: N0600-006-05 ®1 LOGGED BY: J COOPER COMMENTS: S E C®R International Incorporated J i a E r. o 1 W 00 a v a m r LITHOLOGIC DESCRIPTION BORING ABANDONMENT ? vii p �^ (soil classification, color, moisture, density, grain size/plasticity, other) WELL CONSTRUCTION DETAILS w G u - r- V1 Co ° o a o_ , fA 60 140 30 SM/ SANDY SILT IT GRAVEL; LIGHT BROWN, SLIGHTLY MOIST, DENSE, GM GRAVEL CLASTS S 1 1/2- DIAMETER, 50- SLIGHT HYDROCARBON ODOR B" 32 ' 34 48- 550 SM SAME AS ABOVE. VERY DENSE, MODERATE HYDROCARBON DOOR GM ell 36 38 76- 964 40 SM/ SANDY SILT WITH GRAVEL• LIGHT BROWN. SLIGHTLY MOIST, VERY STIFF, GM GRAVEL CLASTS S 1" DIAMETER, OCCASIONAL CLAY INTERSEDS, 10" MODERATE HYDROCARBON ODOR 42 44 BENTONITE SEAL 84- 1460 SM/ SAME AS ABOVE, STRONG HYDROCARBON ODOR 7 GM 46 ----------------------------------- 48 22 730 50 SM SAND: LIGHT YELLOW BROWN, DRY, DENSE. VERY FINE TO MEDIUM GRAINED. STRONG HYDROCARBON ODOR ' 30 40 -------------------------------- 52 i - 54 50 753 GP SANDY GRAVEL: LIGHT BROWN. DRY, DENSE. 40% GRAVEL S1" DIAMETER, MODERATE HYDROCARBON ODOR 50 56 ' 58 60 I 30909100 PROJECT: ARCO STATION NO. 3090, 3333 UNION AVENUE, BAKERSFIELD, CA. LOG OF BORING/WELL PAGE 3 OF 3 BORING LOCATION: SOUTH EDGE-OF UST BASIN, BETWEEN B6 AND B1 ® PROJECT NO.: N0600-006-05 ®1 LOGGED BY: J. COOPER COMMENTS: SEC® International Incorporated J _ > E •• o 1 W ° ° v E 0. n.. LITHOLOGIC DESCRIPTION BORING ABANDONMENT ? (n o (soil classification, color, moisture, density, groin size/plasticity, other) WELL CONSTRUCTION DETAILS 3 = 1n O "I a U CL m o a o_ o 384 60 SW CRAVE LIGHT BROWN, 30% GRAVEL St' DIAMETER, DRY. 42 ODERjA ATE-SN DROCARBON ODOR ' S0" 12' 62 ' 64 ' 23 171 SW SAND: LIGHT BROWN, DRY, MEDIUM DENSE, VERY FINE TO MEDIUM GRAINED, WELL GRADED, MODERATE HYDROCARBON ODOR 26 30 66 68 18 95 70 SW SAME AS ABOVE, SLIGHT TO MODERATE HYDROCARBON ODOR 28 30 72 74 BENTONITE SEAL 16.7 SW SAND: PALE YELLOW BROWN, DRY, MEDIUM DENSE, VERY FINE TO MEDIUM 31 1 3 GRAINED, WELL GRADED, VERY SLIGHT HYDROCARBON ODOR 40 76 i 78 20 21.0 80 SW SAME AS ABOVE, NO HYDROCARBON ODOR 30 42 I - 82 84 27 106 SW SAME AS ABOVE, NO HYDROCARBON ODOR za ' 39 86 88 34 70- 10.7 90 SW SAME AS ABOVE, NO HYDROCARBON ODOR TOTAL DEPTH 14"I 1 1 91.5' ]OYOBIOC g/�pBP West Coast Products LLC 6J 4 Centerpointe Drive La Palma,CA 90623-1066 ,l Mailing Address: /� pp PO Box 6038 C N Artesia,CA 90702-6038 OCT 4 M I September 27,2004 VIA FACSIMILIE Central Valley Regional Water Quality Control Board 1685 E. Street Fresno, Ca 93706 Attention: Release Reporting U RE: Facili �onu�3333 U kersfield Dear Sir/Madam, Attached is an Underground Storage Tank Unauthorized Release Report in connection with a failed Enhanced Leak Detection Test. This report does not positively confirm impact to the subsurface by petroleum hydrocarbons, but rather is sent out of an abundance of caution to provide notification of a potential release as required under California Code of Regulations,Title 23, Section 2644.1,subdivision(a)(5). Please feel free to call me at(714)670-5321 with any questions. Sincerely, ichael Wilson Environmental Compliance Specialist U.S.Convenience Retail Business Cc: Inspector Steve Underwood Bakersfield Fire File DISCLAIMER: This message (including attachments, if any) contains confidential proprietary information, some or all of which may be legally privileged or otherwise protected from unauthorized use, disclosure, distribution or copying. It is for the intended recipient only. If you are not the intended recipient, you may not use, disclose, distribute, copy, print or retain this message or any part of it. If you have received this message in error,please notify us immediately by calling(714)670-5336 collect. i I 1 \140VtL./\V1\V V196/ V I VI\r\VV II'9171\ VIOnV II IVI\16.�.V 1\v��r1V` tVVn/\�I vv1\II'91�111\I"\IIVIO VIII. 1\�• VI\I EMERGENCY HAS STATE OFFICE OF EMERGENCY SERVICES FOR LOCAL AGENCY USE ONLY REPORT BEEN FILED? I HEREBY CERTIFY THAT I HAVE DISTRIBUTED THIS INFORMATION ACCORDING TO THE ❑YES ENO []YES ®NO DISTRIBUTION SHOWN ON THE INSTRUCTION SHEET ON THE BACK PAGE OF THIS FORM REPORT DATE CASE e 0 7 2 9 0 4 ° y1 M D 0 V Y SIGNED DATE NAME OF INDIVIDUAL FILING REPORT PHONE SIGNAT m Michael Wilson 714-670-5321 W REPRESENTING ®OWNER)OPERATOR ❑REGIONAL BOARD COMPANY OR AGENCY NAME p ❑LOCAL AGENCY ❑OTHER BP w ADDRESS 4 Centerpointe Drive La Palma CA 90623 STREET CITY STATE ZIP W NAME CONTACT PERSON PHONE m i BP West Coast Products LLC C1 UNKNOWN Michael Wilson 714-670-5321 yADDRESS W 4 Centerpointe Drive La Palma CA 90623 STREET CITY STATE ZIP FACILITY NAME(IF APPLICABLE) OPERATOR PHONE o Arco Facili No.3090 BP 909-868-7125 ADDRESS 0 3333 Union Ave. Bakersfield Kern 92610 W STREET CITY COUNTY ZIP ~ CROSS STREET U) 34TH/UNION = LOCAL AGENCY AGENCY NAME CONTACT PERSON PHONE m W a Office of Environmental Services,Fire Department Ralph E.Hue 661 326-3979 W w REGIONAL BOARD PHONE d6 f Central Valle y (1) NAME QUANTITY LOST(GALLONS) Gasoline 0.00 ® UNKNOWN U) (Z) m to � ❑ UNKNOWN DATE DISCOVERED HOW DISCOVERED ❑INVENTORY CONTROL ❑SUBSURFACE MONITORING ❑NUISANCE CONDITIONS ul 0 7 2 9 0 4 ® M M TANK TEST ❑TANK REMOVAL ❑ OTHER Customer top-o0 uJ m DATE DISCHARGE BEGAN METHOD USED TO STOP DISCHARGE(CHECK ALL THAT APPLY) ®UNKNOWN ❑REMOVE CONTENTS ❑CLOSE TANK 8 REMOVE C1 REPAIR PIPING Cr Ml Ml III W A A C HAS DISCHARGE BEEN STOPPED? ❑REPAIR TANK ❑CLOSE TANK S FILL IN PLACE ❑CHANGE PROCEDURE N c ❑YES ® NO IF YES,DATE ddl dal 01 1 A Y ❑REPLACE TANK ®OTHER Evaluate tank system for potential repairs SOURCE OF DISCHARGE CAUSE(S) ❑ TANK LEAK ❑ UNKNOWN ❑ OVERFILL ❑ RUPTUREIFAILURE ❑ SPILL y ❑ PIPING LEAK ® OTHER ❑ CORROSION ®UNKNOWN ❑ OTHER CHECK ONLY ONE ® UNDETERMINED ❑ SOIL ONLY ❑ GROUNDWATER ❑ DRINKING WATER-(CHECK ONLY IF WATER WELLS HAVE ACTUALLY BEEN AFFECTED) CHECK ONLY ONE ❑ NO ACTION TARN ❑ PRELIMINARY SITE ASSESSMENT WORKPLAN SUBMITTED ❑ POLLUTION CHARACTERIZATION ® LEAK BEING CONFIRMED ❑ PRELIMINARY SITE ASSESSMENT UNDERWAY ❑ POST CLEANUP MONITORING IN PROGRESS ❑ REMEDIATION PLAN ❑CASE CLOSED(CLEANUP COMPLETED OR UNNECESSARY) ❑ CLEANUP UNDERWAY CHECK APPROPRIATE ACTION(S) ❑ EXCAVATE a DISPOSE(ED) ❑ REMOVE FREE PRODUCT(FP) ❑ ENHANCED BIO DEGRADATION(IT) tAE PICA sae 0ET°use p O ❑ CAP SITE(CD) ❑ EXCAVATE&TREAT(ET) ❑ PUMP&TREAT GROUNDWATER(GR) ❑ REPLACE SUPPLY(RS) Q< ❑ CONTAINMENT BARRIER(CB) ❑ NO ACTION REQUIRED(NA) ❑ TREATMENT AT HOOKUP(HU) ❑ VENT SOIL(VS) ❑ VACUUM EXTRACT(VE) ® OTHER Complete EnflWMd Leak Detelsion process BW make arty necessary repairs or AustmeMS. Detailed description here. rn An Enhanced Leak Detection test indicated presence of a tracer(vapor)compound in samples collected during the test. This report does not fpositively confirm impact to the subsurface by petroleum hydrocarbons,but rather is sent out of an abundance of caution to provide notification of M a potential release as required under California Code of Regulations, Title 23, Section 2644.1, subdivision (a)(5). BP will evaluate the UST system and make necessary repairs. If a release was positively identified,a follow up report will be submitted. 1 la TRACER TIGHTS TEST RESULTS CUSTOMER COPY 8/30x'2004 Shirley Environmental LLC Job No: 860406 9595 Lucas Ranch Rd. AM/PM Mini Mart#3090 Rancho Cucamonga,CA 91730 3333 Union Ave. Bakersfield, CA 93305 SYSTEM STATUS SYSTEM#- PRODUCT SIZE TRACER SYSTEM STATUS Tank 1 89 10,000 W FAIL Tank 2 87 Master 10,000 R PASS Tank 3 87 Slave 10,000 G FAIL Tank 4 91 10,000 A PASS Soil permeability is greater than 89.1 darcys. GROUND WATER AND PRODUCT INFO - AT INOCULATION AT SAMPLING DEPTH FROM GRADE 08/06/04 08(16/04 WATER TANK TANK TABLE BOTTOM TOP SYSTEM# H2O PROD H2O PROD min) (in) (in) (in) (in) (in) (in) Tank 1 0.00 40.00 0.00 38.00 >144 187 67 Tank 2 0.00 83.00 0.00 70.00 >144 182 62 Tank 3 0.00 82.00 0.00 69.00 >144 177 57 I Tank 4 0.00 38.00 0.00 49.00 >144 172 52 I TEST EVENTS INSTALLATION INOCULATION SAMPLING ANALYSIS 08/06/04 08/06/04 08/16/04 0824104 FILL RISER—SPILL BUCKET TEST TANK# PASS/FAIL Tank I Pass Tank 2 Pass Tank 3 Pass Tank 4 Pass 1 declare under penalty of perjury that I am a licensed tank tester in the State of California and that the information contained in this report is true and correct to the best of my knowledge. lnstall/lnoculate-:�QLA- CA Lic.No:O_j�-864y Signature __iG Ore g Date 9-" Sampler 1?DBcR-7' Svr'o CA Lic.Noio Z-OdAo Signature /L-9 Date T-t3-a TRC Analyst i ne " st CA Lic.No:93-I S6 d Signature_ Date l9�r r i i I ' R Tank 4 Praxair Services, Inc. 10,000 gal 91 9 Tracer (A) / - 10 1L IS 16 1 V L . -----------I_--------1-----,---� 1 T Q U �I 1 F ® I 1 D I 12 1 1 7 ! 1 I 1 I• 17 I •71 I I 1 1 V L I STP O / I I LB •1 I S t o r e 5 1L� A 1 Tank 3 13 •j I i j 1 I 10,000 gal I 1 I 1 / �•(V F--•- 1 1 1 1 87 Slai7e I 1. 10 1 I 1 �0 1 Tracer (OI 1 1 1 1. 19 P ! - 31 1 v f 11 Tank 2 it 10.000 gal 1 •1 A 87 Master I 1B1°nk 2 • 1 Tracer (R) 1 � / Tank 1 ! �1 10,000 gal M 1 20 89 w /• zl u Tracer (W) � a ! ! ! I ! - 1 1 ! 1 1- 22 I Dumps t er 1 1 , 1 1 D ! vrnae -----------------•_..1 ° 25 24 23 860406 S H I R L E Y E N V I R O N M E N T A L E X P L A N A T I 0 N A M / P M M i n i M a r t # 3 0 9.0 •1 Sampling Probe Location N 3 3 3 3 u N I o N A V e N u E B A K E R S F I E L D . C A L I F O R N I A i ------ Approximate Pipeline Location O 10 20 S A M P L I N G L O C A T I O N S i t �11�:850006-1 Bir�.A F i g u r e 1 Ar°,B6°•O6-• - Date,09.01-0♦ ' i•w3� R Tank 4 Praxair Services, Inc. 10,000 gal 91 9 (no) , Tracer [A) r.4 10 4N01 11 uvm 15 Iva) 16 Ivor I I I�1 I I I ®'~- �1 I I (Nip. F OA f I D I 12 IND) I D 1 1 I 1 I I I• 17 INDI 1 V •.7 INDI l 1 1 I I I j 1 „ 1 1 �l 1 Y I 1 1 I I � TY O- I IM 1 1 (Mal l 1B '1 I I •1 I 1 I S t o r e lo.000s) 5 13 - A I Tank 3 1 1 1 1 6" 10,000 -gal I j I I V.1-�� I I I I I I K.lAl15T •�I INDI 97 Slave I. 14 IND) I I Io.000U a�6 0- II Tracer [O) I D I 1 D I. 19 I)m1 I - g /��.,��V I • aft)) Tank 2 II I FI-� 3T II 10,000 gal I f 11 I A 87 Master IBl'DR Tracer [R] t f Tank 1 10,000 gal 1 / 20 INDI 89 41 /• 21 INDI Tracer [WJ a / / I i 1•22 (ND) j Dumpater I iI / : / vanes$-,-- -------------- 0 2$ INDI 24 (ND) 23 (ND) I I 860406 I S H T R L E Y E N V I R O N M E N T A L i E X P L A N A T I O N A M / P M M i n i M a r t # 3 0 9 0 1 •1 Sampling Probe Location j N 3 3 3 3 U N I O N A V E N U E I ------ Approximate Pipeline Location B A K R R 6 F I E L D . C A L 1 F 0 R N I A 0 10 20 T r a c e r [ G ) D i s t r i 10.000) Soil Gas Sample Value (µg/L) ►ue:s9o.o6-A 9t.a,w f e e t A.c a6o4o6-4 Dat-09-01-00 F i g u r e 1 a I PRAWA1R Tank 4 Praxair Services, Inc. 10,000 gal I � 91 9 10.7 9511 Tracer [A) t + _ 10 11.09731 11 11.609.1 15 10.0734. 16 10.021s) 1 I v A. -_- 1"- 1 �---� _ 1 �1 i I F. ��` 1 I D 1. 12 10.05911 1 p 1 10.77911 8 _ A I 1 1 1 1 1 I 1 1 1• 17 10.01691 1 ,7 10.FloT1 1 1 1 1 ! V I_�` 1 1 I I 1 1 9T O I 10.0361•1 I 40.1061 10 •1 1 I 1 F S t o r e 40.14611 5.� A 1 Tank 3 13 1 I 1 II ,v _ .61 10,000 gal I 1 1 1 ! ST �I. 87 slave 1. 14 10.0751 1 1x01 0�F O ! Tracer [0] I 12!. 19 10.01011 f 1 (o. 1611 lwr I�L ' _ I 3 1 V`I f 1 1 10.0091 Tank 2 ST o / 10,000 gal f I 1 A 87 Master 1 1elenk Tracer [R) `10.00631 2 • I _ 1 1 �1 '&D' f Tank 1 / I �f 10,000 gal N / 20 10.01591 89 0) 1. 21 40.02511 Aj D f 1 Tracer [W) 10 / a 1 / / I I / /• 22 10.01161 Dumpeter / / o / o 25 24 10.01051 23 10.01191 40.0131) j 860406 I S H I R L E Y E N•V I R O N M E N T A L E X P L A N A T I O N A M / P M M i n i M a r t # 3 0 9 .0 •1 Sampling Probe Location N lV 3 3 3 J U N I O N A V E N U E ------ Approximate Pipeline Location B A K E A S F I E L O C A L I F O R N I A 0 10 20 0.00071 Soil Gas Sample Value (pq/L) T r a c e r [ W ] D i a t r i b u E e a t 111e:860606-e llae:A I Arc�B60606-• Dsce:o9-01-06 F i g u r e l b i = rR � Tank a Praxair Services, Inc. 10,000 gal i 91 9 flow Tracer tA] f --� 10 11 1", 15 INO, 16 INDI 1 1 ! I 1 I ( 1 i I F: TF O 1 / 1 IloD) 8`� A 1 I I• 12 IloD, I 1 1I I I 1 1 1. 17 INDI •' (ND) 1 1 I 1 / .V L I I I 1 I I 1 '1 1 1 1 1 � F TP O— � I leDl I 1 flop. 18 '1 1 S t o r a loDl 5 A 1 Tank 3 1.3 •� j 6j1 10,000 gal j r) —I 87 Slave �• ld INm j 1 ( F�'% T O ! Tracer t0] 1 1 1 (• 19 INw fww 4 r A r IloD/ 1 ° ! J Tank 2 1 I�WF-C�71 / j I F ST O 1 10,000 gal I j • 1 A 87 Master 1 ' I *elank Tracer (R) /- (ODI / 2 1 IND( 1 Tank 1 / -1 10,000 gal / 20 IND) 89 V i 21 1"? / Tracer (W) / � a � / / / / / r /• 22 fnD( 7 / Dumpater / / 1 / / I I / O / Vanes 0 ---------------� O ZS fY01 ZO mol 23 flew I 860406 S H I R L E Y E N V I R O N M E N T A L E X P L A N A T I O N A M / P M M i n i M a r t # 3 0 9 0 •1 Sampling Probe Location 7�� i �.V 3 3 3 3 U N I O N A V E N U E 'I ------ Approximate Pipeline Location B A K s R s F I e L D . C A L I F 0 R N I A 0 10 20 Soil gas Sample Value (Jug/L) T V H C D i s t r i b u t i o n e.000ll t e e C ►11-0 6 060 6-C $I—A Are,060406-6 r-6.09-01-04 F 1 Q D r E' 1 C i I Tracer Tight ® S I T E I N F O R M A T I O N F 0 R M I � Inoculation ��` j"IaQ�}(t TracerTighllD ,\O50 state Technician J IV 0: License # :cn�3—t(�4 LJ I Tracer Job # sampling TracerTighte state Technician VrxL NSW=a ID \IGSO License # 03ri(AtA Site AKA,?H Hasa KK Kn V#3090 1 c arrilliate �71�1(aRLay E1jVlteNME1J AL site �� ) q Address 3333 uv%zon Avc, City : ,K(j,��jc1Q state Ca Zip : UlaS Precision Test ❑ Leak Delineation ❑ Depth to ground:water in tank pit j Initial Test All Water Ingress E] Inoculation date 8 / 6 / 04 at inoculation/initial visit (in inchea): 1.. i (see box at right) Depth to ground water in tank pit Annual Teet [] p g/ ( ) 44 in. j Monthly Monitoring ❑ Sampling date � � /((p /G� et sampling/second Itn second visit in inches ' Aeleat ❑ Moni To be used for.ALL Water Ingress Tests Maximum Sample Vacuum Tank(s) were constantly k completely i Result Verification❑ p submerged in ground water for the ❑ ® i Residential Tanks) ❑ (Highest probe Vacuum on site) r. !n Hg . duration of the test 7 YES NO $ s .a o $ � y � 0 5e �6 1e 1 At inoculation At sampling Tank No. Product 204 Volume $ F1 n o ° Tj g3 g•Hsl1 level Tow Uquid Hso level Tetal uqula °E (in gallons) o � ° w In task level in teak level ~ J 0 a `,� V ^ti 6 "1 t1 x a x a q g o o ° ° y R (in inches) (In lnohes (in inches (1n inches o (v' ° oo O D Q � e) $l M1UTeV, ° 10iooa 10x11 R-,76o � po 0 as o t � ° � ° Asa 3 87 SLAUC ° No �o,000 1,oK1� 6�boo No 0 9L o e o ® a I vu No y �1 ° ® 101000 11b,K17 A-1011 h N0 o 1 , No No Too® a ❑ ❑ ❑ ❑ O ❑ TBe No "A No via NO ❑ ❑ ❑ ❑ ❑ ❑ I TTa No TU No Tag No ❑ ❑ ❑ ❑ ❑' ❑ ne No To No yes No ❑ ❑ ❑ ❑ ❑ ❑ no NO Y® No YBa No Comments :�r�tik: 2ar� o►�!'_\4r4,OiAad_-- -------- Revised 8-27-98 Rev. 03 TI®teal R!lesPl� Ct►!00//I%00 I CONFIDENTIAL Praxair Services, Inc. Technical Solutions for the Industrial World. UCISCO �T��t B.�et, r... Site Information For Enhanced Leak Detection Sites Submit Completed Form IMth Each Jobl Tee�iri® r�O6,g..rw. Job W f Q(OO e-6`04 site Nam Fa nose of test:(Pia"on=iw w?Wift 1OW'of acW Unksla le secaadacy doom DtegaWosy daeodve7 New lnaail UM? &w aay�0of!t itmrtteoe aad eetbak c�ra r,�etatsrr+:sJoak Sgltl�Ttat: •Z�1:.�`' Zffi T® Z� �3 (Paas/Fa� 1>6b (Fasa/F'aii) TvneetSSemoPamn.(Suatloal fSSs'6mel ���4� vent Lars rra gs 'ti r 2L t LS-E4 awso Z6 yaoofBmovarI&Mpvbea T1�. awm- as Lam, Zara.3pg=6 S Typeo.ofBadcM CVMM$d Caw UA Al Conommut n= ( _ Iimac r*iV eWad ooi>ee (stxt) (l W.,.h) (otba5 veotLma rbm&71q &i3h1e_WM (SteQ O (0*" ' -- vapor R'QYPU*Watt 'M_�Kyw (Simi) t 1 (O&M Vanorlraootev ) (AaeiaQ Imo QM'=' ctiorc (Sealed to took tap) (Dirt) -baked to risi at tmk top) (jtmroat-bolted to asertwey) flvafiQ Pmcevi t�c��.lr.a. � . Wetrin B—F 1fE.S.,. . Depth from CLZ Witterin Lino tmneh: YES Dq&fsom amfaor Water in tank pit YES f Depth tom ssnace: Tine Deteetoes unapt �y - Fibethmet eleeaiotietn: Shape(draw pfctateif txcenoaty): Depth to top s4petum of site peeame VCdfYiag caoMcn of site at and of iastailatioa l fo, / - - - — I If 3/ I .1 1 ocp,e � 20 �L ��► u gq 17 HASTt R a't S�Auf 9 l / luluw 10,000 •1010110 lo,0w 10M 10X17 119y'17 lox?? tu-M 11-76u 640DO A•1013 4 I FLU Out Form Completely It Please Print Clearly II Map Check List Tank Details Total Q Tank Outlines Nearb Buildin a W Tank Size Number Number Of N ° y g ®Numbered Probe Locations O Tank Size On Site Piping Locations Ground Coverings Probe Lengths Total to Tank Product ©Dispensers Identified lank Location Number p Tracer In Tank Length 1.5' 5' �D of Probee Total Vent Pipes North Direction Number 6�kYll pipe Number Of rj Of C !J� Sump Pump Tanks i y]Fill Locations E)Monitoring Wells Probes J g5 ❑ Manifolds Tested t loch = 2P it. Trecr� Res�e�rD Cuiooie/ioo i i ATTACHMENT 2. SOIL BORING AND SAMPLING PROCEDURES CENTRAL SIERRA ENVIRONMENTAL, LLC'S STANDARD OPERATING PROCEDURES FOR SOIL BORING AND SAMPLING PROCEDURES PRE-DRILLING PROTOCOL Prior to the start of drilling, necessary permits, site access agreements, and/or encroachment permits are obtained. "As-built" 'drawings are obtained if possible. At least 48 hours prior to drilling, Underground Service Alert or an equivalent utility notification service is notified. A geophysical survey may be conducted. to locate subsurface utilities. Site plans and/or "as-built" drawings are compared to actual conditions observed at the site. The property owner/retailer is interviewed to gain information about locations of former UST systems (including dispensers, product lines, and vent lines). A visual inspection is made of the locations of the existing UST'system, and scars and patches in pavement are noted. The emergency shut-off switch is located for safety purposes. The critical zone, which is defined as 10 feet from any part of the UST system, is identified, and any proposed drilling locations within the critical zone may be subject to special hole clearance techniques. Drilling locations within the critical zone are avoided if possible. Notifications are made at least 2 weeks in advance of drilling to the property owner, client representative, on-site facility manager, regulatory agency, and/or other appropriate parties. A site-specific, worker health and safety plan for the site is available on site at all times during drilling activities. Prior to commencing drilling, a health and safety meeting is held among all on-site personnel involved in the drilling operation, including subcontractors and visitors, and is documented with a health and safety meeting sign-in form. A traffic control plan is developed prior to the start of any drilling activities for both on-site and off-site drilling operations. The emergency shut-off switch for the service station is located prior to the start of the drilling activities. A fire extinguisher and "No Smoking" signs (and Proposition 65 signs in California) are present at the site prior to the start of the drilling activities. The first drilling location is the one located furthest from any suspected underground improvements in order to determine the natural subsurface conditions, to be able to better recognize fill conditions, and to prevent cross contamination. For monitoring wells, a 2 x 2-foot square or 2-foot diameter circle is the minimum removal. For soil borings and push-type samplers, the minimum pavement removal is 8-inches. When pea gravel, sand, or other non-indigenous material is encountered, the drilling location will be abandoned unless the absence of subsurface facilities can be demonstrated and client approval to proceed is obtained. If hole clearance activities are conducted prior to the actual day of drilling, the clearance holes are covered with plates and/or backfilled. The minimum hole clearance depths are 4 feet below grade (fbg) outside the critical zone and 8 fbg within the critical zone and are conducted as follows: • 0 to 4 fbg: The area to be cleared exceeds the diameter of the largest tool to be advanced and is sufficiently large enough to allow for visual inspection of any obstructions encountered. The first 1 to 2 feet is delineated by hand digging to remove the soil, then the delineated area is probed to ensure that REVISED 3/29/02 ' LSE's Standard Operating Procedures for Soil Boring and Sampling Procedures Page 2 no obstructions exist anywhere near the potential path of the drill auger or push-type sampler. Probing is extended laterally as far as possible. Hand augering or post-hole digging then proceeds, but only to the depth that has been probed. If subsurface characteristics prohibit effective probing, a hand auger is carefully advanced past the point of probing. In this case, sufficient hand augering or post-hole digging is performed to remove all the soil in the area to be delineated. For soil borings located outside of the critical zone, an attempt should be made to probe an additional 4 feet. • 4 to 8 fbg: For the soil borings located inside the critical zone, probing and hand clearing an additional 4 feet is performed. If probing is met with refusal, then trained personnel advance a hand auger without excessive force. An alternate or additional subsurface clearance procedures may also be employed,-as required by clients, permit conditions, and/or anticipated subsurface conditions (for example, near major utility corridors or in hard soils). Alternate clearance techniques may include performing a geophysical investigation or using an air knife or water knife. If subsurface conditions prevent adequate subsurface clearance, the drilling operation is ceased until the client approves a procedure for proceeding in writing. If any portion of the UST system is encountered, or if there is any possibility that it has been encountered, the work ceases, and the client is notified immediately. If there is reason to believe that the product system has been damaged, the emergency shut-off switch is activated. The client will decide if additional uncovering by hand is required. If it is confirmed that the UST system has been encountered, tightness tests are performed. The hole is backfilled only with client approval. DRILLING AND SOIL SAMPLING PROCEDURES Soil boring are drilled using one of the following methods: • Manual drilling: Manual drilling utilizes a 2-inch-OD, hand auger manufactured by Xitech Industries, Art's Manufacturing Company, or similar equipment. Soil samples are collected with a drive sampler, which is outfitted with 1.5-inch by 3-inch steel or brass sleeves. The specific equipment used is noted on a soil boring log. • Truck-mounted, powered drilling: Truck-mounted, powered drilling utilizes hollow-stem flight auger drilling, air rotary drilling, or percussion hammer drilling, or similar technologies. Soil samples are collected in steel or brass sleeves with a California-modified, split-spoon sampler or, for specific projects, a continuous sampler. The specific equipment used is noted on a soil boring log. • Direct push sampling: Direct push sampling utilizes Geoprobes®, cone penetrometer testing rigs, or similar technologies. Soil samples are collected with a drive sampler, which is outfitted with steel or brass sleeves. The specific equipment used is noted on a soil boring log. REVISED 3/29/02 ' CSE's Standard Operating Procedures for Soil Boring and Sampling Procedures Page 3 Before each soil sampling episode, the sampling equipment is decontaminated using a non-phosphate soap wash, a tap-water rinse, and a deionized water rinse. The drill string is decontaminated with a steam cleaner between each soil boring (truck-mounted rigs). Soil samples that are collected in steel or brass sleeves are covered with aluminum foil or Teflon TM tape followed by plastic caps. If EPA Method 5035 is required, then 5 to 20 grams of soil is extracted from the sample and placed in methanol-preserved containers supplied by the laboratory, or sub samples are collected using Encore® samplers. During the drilling. process, soil samples and cuttings are field screened for VOCs using a photoionization detector calibrated to 100 parts per million by volume isobutylene. Any soil staining or discoloration is visually identified. Soils are classified according to the Unified Soil Classification System. Specific geologic and hydrogeologic information collected includes grading, plasticity, density, stiffness, mineral composition, moisture content, soil structure, grain size, degree of rounding, and other features that could affect contaminant transport. All data is recorded on a soil boring log under the supervision of a geologist registered in the state in which the site is located. The samples are labeled, sealed, recorded on a chain-of-custody record, and chilled to 4°C in accordance with the procedures outlined in the California State Water Resources Control Board's Leaking Underground Fuel Tank Field Manual and the Arizona Department of Environmental Quality's Leaking Underground Storage Tank Site Characterization Manual. Sample preservation, handling, and transportation procedures are consistent with Central Sierra Environmental, LLC's quality assurance/quality control procedures. The samples are transported in a chilled container to a state-certified, hazardous waste testing laboratory. Cuttings from the, soil borings are stored in 55-gallon, Department of Transportation (DOT)-approved drums, roll-off bins, or other appropriate containers, as approved by the client. Each container is labeled with the number of the soil boring(s) from which the waste was derived, the date the waste was generated, and other pertinent information. The drums are stored at the site of generation until sample laboratory analytical results are obtained, at which time the soil is disposed of appropriately. A soil boring log is completed for each soil boring and includes the following minimum information: • date of drilling; • location of soil boring; • project name and location; soil sample names and depths; • soil descriptions and classifications; • standard penetration counts (rigs); • photoionization detector readings; • drilling equipment; • soil boring diameter; • sampling equipment; REVISED 3/29/02 • CSE's Standard Operating Procedures for Soil Boring and Sampling Procedures Page 4 • depth to groundwater in soil boring; • name of person performing logging; • name of supervising registered geologist; and • name of drilling company (rigs and direct push). SOIL BORING COMPLETION PROCEDURES All soil borings are either properly abandoned or completed as a well. Abandonment Each soil boring that is not completed as a well is backfilled with bentonite grout, neat cement, concrete, or bentonite chips with a permeability less than that of the surrounding soils, and/or soil cuttings, depending on local, regulatory requirements or client instructions. Grout is placed by the tremie method. Backfilling is performed carefully to avoid bridging. The type of backfill material is noted on the soil boring log. Well Installation Wells are designed according to applicable state and local regulations as well as project needs. Details of the well design and construction are recorded on the soil boring log_and include the following minimum information (in addition to the items noted above for soil borings): • detailed drawing of well; • type of well (groundwater, vadose, or air sparging); • casing diameter and material; • screen slot size; • well depth and screen length (±1 foot); • filter pack material, size, and placement depths; • annular seal material and placement depths; • surface seal design/construction; • well location (±5 feet); and • well development procedures. Groundwater monitoring wells are generally designed with 30 feet of slotted casing centered on the water table, unless site conditions, project needs, or local regulations dictate a different well design. The sand pack is placed at least two feet above the top of the screen, and at least 3 feet of low permeability seal material is placed between the sand pack and the surface seal. The sand pack and low permeability seal material are placed in the annular space from the bottom up using the tremie method. When drilling in asphalt, a 24-inch round cut is made for the well pad. When drilling on concrete, a 2 x 2-foot square is sawcut. The well cover is traffic-rated and has a white lid with a black triangle painted on it (3 inches per side) or a black lid with a white triangle (3 inches per side). The completed well pad should is concrete of matching color with the existing surface. The well number is labeled on the outside of the well box/pad REVISED 3/29/02 • LSE's Standard Operating Procedures for Soil Boring and Sampling Procedures Page 5 and the inside of the well box. The number on the outside is painted on with a stencil, stamped, or attached to the well with a metal plate. The number on the inside is written on the well cap with waterproof ink. The casing has a notch or indication on its north side indicating a unique measuring/surveying point. Well development is conducted by simple pumping if bridging of the screen does not occur. If bridging occurs, well surging is conducted for adequate well production. Well surging is created by the use of surge blocks, bailers, or pumps, whichever method is most appropriate for the well use. Only formation water is used for surging the well. Well development continues until non-turbid groundwater is produced or turbidity stabilizes. All purged groundwater is held on site in covered 55-gallon DOT-approved drums or other appropriate containers until water sample analytical results are received. The elevation of the north side of the top of well casing (or other appropriate reference point from which the depth to groundwater can be measured) is surveyed to an accuracy of±0.01 foot. All measurements are reproduced to assure validity. Surveying is performed by a state-licensed surveyor if required by state or local regulations. In the State of California, wells are surveyed in accordance with AB2886. DATA REDUCTION The data compiled from the soil borings is summarized and analyzed. A narrative summary of the soil characteristics is also presented. The soil boring logs are checked for the following information: • correlation of stratigraphic units among borings; • identification of zones of potentially high hydraulic conductivity; • identification of the confining layer; • indication of unusual/unpredicted geologic features (fault zones, fracture traces, facies changes, solution channels, buried stream deposits, cross-cutting structures, pinchout zones, etc.); and • continuity of petrographic features such as sorting, grain-size distribution, cementation, etc. Soil boring/well locations are plotted on a properly scaled map. If appropriate, soil stratigraphy of the site is presented in a scaled cross section. Specific features that may impact contaminant migration, e.g., fault zones or impermeable layers, are discussed in narrative form and supplemented with graphical presentations as deemed appropriate. REVISED 3/29/02 ATTACHMENT 3. WORKER HEALTH AND SAFETY PLAN WORKER HEALTH AND SAFETY PLAN FOR UNDERGROUND STORAGE TANK INVESTIGATIONS SITE-SPECIFIC INFORMATION Site Address: 3333 Union Avenue, Bakersfield, California Name of Business Occupying Site: ARCO AM/PM Mini Market No. 3090 BP Contact: Mr. Jack Oman Owner Tel. #: (714) 670-3958 BFDHMD Contact: Mr. Howard Wines III Tel. #: (661) 326-3659 FIELD ACTIVITIES AND GOALS OF THIS INVESTIGATION: Drill six soil borings to assess gasoline hydrocarbons in soil. KNOWN HAZARDS AT THE SITE INCLUDE: Gasoline hydrocarbons KEY PERSONNEL AND RESPONSIBILITIES: NAME RESPONSIBILITIES Mark R. Magargee, PG, CHg SITE SAFETY OFFICER - Primarily responsible for site safety, response operations, and protection of the public. Responsible for work site inspections to identify particular hazards and define site (661) 325-4862 security. Mark R. Magargee, PG, CHg PROJECT MANAGER - Primarily responsible for site characterization. The project manager delineates authority, coordinates activities and functions, and directs activities related to mitigative efforts of cleanup (661) 325-4862 contractors. Mark R. Magargee, PG, CHg SITE INVESTIGATIVE PERSONNEL - Responsible for actual field work including sampling, monitoring, equipment use, and other related (661) 325-4862 tasks as defined by the project manager. ANTICIPATED WEATHER CONDITIONS FOR THIS AREA DURING THE PROJECT'S DURATION WILL BE: Temp. range: 90-100°F Humidity: 20-40% Ambient temp.: 95°F Potential for heat stress: High: X Medium: Low: ANTICIPATED PROTECTION LEVEL DURING THIS PROJECT* Level "D" *Will be upgraded or downgraded to fit situations as they arise. EMERGENCY INFORMATION: All emergency calls: 911 Closest hospital with emergency room: Bakersfield Memorial Hospital 420 34th Street, Bakersfield, California, (661) 327-4647 Map Showing Route from Site to Hospital Attached? Yes: X No: SAN FRANCISCO A '90 /00 BAKERSFIELD O� yti LOS ANGELES s _W-Columbus St v SAN DIEGO Columbus St 40th St: Miner St. a e� m S LMontrosa St .38th z m Bakersfield Loma v- - 'S '.: E Memorial - — Hospital Guy. GO m Bernard Si ..... 33rd:St SITE Jeffersdn a� MR. MUNTHER HAWATMEH 32nd St :_rn :: o.. ...._� Lincoln:S! ARCO AM/PM MINI MARKET NO.3090 31.st:St:... E E Bake'ce geld Flower sr. . 3333 UNION AVENUE a - Quinc Y Sf Qui BAKERSFIELD, CALIFORNIA HOSPITAL MAP CENTRAL SIERRA ENVIRONMENTAL, LLC r r WORKER HEALTH AND SAFETY PLAN FOR FUEL STORAGE TANK SITE INVESTIGATIONS This document outlines Central Sierra Environmental, LLC.'s (CSE's) worker health and safety plan for its employees to be used at City of Bakersfield fuel storage tank site investigations. Site-specific information is provided on the cover page to this document. This worker health and safety plan was developed by CSE's through consultation of the following documents: • OSHA 29 CFR 1910 - "Hazardous Waste Operations and Emergency Response, Final Ruling," March 1989; • NIOSH/OSHA/USCG/EPA "Occupational Safety and Health Guidance Manual for Hazardous Waste Site Activities," October 1985; and • CSE's Corporate Health and Safety Program. This worker health and safety plan is divided into the following categories: 1. Job Hazard Assessment; 2. Exposure Monitoring Plan; 3. Personal Protective Equipment; 4. Work Zones and Security Measures; 5. Decontamination and Disposal; 6. Employee Training; and 7. Emergency Procedures. 1.JOB HAZARD ASSESSMENT Immediate tasks at petroleum release sites include an evaluation of any present or potential threat to public safety. Questions need to be answered regarding the dangers of significant vapor exposures and potential explosion hazards. Potential Chemical Hazards The chemical components of gasoline that are the most dangerous to site workers are the volatile aromatics, benzene, toluene, ethylbenzene, xylene, and potentially, organic lead (see Appendix 1 for Material Safety Data Sheet). Additionally, solvents such as 1,2-dichlorobenzene and 1,2-dichloroethane may also be used as cleaning solutions at service stations. The primary health risks associated with each of these chemicals are described below. • I Worker Health and Safety Plan Page 2 Gasoline - Suspected human carcinogen. A TLV of 300 ppm or 900 mg/m3 has been assigned to gasoline. This value of 300 ppm was assigned based on an average of 3 percent benzene (10 ppm TLV) in gasoline. Low-level inhalation exposure to gasoline can cause irritation to the eyes, nose, and respiratory system; headache; and nausea. Benzene Suspected human carcinogen. A TLV of 10 ppm or 30 mg/m3 has been assigned to benzene. Benzene has a low odor threshold limit of 1.4 ppm. Low-level inhalation exposure to benzene can cause irritation to the eyes, nose, and respiratory system; headache, and nausea. Toluene - A TLV OF 100 ppm or 375 mg/m3 has been assigned to toluene. Toluene has a low odor threshold limit of 2.1 ppm. Low-level inhalation exposure to toluene can cause fatigue, weakness, confusion, and euphoria. Ethvlbenzene -A TLV of 100 ppm or 435 mg/m3 has been assigned to ethylbenzene. Ethylbenzene has a low odor threshold limit of 2 ppm. Low-level inhalation exposure to ethylbenzene can cause irritation to the eyes and mucous membranes. Xylene - A TLV or 100 ppm or 435 mg/m3 has been assigned to xylene. No low odor threshold limit has been established for xylene. Low-level inhalation exposure to xylene can cause dizziness, excitement, and drowsiness. 1,2-Dichlorobenzene - A TLV of 50 ppm or 306 mg/m3 has been assigned to 1,2-dichlorobenzene. 1,2-dichlorobenzene has a low odor threshold limit of 4.0 ppm. Acute vapor exposure can cause coughing, dizziness, and drowsiness. It may cause skin irritation. 1,2-Dichloroethane - A TLV of 200 ppm. No data is available concerning odor threshold. Acute vapor exposure can cause coughing, dizziness, drowsiness, and skin irritation. Tetraethyl Lead -A TLV of 0.1 mg/m3 has been assigned to tetraethyl lead. Tetraethyl lead is a colorless or red-dyed liquid at atmospheric conditions. No data is available concerning odor threshold. Acute vapor exposure can cause insomnia, delirium, coma, and skin irritation. Potential Physical Hazards Trenching - Dangerously high fuel vapor levels will be monitored using an LEL meter. The presence of underground utilities are also of concern, and Underground Service Alert will be notified in advance of any trenching work for identification of all underground utilities in the immediate area. Worker Health and Safety Plan Page 3 Drilling - Dangerously high fuel vapor levels will be monitored using an LEL meter. The presence of underground utilities are also of concern, and Underground Service Alert will be notified in advance of any drilling work for identification of all underground utilities in the immediate area. Sampling - Use of personal protective equipment will minimize the potential for exposure of personnel conducting site investigation activities. Heat stress will be monitored by each individual and controlled through regular work breaks as outlined in the American Conference of Governmental Industrial Hygienists' TLV's for heat stress conditions. 2. EXPOSURE MONITORING PLAN Potential exposure hazards found at fuel storage tank sites primarily include toxic airborne vapors from the petroleum release. The most dangerous airborne vapor likely to be encountered during a fuel storage tank investigation is benzene. Gasoline vapor concentration levels will be monitored in the breathing zone with a PID calibrated to benzene. When the action level of 150 ppm (one half the TLV of gasoline) is detected in the breathing zone, respiratory protection will be required utilizing full-face or half-face respirators with organic vapor cartridges. Monitoring for combustible gases will also be performed using an LEL meter when vapor concentrations above 2,000 ppm are detected with the PID. The action level is 35 percent of the LEL for gasoline vapors or 4,500 ppm. If this level is attained or exceeded, the work party will be IMMEDIATELY withdrawn. 3. PERSONAL PROTECTIVE EQUIPMENT The level of protection during the site investigation will usually be level "D." Level D protective equipment includes coveralls, safety boots, safety glasses, gloves, and hard hats if drilling or trenching operations are in progress. Upgrading the protection level would be based on airborne benzene concentration levels equal to or exceeding the action level. An upgrade to level "C" protection would be required if the action level is equaled or exceeded. Additional equipment required for level C would be a full-face or half-face air purifying canister-equipped respirator and TyvekTM suits with taped arm and leg seals. If the action level is met or exceeded (35 percent) for the LEL, work will cease until the vapor level is measured to be below 20 percent of the LEL. r Worker Health and Safety Plan Page 4 A fire extinguisher will be maintained on site. Decisions for workers' safety are based on a continual evaluation of existing or changing conditions. 4. WORK ZONES AND SECURITY MEASURES To facilitate a minimum exposure to dangerous toxic vapors and/or physical hazards, only authorized persons will be allowed on the job site. Work zones will be defined by CSE staff who will also be responsible for maintaining security within these zones. Only the minimum number of personnel necessary for the fuel storage tank investigation will be present in the work zone. 5. DECONTAMINATION AND DISPOSAL CSE's standard operating procedures establish practices that minimize contact with potentially contaminated materials. Decontamination procedures are utilized if there is suspected or known contamination of equipment, supplies, instruments or any personnel surfaces. Soap and water will be utilized to remove contaminants from personnel surfaces as well as equipment and instruments. Contaminated wash water will be disposed of in accordance with procedures outlined in the LUFT guidance documents. 6. EMPLOYEE TRAINING All CSE employees working on the site will have had, at a minimum, the required 40-hour OSHA Training for Hazardous Waste Site Activities (29 CFR 1910, 120), which includes training in the use of personal protective equipment. Individualized respirator fit testing is required of all CSE employees working at the site. 7. EMERGENCY PROCEDURES CSE employees are trained in emergency first aid, and emergency first aid provisions will be brought to the site. In the event of overt personnel exposure (i.e., skin contact, inhalation, or ingestion), the victim will be transported to and treated at the closest hospital (see Hospital Map). A 911 call will dispatch EMT's to the scene of the injury. If warranted by the severity of the injury, EMT's would summon an air ambulance. r APPENDIX 1. MATERIAL-SAFETY DATA SHEET r i APPENDIX 1. MATERIAL SAFETY DATA SHEET Chelron Plus Unleaded Gasoline MSDS#3205 Rev#23(12/08/00) CROW Material Safet y Data Sheet Cheer®n Plus Unleaded Gasoline MSDS: 3205 Revision #: 23 Revision Date: 12/08/00 Click here to search the product data sheet database 1. CHEMICAL PRODUCT AND COMPANY IDENTIFICATION CHEVRON MID-GRADE UNLEADED GASOLINE PRODUCT NUMBER(S): CPS201001 CPS201003 CPS201004 CPS201006 CPS201007 CPS201008 CPS201010 CPS201011 CPS201018 CPS201021 CPS201025 CPS201031 CPS201032 CPS201033 CPS201034 CPS201036 CPS201037 CPS201038 CPS201041 CPS201043 CPS201046 CPS201048 CPS201064 CPS201208 CPS201210 CPS201211 CPS201212 CPS201230 CPS201231 CPS201232 CPS201260 CPS201261 CPS201262 CPS201271 CPS201272 CPS201273 CPS201280 CPS201281 CPS201282 CPS201288 CPS201290 CPS201291 CPS201292 CPS201851 CPS201852 CPS201858 CPS201859 CPS201860 SYNONYM: Calco Mid-Grade Unleaded Gasoline CHEVRON Plus Unleaded Gasoline COMPANY IDENTIFICATION EMERGENCY TELEPHONE NUMBERS Chevron Products Company HEALTH (24 hr): (800)231-0623 or Marketing, MSDS Coordinator (510)231-0623 (International) 6001 Bollinger Canyon Road TRANSPORTATION (24 hr): CHEMTREC San Ramon, CA 94583 (800)424-9300 or (703)527-3887 Emergency Information Centers are located in U.S.A. Int'1 collect calls accepted PRODUCT INFORMATION: MSDS Requests and Technical Information: (800) 689-3998 http://library.cbest.chevron.com/lubes/chevmsd.../33ef0475182faded8825661f005d73f6?OpenDocument(1 of 18)[11/26/2001 6:29:42 PM] Che\Aron Plus Unleaded Gasoline MSDS#3205 Rev#23(12/08/00) SPECIAL NOTES: This. MSDS applies to: Federal Reformulated Gasoline, California Reformulated Gasoline, Wintertime Oxygenated Gasoline, Low RVP Gasoline and Conventional Gasoline. 2. COMPOSITION/INFORMATION ON INGREDIENTS 100.0 % CHEVRON MID-GRADE UNLEADED GASOLINE CONTAINING COMPONENTS AMOUNT LIMIT/QTY AGENCY/TYPE GASOLINE (GENERIC) 100.00% 890 mg/m3 ACGIH TWA 1480 mg/m3 ACGIH STEL 2000 mg/m3 OSHA PEL POTENTIALLY INCLUDING BENZENE Chemical Name: BENZENE CAS71432 < 4.90% 0.5 ppm ACGIH TWA 2.5 ppm ACGIH STEL 1 ppm OSHA PEL 5 ppm OSHA CEILING 10 LBS CERCLA 302.4 RQ ETHYL BENZENE Chemical Name: BENZENE, ETHYL- CAS 100414 100 ppm ACGIH TWA 125 ppm ACGIH STEL 100 ppm OSHA PEL 1,000 LBS CERCLA 302.4 RQ XYLENE Chemical Name: BENZENE, DIMETHYL- CAS 1330207 100 ppm ACGIH TWA 150 ppm ACGIH STEL 100 ppm OSHA PEL 100 LBS CERCLA 302.4 RQ http://Iibrary.cbest.chevron.com/tubes/chevmsd.../33ef0475182faded8825661 f005d73f6?0penDocument(2 of 18)[11/26/2001 6:29:42 PM] • Chevron Plus Unleaded Gasoline MSDS#3205 Rev#23(12/08/00) TOLUENE Chemical Name: TOLUENE CAS 108883 50 ppm ACGIH TWA 200 ppm OSHA PEL 300 ppm OSHA CEILING 1,000 LBS CERCLA 302.4 RQ N-BUTANE Chemical Name: N-BUTANE CAS 106978 800 ppm ACGIH TWA N-HEPTANE Chemical Name: N-HEPTANE CAS 142825 400 ppm ACGIH TWA 500 ppm ACGIH STEL 500 ppm OSHA PEL N-HEXANE Chemical Name: N-HEXANE CAS 110543 50 ppm ACGIH TWA 500 ppm OSHA PEL 5,000 LBS CERCLA 302.4 RQ. HEXANE ISOMERS (OTHER THAN N) HEXANES 500 ppm ACGIH TWA 1000 ppm ACGIH STEL PENTANE (ALL ISOMERS) PENTANES 600 ppm ACGIH TWA 750 ppm ACGIH STEL 1000 ppm OSHA PEL CYCLOHEXANE Chemical Name: CYCLOHEXANE CAS 110827 300 ppm ACGIH TWA 300 ppm OSHA PEL 1,000 LBS CERCLA 302.4 RQ METHYLCYCLOHEXANE Chemical Name: CYCLOHEXANE, METHYL CAS 108872 400 ppm ACGIH TWA 500 ppm OSHA PEL TRIMETHYLBENZENE http://library.cbest.chevron.com/lubes/chevmsd.../33ef0475182faded8825661f005d73f6?Open Document(3 of 18)[11/26/2001 6:29:42 PM] Che4,ron Plus Unleaded Gasoline MSDS#3205 Rev#23(12/08/00) Chemical Name: BENZENE, TRIMETHYL- CAS25551137 25 ppm ACGIH TWA 2,2,4-TRIMETHYLPENTANE Chemical Name: 2,2,4-TRIMETHYLPENTANE CAS540841 1,000 LBS CERCLA 302.4 RQ CAN CONTAIN METHYL TERT BUTYL ETHER (MTBE) Chemical Name: 2-METHOXY-2-METHYL PROPANE CAS 1634044 < 15.00% 40 ppm ACGIH TWA 50 ppm Chevron STEL 1,000 LBS CERCLA 302.4 RQ ETHYL TERT BUTYL ETHER (ETBE) Chemical Name: 2-ETHOXY-2-METHYL PROPANE CAS637923 < 18.00% NONE NA TERT-AMYL METHYL ETHER (TAME) Chemical Name: 2-METHOXY-2-METHYL-BUTANE CAS994058 < 17.00% 50 ppm Chevron STEL OR ETHANOL Chemical Name: ETHYL ALCOHOL CAS64175 < 10.00% 1000 ppm ACGIH TWA 1000 ppm OSHA PEL COMPOSITION COMMENT: Refer to the OSHA Benzene Standard (29 CFR 1910.1028) and Table Z-2 for detailed training, exposure monitoring, respiratory protection and medical surveillance requirements before using this product. Motor gasoline is considered a mixture by EPA under the Toxic Substances Control Act (TSCA). The refinery streams used to blend motor gasoline are all on the TSCA Chemical Substances Inventory. The appropriate CAS number for refinery blended motor gasoline is 86290-81-5. The product specifications of motor gasoline sold in your area will depend on applicable Federal and State regulations. Ethyl Alcohol is only added in limited specific distribution areas. 3. HAZARDS IDENTIFICATION http://library.cbest.chevron.com/lubes/chevmsd.../33ef0475182faded8825661f005d73f6?OpenDocument(4 of 18)[11/26/2001 6:29:42 PM] Chevron Plus Unleaded Gasoline MSDS#3205 Rev#23(12/08/00) *** * * * * * EMERGENCY OVERVIEW * *x ** * Colorless to yellow liquid with a gasoline hydrocarbon odor. - EXTREMELY FLAMMABLE - HARMFUL OR FATAL IF SWALLOWED - CAN ENTER LUNGS AND CAUSE DAMAGE - VAPOR HARMFUL. - MAY CAUSE EYE AND SKIN IRRITATION - LONG-TERM EXPOSURE TO VAPOR HAS CAUSED CANCER IN LABORATORY ANIMALS - KEEP OUT OF REACH OF CHILDREN IMMEDIATE HEALTH EFFECTS EYE: Contact with the eyes causes irritation. Eye contact with the vapors, fumes, or spray mist from this substance could also cause similar signs and symptoms. SKIN: Contact with the skin causes irritation. Not expected to be harmful to internal organs if absorbed through the skin. Prolonged or frequently repeated contact may cause the skin to become cracked or dry from the defatting action of this material. INGESTION: Because of the low viscosity of this substance, it can directly enter the lungs if it is swallowed (this is called aspiration). This can occur during the act of swallowing or when vomiting the substance. Once in the lungs, the substance is very difficult to remove and can cause severe injury to the lungs and death. INHALATION: May be harmful if inhaled. Breathing the vapors at concentrations above the recommended exposure standard can cause central nervous system effects. The vapor or fumes from this material may cause respiratory irritation. SIGNS AND SYMPTOMS OF EXPOSURE: Eye damage or irritation: may include pain, tearing, reddening, swelling, and impaired vision. Skin injury:.may include pain, discoloration, swelling, and blistering. Respiratory irritation: may include coughing and difficulty breathing. Central nervous system effects may include headache, dizziness, nausea, vomiting, weakness, loss of coordination, blurred vision, drowsiness, confusion, or disorientation. At extreme http://library.cbest.chevron.com/lubes/chevmsd.../33ef0475182faded8825661f005d73f6?OpenDocument(5 of 18) [11/26/2001 6:29:42 PM] Ch6ron Plus Unleaded Gasoline MSDS#3205 Rev#23(12/08/00) exposures, central nervous system effects may include respiratory depression, tremors or convulsions, loss of consciousness, coma or death. CARCINOGENICITY: Risk depends on duration and level of exposure. See Section 11 for additional information. Gasoline has been classified as a Group 2B carcinogen (possibly carcinogenic to humans) by the International Agency for Research on Cancer (IARC). Contains chemical(s) known to the State of California to cause cancer. Contains benzene, which has been classified as a carcinogen by the National Toxicology Program (NTP), and a Group 1 carcinogen (carcinogenic to humans) by the International Agency for Research on Cancer (IARC). Contains ethylbenzene which has been classified as a Group 2B carcinogen (possibly carcinogenic to humans) by the International Agency for Research on Cancer (IARC). Whole gasoline exhaust was reviewed by the International Agency for Research on Cancer (IARC) in their Monograph Volume 46 (1989). Evidence for causing cancer was considered inadequate in animals and inadequate in humans. IARC placed whole gasoline exhaust in Category 213, considering it possibly carcinogenic to humans. 4. FIRST AID MEASURES EYE: Flush eyes with water immediately while holding the eyelids open. Remove contact lenses, if worn, after initial flushing, and continue flushing for at least 15 minutes. Get medical attention if irritation persists. SKIN: Wash skin immediately with soap and water and remove contaminated clothing and shoes. Get medical attention if irritation persists. Discard contaminated clothing and shoes or thoroughly clean before reuse. INGESTION: If swallowed, give water or milk to drink and telephone for medical advice. DO NOT make person vomit unless directed to do so by medical personnel. If medical advice cannot be obtained, then take the person and product container to the nearest medical emergency treatment center or hospital. INHALATION: Move the exposed person to fresh air. If not breathing, give artificial respiration. If breathing is difficult, give oxygen. Get medical attention if breathing difficulties continue. NOTE TO PHYSICIANS: Ingestion of this product or subsequent vomiting can result in aspiration of light hydrocarbon liquid which can cause pneumonitis. http://library.cbest.chevron.com/lubes/chevmsd.../33ef0475182faded8825661f005d73f6?OpenDocument(6 of 18)(11/26/2001 6:29:42 PM] Chelron Plus Unleaded Gasoline MSDS#3205 Rev#23(12/08/00) 5. FIRE FIGHTING MEASURES FIRE CLASSIFICATION: OSHA Classification (29 CFR 19 10.1200): Flammable liquid. See section 7 for appropriate handling and storage conditions. FLAMMABLE PROPERTIES: FLASH POINT: (TCC) < -49F (<-45C) AUTOIGNITION: 536-835F (280-456C) NFPA FLAMMABILITY LIMITS (% by volume in air): Lower: 1.4 Upper: 7.6 EXTINGUISHING MEDIA: Dry Chemical, CO2, AFFF Foam or alcohol resistant foam if>15% volume polar solvents (oxygenates). NFPA RATINGS: Health 1; Flammability 3; Reactivity 0. FIRE FIGHTING INSTRUCTIONS: Use water spray to cool fire-exposed containers and to protect personnel. For fires involving this material, do.not enter any enclosed or confined fire space without proper protective equipment, including self-contained breathing apparatus. COMBUSTION PRODUCTS: Normal combustion forms carbon dioxide and water vapor; incomplete combustion can produce carbon monoxide. 6. ACCIDENTAL RELEASE MEASURES CHEMTREC EMERGENCY NUMBER (24 hr): (800)424-9300 or (703)527-3887 International Collect Calls Accepted ACCIDENTAL RELEASE MEASURES: Eliminate all sources of ignition in the vicinity of the spill or released vapor. Stop the source of the leak or release. Clean up releases as soon as possible, observing precautions in Exposure Controls/Personal Protection. Contain liquid to prevent further contamination of soil,.surface water or groundwater. Clean up small spills using appropriate techniques such as sorbent materials or pumping. Where feasible and appropriate, remove contaminated soil. Follow prescribed procedures for reporting and responding to larger releases. Place contaminated materials in disposable containers and dispose of in a manner.consistent with applicable regulations. Contact local environmental or health authorities for approved disposal of this material. http://Iibrary.cbest.chevron.com/lubes/chevmsd.../33ef0475182faded8825661f005d73f6?OpenDocument(7 of 18)(11/26/2001 6:29:42 PM] ChOron Plus Unleaded Gasoline MSDS#3205 Rev#23(12/08/00) Release of this product should be prevented from contaminating soil and water and from entering drainage and sewer systems. U.S.A. regulations require reporting spills of this material that could reach any surface waters. The toll free number for the U.S. Coast Guard National Response Center is (800) 424-8802. 7. HANDLING AND STORAGE This product presents an extreme fire hazard. Liquid very quickly evaporates, even at low temperatures, and forms vapor (fumes) which can catch fire and burn with explosive violence. Invisible vapor spreads easily and can be set on fire by many sources such as pilot lights, welding equipment, and electrical motors and switches. Electrostatic charge may accumulate and create a hazardous condition when handling this material. To minimize this hazard, bonding and grounding may be necessary but may not, by themselves, be sufficient. Review all operations which have the potential of generating an accumulation of electrostatic charge and/or a flammable atmosphere (including tank and container filling, splash filling, tank cleaning, sampling, gauging, switch loading, filtering, mixing, agitation, and vacuum truck operations) and use appropriate mitigating procedures. For more information, refer to OSHA Standard 29 CFR 1910.106, "Flammable and Combustible Liquids", National Fire Protection Association (NFPA) 77, "Recommended Practice on Static Electricity", and/or the American Petroleum Institute (API) Recommended Practice 2003, "Protection Against Ignitions Arising Out of Static, Lightning, and Stray Currents". Improper filling of portable gasoline containers creates danger of fire. Only dispense gasoline into approved and properly labeled gasoline containers. Always place portable containers on the ground. Be sure pump nozzle is in contact with the container while filling. Do not use a nozzle's lock-open device. Do not fill portable containers that are inside a vehicle or truck/trailer bed. Never siphon gasoline by mouth. Use only as a motor fuel. Do not use for cleaning, pressure appliance fuel, or any other such use. DO NOT USE OR STORE near heat, sparks or open flames. USE AND STORE ONLY IN WELL VENTILATED AREA. Keep.container closed when not in use. READ AND OBSERVE ALL PRECAUTIONS ON PRODUCT LABEL. Container is not designed to contain pressure. Do not use pressure to empty container or it may rupture with explosive force. Empty containers retain product residue (solid, liquid, and/or vapor) and can be dangerous. http://Iibrary.cbest.chevron.com/lubes/chevmsd.../33ef0475182faded8825661f005d73f6?OpenDocument(8 of 18)[11/26/2001 6:29:42 PM] • Chevron Plus Unleaded Gasoline MSDS#3205 Rev#23(12/08/00) Do not pressurize, cut, weld, braze, solder, drill, grind, or expose such containers to heat, flame, sparks, static electricity, or other sources of ignition. They may explode and cause injury or death. Empty containers should be completely drained, properly closed, and promptly returned to a drum reconditioner, or properly disposed of. 8. EXPOSURE CONTROLS/PERSONAL PROTECTION GENERAL CONSIDERATIONS: Consider the potential hazards of this material (see Section 3), applicable exposure limits,job activities, and other substances in the work place when designing engineering controls and selecting personal protective equipment. If engineering controls or work practices are not adequate to prevent exposure to harmful levels of this material, the personal protective equipment listed below is recommended. The user should read and understand all instructions and limitations supplied with the equipment since protection is usually provided for a limited time or under certain circumstances. ENGINEERING CONTROLS Use process enclosures, local exhaust ventilation, or other engineering controls to control airborne levels below the recommended exposure limits. PERSONAL PROTECTIVE EQUIPMENT EYE/FACE PROTECTION: No special eye protection is normally required. Where splashing is possible, wear safety glasses with side shields as a good safety. practice. SKIN PROTECTION: No special protective clothing is normally required. Where splashing is possible, select protective clothing depending on operations conducted, physical requirements and other substances. Suggested materials for protective gloves include: <Nitrile> <Polyurethane> <Viton> <Chlorinated Polyethylene (or Chlorosulfonated Polyethylene or CPE)> RESPIRATORY PROTECTION: Determine if airborne concentrations are below the recommended exposure limits. If not, wear a NIOSH approved respirator that provides adequate protection from measured concentrations of this material. Use the following respirators: Organic Vapor. Use a positive pressure, air-supplying respirator if there is potential for uncontrolled release, exposure levels are not known, or other circumstances where air-purifying respirators may not provide adequate protection. 9. PHYSICAL AND CHEMICAL PROPERTIES http://library.cbest.chevron.com/tubes/chevmsd.../33ef0475182faded8825661f005d73f6?Open Document(9 of 18)(11/26/2001 6:29:42 PM] Chevron Plus Unleaded Gasoline MSDS#3205 Rev#23(12/08/00) PHYSICAL DESCRIPTION: Colorless to yellow liquid with a.gasoline hydrocarbon odor. pH: NA VAPOR PRESSURE: 5 - 15 PSI @ 100F (REID) VAPOR DENSITY (AIR=1): 3-4 (NFPA) BOILING POINT: 25 - 225C FREEZING POINT: NA MELTING POINT: NA SOLUBILITY: Soluble in hydrocarbons; insoluble in water. SPECIFIC GRAVITY: 0.7 0.8 @ 15.6/15.6C 10. STABILITY AND REACTIVITY HAZARDOUS DECOMPOSITION PRODUCTS: None known CHEMICAL STABILITY: Stable. CONDITIONS TO AVOID: See section 7. INCOMPATIBILITY WITH OTHER MATERIALS: May react with strong oxidizing agents, such as chlorates, nitrates, peroxides, etc. HAZARDOUS POLYMERIZATION: Polymerization will.not occur. 11. TOXICOLOGICAL INFORMATION EYE EFFECTS: The mean 24-hour Draize eye irritation score in rabbits is 0. SKIN EFFECTS: This material was not a skin sensitizer in the modified Buehler Guinea Pig Sensitization Test. For a 4-hour exposure, the Primary Irritation Index (PII) in rabbits is: 4.8. ACUTE ORAL EFFECTS: The oral LD50 in rats is > 5 ml/kg. ACUTE INHALATION EFFECTS: No product toxicology data available. ADDITIONAL TOXICOLOGY INFORMATION: http://Iibrary.cbest.chevron.com/lubes/chevmsd.../33ef0475182faded8825661f005d73f6?Open Document(10 of 18)[11/26/2001 6:29:42 PM] Chevron Plus Unleaded Gasoline MSDS#3205 Rev#23(12/08/00) When vapor exposures are low, or short duration and infrequent, such as during refuelling and tanker loading/unloading, neither total hydrocarbon nor components such as benzene are likely to result in any adverse health effects. In situations such as accidents or spills where exposure to gasoline vapor and liquid is potentially high, attention should be paid to potential toxic effects of specific components in addition to those of total hydrocarbons. Information about specific components in gasoline are found in Section 1 and Section 15 of this MSDS. More detailed information on the health hazard of specific gasoline components can be obtain from the Chevron Emergency Information Center (see Section 1 for telephone numbers). A study was done in which ten volunteers were exposed for 30 minutes to about 200, 500 or 1000 ppm concentrations of the vapor of three different unleaded gasolines. Irritation of the eyes was the only significant effect observed, based on both subjective and objective assessments. An inhalation study with rats exposed to 0, 400 and 1600 ppm of wholly vaporized unleaded gasoline, 6 hours per day on day 6 through 16 of gestation, showed no teratogenic effects nor indication of toxicity to either the mother or the fetus (sex ratio, embryotoxicity, fetal growth and development). An inhalation study with pregnant rats exposed to 0, 1000, 3000, and 9000 ppm of unleaded gasoline vapor, 6 hours per day on days 6 through 20 of gestation, showed no teratogenic effects nor indications of toxicity to either the mother or the fetus. In an inhalation study, groups of 6 Fischer rats (3 male, 3 female) were exposed to 2056 ppm of wholly vaporized unleaded gasoline for 6 hours per day, 5 day per week for up to 18 months. Histopathology of the peripheral nervous system and spinal cord revealed no distal axonal neuropathy of the type associated with exposure to n-hexane even though gasoline contained 1.9% n-hexane. The authors concluded that gasoline treatment may have amplified the incidence and prominence of some naturally occurring age related changes in the nervous system. Wholly vaporized unleaded gasoline was used in a 3 month inhalation study. Groups of 40 rats (20 males, 20 female) and 8 squirrel monkeys (4 male, 4 female) were exposed 6 hours per day and 5 days per week for 13 weeks to 384 or 1552 ppm gasoline. One group of each species served as unexposed controls. The initial conclusion of this study was that inhalation of gasoline at airborne concentrations of up to 1522 ppm caused no toxicity in rats or monkeys. However, further histopathological examination of male rat kidneys on the highest dose group revealed an increased incidence and severity of regenerative epithelium and dilated tubules containing http://Iibrary.cbest.chevron.com/lubes/chevmsd.../33ef0475182faded8825661f005d73f6?OpenDocument(11 of 18)(11/26/2001 6:29:42 PM] Chevron Plus Unleaded Gasoline MSDS#3205 Rev#23(12/08/00) proteinaceous deposits. Rabbits were exposed to unleaded gasoline 24 hour per day, 5 days per week for two weeks; 0, 2.5, 5 or 8 ml were applied to the skin under an occlusive dressing. Applied in such a way, this motor gasoline was corrosive to the rabbit skin and animals in all dose groups had decreased bodyweights. The slight and/or isolated systemic effects noted in the study were judged to be not significant. Unleaded gasoline was assayed for mutagenic and cytogenetic activity. Gasoline was not mutagenic, either with or without activation, in Ames assay (Salmonella typhimurium), Saccharamyces cerevisesae, or mouse lymphoma assays. In addition, point mutations were not induced in human lymphocytes exposed to gasoline in vivo. The gasoline was not mutagenic when tested in the mouse dominant lethal assay. Administration of gasoline to rats did not cause chromosomal aberrations in their bone marrow cells. In a lifetime skin painting study, 50 male Swiss mice were treated with 0.05 ml of unleaded gasoline three times per week. Positive control groups were treated with benzo(a)pyrene in acetone; an untreated negative control group was also included. The repeated exposure to gasoline caused severe skin irritation, ulceration, hyperkeratosis and abscesses. There was no statistically significant increase in the incidence of skin tumors. Histopathology at the end of the study showed that unleaded gasoline did not increase the incidence of tumors in other organs. Lifetime inhalation of wholly vaporized unleaded gasoline at 2056 ppm has caused increased liver tumors in female mice. The mechanism of this response is still being investigated but is thought to be an epigenetic process unique to the female mouse. This exposure also caused kidney damage and eventually kidney cancer in male rats. No other animal model studied has shown these adverse kidney effects and there is no physiological reason to believe that they would occur in man. EPA has concluded that the mechanism by which wholly vaporzied unleaded gasoline causes kidney damage is unique to the male rat. The response in that species (kidney damage and cancer) should not be used in human risk assessment. In their 1988 review of carcinogenic risk from gasoline, The Internatioal Agency for Research on Cancer (IARC) noted that, because published epidemiology studies did not include any exposure data, only occupations where gasoline exposure may have occurred were reviewed. These included gasoline service station attendants and automobile mechanics. IARC also noted that there was no opportunity to separate effects of combustion products from those of gasoline itself. Although IARC allocated gasoline http://library.cbest.chevron.com/lubes/chevmsd.../33ef0475182faded8825661f005d73f6?Open Document(12 of 18)[11/26/2001 6:29:42 PM] Ghelron Plus Unleaded Gasoline MSDS#3205 Rev#23(12/08/00) a final overall classification of Group 213, i.e. possibly carcinogenic to humans, this was based on limited evidence in experimental animals plus supporting evidence including the presence in gasoline of benzene and 1, 3-butadiene. The actual evidence for cacinogenicity in humans was considered inadequate. To explore the health effects of workers potentially exposed to gasoline vapors in the marketing and distribution sectors of the petroleum industry, the American Petroleum Institute sponsored a cohort mortality, a nested case-control, and an exposure assessment study. Histories of exposure to gasoline were reconstructed for a cohort of more than 18,000 employees from four companies for the time period between 1946 and 1985. Data were analyzed based on length of employment, length of exposure,job category, age at first exposure and estimated cumulative and peak exposures. Cumulative exposure was defined as the,sum of products of TWA exposure and duration of exposure of each job in an employee's work history. Amoung cohort members, cumulative exposure ranged from 2 to 8,000 ppm-years. In general, long-term drivers at small terminals had the highest exposures, and short-term workers with "other terminal jobs" had the lowest. A peak exposure was defined as an episode in excess of 500 ppm lasting 15 to 90 minutes. The results of the cohort study indicated that there was no increased mortality from either kidney cancer or leukemia among marketing and marine distribution employees who were exposed to gasoline in the petroleum industry, when compared to the general population. More importantly, based on internal comparisons, there was no association between mortality from kidney cancer or leukemia and various indices of gasoline exposure. For acute myeloid leukemia (AML), a non-significant mortality increase was found in land-based terminal employees, but no trend was detected when the data were analyzed by various gasoline exposure indices. This non-significant excess was limited to land-based terminal employees hired prior to 1948. On the other hand, a deficit of mortality from AML was observed among marine employees. In addition to the cohort study, a subsequent nested case-control study was also conducted. Four diseases were selected for analysis in the case-control study: Leukemia (all cell types), AML, kidney cancer and multiple myeloma. For each case, five individually matched controls were randomly selected from the cohort. In the original cohort study, broad generic job categories were used as part of exposure assessment. In the case-control study, a finer and more homogeneous job classification was developed. In addition to job category, several quantitative gasoline exposure indices were used in the case-control analysis: length of exposure, cumulative exposure (ppm-years in terms of total hydrocarbons) http://library.cbest.chevron.com/tubes/chevmsd.../33ef0475182faded8825661f005d73f6?OpenDocument(13 of 18)(11/26/2001 6:29:42 PM] T Chevron Plus Unleaded Gasoline MSDS#3205 Rev#23(12/08/00) and frequency of peak exposure. Time period of first exposure to gasoline (1948 or before and 1949 or after) was also included as an exposure index. Results of the nested case-control study confirmed the findings of the original cohort study. That is, exposure to gasoline at the levels experienced by this cohort of distribution workers is not a significant risk factor for leukemia (all cell types), acute myeloid leukemia, kidney cancer or multiple myeloma. 12. ECOLOGICAL INFORMATION ECOTOXICITY: Gasoline studies have been conducted in the laboratory under a variety of test conditions with a range of fish and invertebrate species. An even more extensive database is available on the aquatic toxicity of individual aromatic constituents. The majority of published studies do not identify the type of gasoline evaluated, or even provide distinguishing characteristics such as aromatic content or presence of lead alkyls. As a result, comparison of results among studies using open and closed vessels, different ages and species of test animals and different gasoline types, is difficult. The bulk of the available literature on gasoline relates to the environmental impact of monoaromatic (BTEX) and diaromatic (naphthalene, methylnaphthalenes) constituents. In general, non-oxygenated gasoline exhibits some short-term toxicity to freshwater and marine organisms, especially under closed vessel or flow-through exposure conditions in the laboratory. The components which are the most prominent in the water soluble fraction and cause aquatic toxicity, are also highly volatile and can be readily biodegraded by microorganisms. The 96-hour LC50 in rainbow trout (Oncorhynchus mykiss) is 2.7 mg/1 (BTEX). The 4&hour LC50 in daphnia (Daphnia magna) is 3.0 mg/1 (BTEX). The 96-hour LC50 in sheepshead minnow (Cyprinodon variegatus) is 8.3 mg/1 (BTEX). The 96-hour LC50 in mysid shrimp (Mysidopsis bahia) is 1.8 mg/l (BTEX). ENVIRONMENTAL FATE: Following spillage, the more volatile components of gasoline will be rapidly lost, with concurrent dissolution of these and other constituents into the water. Factors such as local environmental conditions (temperature, wind, mixing or wave action, soil type, etc), photo-oxidation, biodegradation and adsorption onto suspended sediments, can contribute to the weathering of spilled gasoline. The aqueous solubility of non-oxygenated unleaded gasoline, based on analysis of http://Iibrary.cbest.chevron.com/lubes/chevmsd.../33ef0475182faded8825661f005d73f6?Open Document(14 of 18)(11/26/2001 6:29:42 PM] Lhetron Plus Unleaded Gasoline MSDS#3205 Rev#23(12/08/00) benzene, toluene, ethylbenzene+xylenes and naphthalene, is reported to be 112 mg/l. Solubility data on individual gasoline constituents also available. 13. DISPOSAL CONSIDERATIONS Use material for its intended purpose or recycle if possible. This material, if it must be discarded, may meet the criteria of a hazardous waste as defined by USEPA under RCRA (40CFR261) or other State and local regulations. Measurement of certain physical properties and analysis for regulated components may be necessary to make a correct determination. If this material is classified as a hazardous waste, federal law requires disposal at a licensed hazardous waste disposal facility. 14. TRANSPORT INFORMATION The description shown may not apply to all shipping situations. Consult 49CFR, or appropriate Dangerous Goods Regulations, for additional description requirements (e.g., technical name) and mode-specific or quantity-specific shipping requirements. DOT SHIPPING NAME: GASOLINE DOT HAZARD CLASS: 3 (FLAMMABLE LIQUID) DOT IDENTIFICATION NUMBER: UN 1203 DOT PACKING GROUP: II 15. REGULATORY INFORMATION SARA 311 CATEGORIES: 1. Immediate (Acute) Health Effects: YES 2. Delayed (Chronic) Health Effects: YES 3. Fire Hazard: YES 4. Sudden Release of Pressure Hazard: NO 5. Reactivity Hazard: NO REGULATORY LISTS SEARCHED: 01=SARA 313 11=NJ RTK 22=TSCA Sect 5(a)(2) 02=MASS RTK 12=CERCLA 302.4 23=TSCA Sect 6 http://library.cbest.chevron.com/lubes/chevmsd.../33ef0475182faded8825661f005d73f6?OpenDocument(15 of 18)(11/26/2001 6:29:42 PM] • rhe*ron Plus Unleaded Gasoline MSDS#3205 Rev#23(12/08/00) 03=NTP Carcinogen 13=MN RTK 24=TSCA Sect 12(b) 04=CA Prop 65-Carcin 14=ACGIH TWA 25=TSCA Sect 8(a) 05=CA Prop 65-Repro Tox 15=ACGIH STEL 26=TSCA Sect 8(d) 06=IARC Group 1 16=ACGIH Calc TLV 27=TSCA Sect 4(a) 07=IARC Group 2A 17=OSHA PEL 28=Canadian WHMIS 08=IARC Group 2B 18=DOT Marine Pollutant 29=OSHA CEILING 09=SARA 302/304 19=Chevron TWA 30=Chevron STEL 10=PA RTK 20=EPA Carcinogen The following components of this material are found on the regulatory lists indicated. BENZENE, ETHYL- is found on lists: 01,02,08,10,11,12,13,14,15,17,26,28, N-BUTANE is found on lists: 02,10,11,13,14,28, CYCLOHEXANE, METHYL is found on lists: 02,10,11,13,14,17,26,28, TOLUENE is found on lists: 01,02,05,10,11,12,13,14,17,26,28,29, N-HEXANE is found on lists: 01,02,10,11,12,13,t4,17,27,28, CYCLOHEXANE is found on lists: 01,02,10,11,12,13,14,17,26,28, BENZENE, DIMETHYL- is found on lists: 01,02,10,1 1,12,13,14,15,17, N-HEPTANE is found on lists: 02,10,11,13,14,15,17,26,28, 2-METHOXY-2-METHYL PROPANE is found on lists: 01,02,10,11,12,14,24,26,27,30, BENZENE, TRIMETHYL- is found on lists: 02,10,11,13,14,26,28, 2,2,4-TRIMETHYLPENTANE is found on lists: 02,10,11,12,26, 2-ETHOXY-2-METHYL PROPANE is found on lists: 25,26, ETHYL ALCOHOL is found on lists: 02,05,10,11,13,14,17,28, BENZENE is found on lists: 01,02,03,04,05,06,10,11,12,13,14,15,17,20,28,29, 2-METHOXY-2-METHYL-BUTANE is found on lists: 24,25,26,27,30, GASOLINE (GENERIC) is found on lists: 04,08,K15,17, PENTANES is found on lists: 14,t5,17, http://library.cbest.chevron.com/tubes/chevmsd.../33ef0475182faded8825661f005d73f6?Open Document(16 of 18)[11/26/2001 6:29:42 PM] •V Cheiqron Plus Unleaded Gasoline MSDS#3205 Rev#23(12/08/00) HEXANES is found on lists: 14,15, WHMIS CLASSIFICATION: Class B, Division 2: Flammable Liquids Class D, Division 2, Subdivision A: Very Toxic Material -Carcinogenicity Class D, Division 2, Subdivision B: Toxic Material -Skin or Eye Irritation 16. OTHER INFORMATION NFPA RATINGS: Health l; Flammability 3; Reactivity 0; HMIS RATINGS: Health l; Flammability 3; Reactivity 0; (0-Least, 1-Slight, 2-Moderate, 3-High, 4-Extreme, PPE:- Personal Protection Equipment Index recommendation, *- Chronic Effect Indicator). These values are obtained using the guidelines or published evaluations prepared by the National Fire Protection Association (NFPA) or the National Paint and Coating Association (for HMIS ratings). REVISION STATEMENT: This revision updates Sections 1 (Company Identification & Product Numbers). ABBREVIATIONS THAT MAY HAVE BEEN USED IN THIS DOCUMENT: TLV - Threshold Limit Value TWA - Time Weighted Average STEL - Short-term Exposure Limit TPQ - Threshold Planning Quantity RQ - Reportable Quantity PEL - Permissible Exposure Limit C - Ceiling Limit CAS - Chemical Abstract Service Number A 1-5 - Appendix A Categories () - Change Has Been Proposed NDA - No Data Available NA - Not Applicable Prepared according to the OSHA Hazard Communication Standard (29 CFR 1910.1200) and the ANSI MSDS Standard (Z400.1) by the Toxicology and Health Risk Assessment Unit, CRTC, P.O. Box 1627, Richmond, CA 94804 ********************************************************************** The above information is based on the data of which we are aware and is believed to be correct as of the date hereof. Since this information may be applied under conditions beyond our control and with which we may be unfamiliar and since data made available subsequent to the date hereof may http://Iibrary.cbest.chevron.com/lubes/chevmsd.../33ef0475182faded8825661f005d73f6?OpenDocument(17 of 18)[11/26/2001 6:29:42 PM] t£hOvron Plus Unleaded Gasoline MSDS#3205 Rev#23(12/08/00) , suggest modification of the information, we do not assume any responsibil- ity for the results of its use. This information is furnished upon condition that the person receiving it shall make his own determination of the suitability of the material for his particular purpose. THIS IS THE LAST PAGE OF THIS MSDS http://Iibrary.cbest.chevron.com/lubes/chevmsd.../33ef0475182faded8825661f005d73f6?Open Document(18 of 18)[11/26/2001 6:29:42 PM] J B E 'R S F I D F/ICE aRrM T RONALD J. FRAZE. May 1, 2006 FIRE CHIEF Mr. Andrew Modugno, P.G. Gary Hutton, SECOR International, Inc. Senior Deputy Chief 290 Conejo Ridge Avenue Administration i 'Thousand Oaks, CA 91361 326-3650 Deputy Chief Dean Clason Operations/Training 326-3652 RE: ARCO No. 3090, 3333 Union Avenue in Bakersfield, CA Dispenser Secondary Containment Upgrade Report Deputy Chief Kirk Blair Fire Safety/Prevention Services I 326-3653 Dear Mr. Modugno, 2101"x"Street I have reviewed the above referenced report, dated January 24, 2006. Bakersfield,CA 93301 Please amend page 2 of the report,under the Soil Sampling section, OFFICE: (661)326-3941 FAX: (661)852-2172-217 0 to show that SECOR collected soil samples under the direction of the BFD Hazardous Materials Specialist Howard Wines in this instance. i RALPH E.HUEY,DIRECTOR Upon receipt of the amended report, I will continue with my intent to PREVENTION SERVICES issue a no further action required letter in this case. FIRE SAFETY SERVICES•ENVIRONMENTAL SERVICES 900 Truxtun Avenue,S uite 210 Bakersfield, CA 93301 If you have any questions,please call me at,(661) 326-3649. OFFICE: (661)326-3979 FAX: (661)852-2171 j Sincerely, David Weirather RALPH E. HUEY, Director of Prevention Services Fire Plans Examiner 326-3706 Howard H.Wines, III Hazardous Materials Specialist 326-3649 Howard H. Wines, III Hazardous Materials Specialist Professional Geologist No. 7239 Prevention Services Division ��44, �, _" ' SECOR www.secor.com INTERNATIONAL E CO R INCORPORATED ' 290 Conejo Ridge Avenue Thousand Oaks,CA 91361 805-230-1266 TEL 805-230-1277 FAX ' January 24, 2006 ' Mr. Steve Underwood, Fire Prevention Officer Bakersfield Fire Department t 900 Truxton Avenue, Suite 210 Bakersfield, California 93301 ' RE: DISPENSER SECONDARY CONTAINMENT UPGRADE REPORT Atlantic Richfield Station No. 3090 3333 Union Avenue ' Bakersfield, California, 93301 Dear Mr. Underwood: ' SECOR International Incorporated (SECOR), on behalf of the Atlantic Richfield Company(Atlantic Richfield), is pleased to present the following report documenting the replacement of penetration fittings with new pan entry fittings at Atlantic Richfield Station No. 3090 (Site), located at 3333 Union Avenue in Bakersfield, ' California(Figures 1 and 2). The services provided by SECOR included the following: • Collecting soil samples following removal of the dispensers and pea gravel as directed by the Bakersfield Fire Department (BFD); and t • Preparation of this technical report. ' SITE INFORMATION ' The Site is located at 3333 Union Avenue in Bakersfield, California; at an elevation of approximately 440 feet above mean sea level. The Site is located on the southwest corner of Union Avenue and 34th Street. Local topography slopes to the south-southwest at approximately 0.02 feet per foot (USGS, 1954). Currently an operating Atlantic Richfield retail gas station and am/pm minimart, there are four 12,000- ' gallon double walled, fiberglass gasoline underground storage tanks (USTs), and six gasoline dispensers. ' SITE BACKGROUND ' The Site is located approximately 275 feet east of the East Side Canal, 400 feet east of the Kern Island Canal, and 1.4 miles south of the Kern River, and is underlain by alluvial fan deposits comprised of silt, sand, and clay. Depth to groundwater in the region is noted to be widely variable and seasonable. Approximately 60 percent of the municipal water supply in Kern County is derived from groundwater ' supplies. A regional confining layer known as the Corcoran Clay or E-clay is located at approximately 200 to 300 feet bgs and has an average thickness of approximately 55 feet (Kennedy, 1990). The Corcoran clay separates a semi-confined to unconfined aquifer (above) from a confined aquifer system (below; KCWA, 1990). Groundwater flow beneath the Site is estimated to be south-southwest, or identical to ttopography(KCWA, 1990) 1 Dispenser Secondary Containment Upgrade Report Atlantic Richfield Station No.3090 ' Bakersfield, California Page 2 ' DISPENSER REMOVAL AND REPLACEMENT Belshire Environmental Services (Belshire) was contracted by Atlantic Richfield to make all required ' preliminary notifications, as well as remove penetration fittings below the dispensers and replace them with pan entry fittings. The Construction Permit for the replacement of penetration fittings with pan entry fittings is included in Appendix A. The following section summarizes the'replacement activities: ' On December 27, 2005, Belshire completed the removal of all penetration fittings below.the dispensers and replaced them with PiciesTM pan entry fittings, as well as replacing both sump 89 and the turbine sumps with fiberglass sumps. The dispenser locations are shown in Figure 2. Pea gravel was removed ' and re-used and placed into the trenches upon completion of the replacement activities. SOIL SAMPLING ' SECOR collected soil samples under the direction of the BFD Fire Prevention Officer Mr. Steve Underwood. _ P Field activities were conducted in accordance with the procedures for soil sampling included in'Appendix B. t The dispenser sample locations are indicated.on Figure.3. This section 'summarizes the results of the soil sampling activities. ' Lead Agencies: Bakersfield Fire Department Permit No. MOD-0390 Agency Contact Name: Steve Underwood, Fire Prevention Officer (661) 326-3190 ' Number of Dispenser Samples: 8 Dispenser Sample Names: D-1-2, D-1-6, D-2-2, D-2-6, D-3-2, D-3-6, D-4-2, ' D-4-6, D-5-2, D-5-6, D-6-2, and D-6-6. ANALYTICAL RESULTS '. All soil samples were relinquished to Del Mar Analytical of Irvine, California (Del Mar) for chemical analysis. Del Mar is an Atlantic Richfield-contracted and California Department of Health Services certified laboratory. ' SECOR and Del, Mar adhered to strict chain-of-custody procedures from sample collection to sample analysis. All soil samples were analyzed in accordance with the appropriate Environmental Protection Agency(EPA) method and for the following analytes: • Gasoline Range Organics (GRO C4—C;2) by EPA Test Method 82606; and • Benzene, toluene, ethylbenzene, and xylenes (BTEX), disopropyl ether (DIPE), ethyl tertiary-butyl ' ether (ETBE),' tertiary-amyl methyl ether (TAME), methyl tertiary-butyl ether (MTBE), tertiary-butanol (TBA), and ethanol by EPA Test Method 8260B. A total of eight soil samples were collected from beneath the dispensers. Detectable concentrations of ' petroleum hydrocarbon constituents above the laboratory reporting limit (RL) were identified in one of the eight samples. Concentrations qualified by a "J-flag" are estimated values detected at a level below the RL and above the method detection limit (MDL). EPA-certified labs therefore-advise that users of these ' data should be aware that these data are of unknown quality. Benzene, MTBE, TBA, and ethanol were Dispenser Secondary Containment Upgrade Report , Atlantic Richfield Station No.3090 ' Bakersfield, California Page 3 not detected above the laboratory RL in any of the soil samples collected. GRO was detected in one ' sample at a concentration of 1,100 mg/kg (D-2-2), and total-xylenes were detected at a concentration of 61 mg/kg (D-2-2). The soil sample analytical'results are summarized in Table 1. A copy of the certified laboratory analytical reports and chain-of-custody documeritation are included in Appendix C. Based.on ' the discovered .impact to subsurface soils, an Unauthorized Release Report was submitted by Atlantic Richfield and is provided in Appendix D. ' SUMMARY • On December 27, 2005, Belshire completed the removal of,all penetration fittings below the ' dispensers. A total 'of eight soil samples were collected from beneath the dispensers for confirmation purposes. Benzene; MTBE, TBA, and ethanol were not detected above the laboratory RL in any of the soil samples collected. GRO was detected in 'one sample at a concentration of 1,100 mg/kg (D-2-2), and total xylenes were detected.at a concentration of 61 mg/kg (D-2-2). • Following completion of the soil sampling and excavation activities, new PiciesTM pan entry fittings were installed below the dispensers. 'Belshire also replaced both sump 89.and the turbine sumps ' with fiberglass sumps: • Based on the discovered ..impact to subsurface soils, an Unauthorized Release Report was ' submitted by Atlantic Richfield. STANDARD LIMITATIONS 1 All work was performed under the supervision of a registered geologist as defined in the Registered Geologist Act-of the California Code'of Regulations. The information contained in this report represents ' SECOR's professional.opinions, and is based in part on information supplied by the client. These.opinions are based on currently available information and are arrived at in accordance with currently accepted hydrogeologic and engineering practices at this time and location. Other than this, no warranty is implied or intended. If you have any questions regarding this letter or the above referenced report, please do not hesitate to ' contact the undersigned at(805)230-1266. ; Respectfully submitted, SECOR International Incorporated 708 �•, Andrew Modugno, R.G.#7036 - - ' Senior Geologist Project Manager CAt�� Dispenser.Secondary Containment Upgrade Report Atlantic Richfield Station No.3090 Bakersfield,California Page 4 ' Appendices: Table 1 —.Summary of Soil Analytical Data Figure 1 —Site Location Map ' Figure 2_Site Map,Showing Hydrocarbon Concentrations'in Dispenser Soil Samples Appendix A—Construction Permit Appendix B=Soil Sampling Procedures Appendix C—Laboratory Analytical Reports and Chain-of-Custody.Documentation Appendix D—Underground Storage Tank Unauthorized Release Report cc: Ray Vose—Atlantic Richfield Company 1 1 1 1 ' Dispenser Secondary Containment Upgrade Report Atlantic Richfield Station No. 6218 ' Bakersfield,California Page 5 ' REFERENCES United States Geological Survey (USGS), 1954, Gosford Quadrangle, 7.5 minute topographic, ' photorevised 1973. United States Geological Survey (USGS), 1954, Lamont Quadrangle, 7.5 minute topographic, ' photorevised 1992. United States Geological Survey (USGS), 1954, Oil Center Quadrangle, 7.5 minute topographic, photorevised.1992. United States Geological Survey (USGS), 1954,,_Oildale Quadrangle, 7.5 minute topographic, ' photorevised 1973. Bertoldi, G. L., Johnston, R. H. and Evenson, K.D., 1991, Ground Water in the Central Valley, ' California-A.Summary Report, U. S. Geological Survey Special Paper 1401-A, pgs 44. Kennedy, .D. N., 1990, Kern Water Bank-First Stage'Kern Fan Element Feasibility Report, Department of Water Resources, pgs 36. 1 1 . 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 TABLE 1 TABLE 1 HISTORICAL SOIL ANALYTICAL RESULTS ATLANTIC RICHFIELD COMPANY STATION NO. 3090 3333 Union Avenue Bakersfield,California EPA Method: 82606 . Sample Sample GRO B T E X MTBE TBA DIPE ETBE TAME ETHANO --I-D. --I -Date-==mg/ -mg/kg 1 1 1 � Flea.= 1 1 1 1 1 1 1 1 1 1 1 1 1 "v�.��/gII r___�- �4ry `/ 42o r �/ •S� ( :��`N k�s.,. � a�?� • K%�''pi!, Y �.\ r r / � � y �`" t ray��i h ..iY e! �::� �:i 14 P\5 '�tt ry r t{.-Y r�sl\ ¢ ♦'<F, *w4^ .� ,. y¢- �. .Y '<• �o 4 ��tma, ., :j.' `�$ � p,�� �t�,., � /�'•'•f•.:e :�2 ,Ss �,�•x nw <i,�v, a'<'`F;,yk n'�i$.,�2`�,♦ ���� \ Y ../ '-;-�..J-•� �.�ba�h, 0� �< ,.,i yf�c x,4 y�` .; a e*r,'„v, .,a�.� ♦.C�'r`���ta�.Li- %p"$' <•rb< �- /.; ¢✓� '� 1<�Ft�bV :� �;, a 4 > i n tax h•,G T .� , ' �� t t 4�.,, .' '\`t 1''``•.`� 1/i L_ ��y}..�. S"`.vnr- `� „r. iY♦y s" c` - o',�� �♦ i �}��, r/- 1 �#� i.'• \\ ,�.V rl`r���..'r( .� [dt�}}3'JF t�✓' vt 'S ? Z•'1it bi + �`.�. sY"' ..- -,�l y,`l� �h4 a /N r .y .'�J `SO •��p.'A/ FOUR"Y*IR ` Si 'i1-0n/�� 111 h ;- 6 , �Y ati.yV :*_ 'h 7' •- Kc t �S. ,ono 4"/..�•`=�. ��"":•' •�� _ �UW t.t` •fll rC/�� r �' ��}♦i {"S`' ,� ��' `;�" �,%�/y ,�".� �S kY�r ��y yr•,�& ��< CALI,OWAM�:�` d" tl. �t 1 /„'.''Q�i a,... •.<�-SZ'�S, ,f�Y, � �i t , WEIRe •• n ��� tt� 1 X011 1�1�� i z ,,, i � .�y ♦ .ti x•,{.�s.. t ;uou nOU.rr t C� 1 �{ } ♦ �' .,• .•• a/4 _oa ♦ •i L1_= Bell Park �_ /i t•a •\\`: o r• ti� %. '.'C '°�< 'f't ; y< 1. { G• ♦d >•=. AI�7N-i• •u =_ . '`t .�\« .� <<\.4": 7e�nifv); `I` • ' .' ~V ,W ti t`_�; �,- :,•`\ t \ a;.. R.'+�<.t,?it ,� i c :,�•`>>.• tt�y; �. �,� �,;� ? <;<.� tu'.. � �• � fl (1' a � �` >3 r ��j✓^4`` ��(''Qv< .ir� � - "af ti hti! 7 Q. ''tk: i•' .�x;..�� 1 � J: naaaJ .t\`, I r, � e 1+\ <,Y",• �y ♦,i, .'4�O l �i h�y�,�X„< t.�ja�� le"fix "�{`ri a' \�Fi FEE� _ O �e •�� Ott:, 3t' i f �� ,�� ��' ,, +-•'SXr' ^}; "a6\ y W II -,.1�\\♦ •.County Musan+ I�� y it\�wr i�¢a nko o•; tl ! av, al�z!J ��p� � \t. � {j 8Tsl A�T4 Oi N Wa eo Hosprta % �S D T H v•<`'°p�'}ni .s»�i`. ...,a� .1 ♦rte on<±t/t b;,}3 v>im- Ji?' �nr 4b<ct, a •�y�}'si r J. ST t� •1 e� S..rh`u �5 < a••i+:ao ..� < -�^K n Cam, a.E ��... 1' ��5• ` -t v �LIAI)�81 00 °``nit }•Ia>.� ♦\fit A+M� ,yam�a,� - � �� s a _A r" ' � • � ,� t -1 i �, S"ri :Q. eC�.r�+.. �r :`a>,4, y\`Styy�^�,♦�yf.,,.Y�' r L +' �-♦ ?;•.� ' °( �. ' \ r i 7 ° 4Gf p t' fit+• -) f ♦\ OD�Cei,�T ::. .Y V: ` ';.-{yr'e?.''.Hli it 30 H Cirele ST:,� -.6, ��~.'1�.0 l } `�4� ':`�'' y �`�}{ h6� A�� �' �` �ji'F y� n�`. a3•'��" +,'♦ �� ) ' I f '-. /�O J •Wipe'i 1 ♦C( •C. � akz�'`� sp vZ . 'k •r r it ' � � f ,15L�'�•:g.:� ni ?�;yY��4*}� :i+ .>�;" t� � '�'� �� ,>�r2 f r :r Hos ' 7\� tl � 4t � � Ntt__• I� .:.r< � _'' .. ... '�.�',� �?' r�r�:��� h5�<� ck 1�` _ .� -tV N 747 4.. ,I-; � 4 'i \� � 1 d+`,lV-u,':.• <sA'S�; C'`� ,s � yt \+y � Y T 4 .. ^r ,,>t-*- \ t �� ♦.� '�4S ` �}?�` iS; �i'2\F� A♦y. Lj `"` --{` ° �� 2 'y ', ,• i,Fr�h♦_U%�':y`�� 1 �»,� `S>}� -„`?or ��<' 4.� r,tip, '�•�t�,'.♦`•�`C�y,+r. ' ' � ,_Y. r[{o ` •�"��-'.^4745°.. "� `C�£ - is tit >zi4, '�>S.` ,. \ p'h'i.••. 'Ki��'"i ,n• � s �,�;�'. ��t !I 4e� •'/ •i ��9 ���'��, �'►° .�"'� ,,��,y s•=Yom^.`.^"' �.;`. L-J)S1' "•HOSD al• I'�a��, 4� rjr,_I`� S ,Y" <r ♦�$Cd� a:YrS!s` '{,y .. '�' '� IME © iSS o wr,{, sY♦. . its "s'�.x' �< st'`�LaY ...•. _ i j C �.<f y .,r w ♦.c<{ C" twi ,_.*.., {"". t..' ' SOURCE: USGS 7.5 MINUTE TOPOGRAPHIC MAPS, OILDALE QUADRANGLE, 1954 CELANO PHOTOREVISED 1973 wASCO OIL CENTER QUADRANGLE, 1992 GOSFORD QUADRANGLE, 1954 99 PHOTOREVISED 1973 ' es LAMONT QUADRANGLE, 1992 BUTrONwII.LOw BAKERSFBA N 119 ' 33 168 ARVIN / / 0 2000 4000 ' APPROXIMATE SCALE(FEET) I/ FOR: FIGURE: ATLANTIC RICHFIELD COMPANY STATION NO.3090 SITE LOCATION MAP ' 3333 UNION AVENUE S E C O R Bakersfield,California 290 Conejo Ridge Avenue,Suite 200 Thousand Oaks,CA 91361 JOB NUMBER: DRAWN BY: CHECKED BY: APPROVED BY: DATE: ' (805)230-1266/230-1277(Fax) 370T.03090.01/0622 I RUE A.Modugno A.Modugno 12/22/05 FILEPATH:O:\CADD•37\Client\ARCO\Project\3090_Bakersfield\SLM\3090-SLM.dwg I rerdman I Jan 18,2006 at 11:051 Layout:SUM ' 34t-h--ST-RE-ET ' Sidetralk I APP+'oa-a Planter ' SAMPLE IN DS-3 UMFU DAIS 12 27 05 I Planter DEPTH I GRO BENZ MTBE TBA 2 <0.088 <0.0018<0.0044 <0.044 6 <0.086 <0.0017<0.0043 <0.043 I Iel�anda Q ' KE ID:DS-4 SAMPLE DATE: 12 27 05 � I � I f DEPTH I GRID BENZ MTBE TBA w S-1 S- t I a 2 <0.091 <0.0018<0.0046 <0.046 I d I I I ' 6 <0.11 <0.0023<0.0057 <0.057 ' O SAMPLE Ilk Ds-1 SAMPLE a►T- 12 27 05 § :0. _ I z DEPTH I GRO BENZ I MTBE I TBA , ` ; 2 <0.091 1<0.0018 1<0.0045 <0.045 ' 6 1<0.086 1<0.00171<0.00431<0.043 SAMPLE III.DS-2 SAMPLE DATE 12 27.05 DEPTH I GRO I BENZ I MTBE I TBA `�'•�, I I I ' 2 1,100: <1.7 1 <4.3 1 <86 6 0.30 1<0.00171 0.15 10.019 J I ( I ARCO N BUIIAING N0. 3090 I a I Piping Legend I I I I ---- PRODUCT PIPING I I ' — - VAPOR RECOVERY PIPING I - — — — VENT PIPING I I DS-1 DISPENSER SOIL SAMPLE LOCATIONS I ' 0 50 100 ' APPROXIMATE SCALE(FEET) . FOR: FIGURE: ATLANTIC RICHFIELD COMPANY SITE MAP SHOWING ' 'STATION NO.3090 HYDROCARBON CONCENTRATIONS IN 3333 Union Avenue I DISPENSER SOIL SAMPLES S E C O R Bakersfield,California 290 Conejo Ridge Avenue,Suite 200 Thousand Oaks,CA 91361 JOB NUMBER: DRAWN BY: CHECKED BY: APPROVED BY: DATE: (805)230.1266/230.1277(Fax) 37BP.03090.01/0622 RILE A.Modugno A.Modugno 01118106 FILEPATH:Q:\CADD-37\Client\ARCO\Project\3090-Bakersfield\SLM\3090-SLM.dwgIrerdmanI Jan 18,2006 at 13:301 Layout:DISP HC 1 1 1 1 1 - APPENDIX A ' Construction Permit 1 1 1 1 1 1 , 1 1 _/BELSH E ENVIRONMENTAL SERVICES,INC.. ' 25971 Towne Centre Drive Lake Forest, CA 92610 (949)460-5200 ' Fax(949)460-5210 December 26, 2005 MUNTHER HAWATMEH ' ARCO FACILITY NO.,30 30 p0 3333 UNION AVE , 99'. BAKERSFIELD, CA.93305 ' RE: Secondary Containment Repairs ' Dear Sir/Madam: Your facility has been scheduled for repairs to the underground storage tank (UST).system due to failures identified during recent secondary.containment testing (SB 989 testing): This work is being performed at the request of the BP/ARCO Facilities and Engineering Department and as required by the California State Water Resources Control Board. Work has been scheduled for the following dates and times: ' Start Date: 12/26/2005 Start Time: 7:00:00 AM Estimated Completion Date: 12/29/05 ' Estimated Completion Time: 4:00 pm Facility Requirements: • Do not schedule a fuel delivery during repair activities ' It will be necessary to discontinue fuel sales d urin g repair activities-.. We will do everything within our power to expedite work and re-open your facility. ' If you have an uestions regarding testing activities lease contact Ted Y any g 9 9 , p . Stephenson at (949) 337-9090. ' Sincerely, Ji B own ' Proj t Manager ' Cc Ron Rogers, BP Janet.Wager, BP Wade Melton, Secor 1 1 _ MLSHIRE =I EERVICES INC NVIRON�tENTiiC Scope of Work ' S Facility: BP 03090 Date: 7/19/2005 Job Number: 2612 i 3333 UNION AVE 1 ' BAKERSFIELD, CA Estimate No: 239 Contact: Rick Kinnaman I t Repatr:Locat�on Drspenser 7/8 j Work to be perFormed �ireak grQUnd end expose piping;Remove.and replace dispenser to zbange total j conta�rnent.pan,entry..booi :fo„proies:pan:entry.;paots . E Repair°:Le�catlon;;; fl::Surn:p Work to besper#omied .Fakeegfas sumt5:ta;co(.ac .. ... Repair Location. Tucbrne Sumps Various : . Work:to be pertormed Frberg)ass sump ta.cotlar in a(I.furbine sumps , Possible have ta.instal blue.line-repair tpetietratrors as needed , i 1 i r I 1 1 i i i 1 1 Ri.ghtFax 9/20/2005 10:24 PACE 002/005 Fax Server i ' UNDERC(t Bakersfield Fire Dept. ROUND STORAGE TA Environmental Service # P RMIT APPLICAT'I UNO 900'IYuxtun Ave.,.Stc. 210 CONSTRUCTI MO©(FY OR It>rI Bakersfield, CA 93301 Tel: (661)326-3979 MODIFICATION OF AN Fax: (661)852-2171 PERMIT NO.. QD. o d � �' � •Y Qy Q ��,� ,p Pape 1 of f t TYPE OF APPLICATION: (Check one item only) o NEW FACILITY o NEW TANK INSTALLATION AT EXISTING FACILITY j O MODIFICATION OF FACILITY 0 MINOR MODIFICATION OF FACIUTY' TARTING DATE PROPOSED COMPLETION DATE . ' AC - - FACILITY PERMn'NO. I A SS - ITV P CODE ' rypE of OUSMESsa P"r ! PHONE- ADDRESS Ufry zip CODE i ' ZONTRAWCIVR LICENSE NO. cc NO. WDRYrSS }r,9 RSF INESS Ll�N0, ' 8R1FiLr DESCRIBE THE WORK TO NE DONE ' WATER TO FACILITY PROVIDED BY - r DEPTH TO CtiOUND WATER SOM TYPE EXPECTED AT SITE• . a' NO.OF YANKS TO BE INSTALLED ARE THEY FOR MOTOR FUEL SPILL PREVENTION CONTROL AND COUNTER MEASURES PLAN ON FILE 17 YEs O NO 13 YEs n NO THIS SECTION IS FOR MOTOR'FUEL TANG NO WOLUME UNLEADED REGULAR PRIamum DIESEI. "'now THIS SECTION IS FOR NON MOTOR FUEL STORAGE TANKS TANG NO, VOLUME UNLEADED REGULAR PREMIUM AVIATIM t FOR OFFICIAL USE ONLY ? APPIICATTON D.ATE FACIUIY NO. NO,OF TANKS f ' 77u vplkijL- ided, rs and wW comply with the attached coru/id The penlla and any other state,local and fe&ml s en eyed ajyerjNry. 1K„' and Correct jp APPROVE BY: _ APPLICANT NAME( SIGN471Ui£ ' THIS APPLJCATION 19ECOMES A PERMIT WHEN APPROVED o ' Zs 1 _ 1 APPENDIX B ' Soil Sampling Procedures 1 1 1 1 1 SOIL SAMPLING PROCEDURES b . Soil samples were collected using an EPA.Method,5035 approved,sampling,device (EnCoreTA4). The ENCORE.Samples are immediately capped, locked and then placed back into the Encore Sample Bag. ' Each sample is, en labeled,identified on the chain of custody, and stored in a.chilled cooler for transport to the laboratory. Remaining 'soii in the "sampler is-used for later screening with a photo-ionization detector (PID) or.equivalent..All samples were delivered to State-certified Del Mar Analytical of Irvine, California for potential chemical analysis. . Soil sampling was conducted under the verbal direction of the associated ' Agency Inspector:' SECOR initiated Chain-of-Custody protocol immediately following the collection of all soil samples::All:sampling'equipment'was cleaned in an aqueous solution of Liqui-Nox cleanser or equivalent (no phos"hates); double rinsed with tap water, and final rinsed with de-ionized water dispensed from a ' HudsonT ,type'sprayer to`prevent cross-contamination between sample intervals 1 1 i APPENDIX C ' Laboratory Analytical Reports Anal ical Re P And Chain-of-Custody Documentation 1 1 1 ' 17461 Derian Ave.,Suite 100,Irvine,CA 92614 (949)261-1022 FAX(949)260-3297 1014 E.Cooley Dr.,Suite A,Colton,CA 92324 (909)370-4667 FAX(909)370-1046 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123(858)505-8596 FAX(858)505-9689 DA Del Mar A n a I yti ca I 9830 South 51st SL,Suite B-120,Phoenix,AZ 85044 (480)785-0043 FAX(480)785-0851 ' 2520 E.Sunset Rd.#3,Las Vegas,NV 89120(702)798.3620 FAX(702)798.3621 ' LABORATORY REPORT Prepared For: SECOR International,Inc.-Thousand Oaks Project:ARCO 3090 Bakersfield 290 Conejo Ridge Avenue,Suite 200 ' Thousand Oaks;CA 91361 Attention:Andrew Modugno Sampled: 12/27/05 Received: 12/28/05 ' Issued: 01/12/0619:28 ' NELAP#01108CA California ELAP#1197 CSDLAC#10117 The results listed within this'Laboratory Report pertain only to the samples tested in the laboratory. The analyses contained in this report were performed in accordance with the BPGCLN Technical Specifications,applicable federal,state,local regulations and certification requirements as well as the methodologies as described in laboratory SOPS reviewed by the BPGCLN. This Laboratory Report is ' confidential and is intended for the sole use of Del Mar Analytical and its client. This report shall not be reproduced,except in full, without wrilten permission from Del Mar Analytical. The Chain of Custody, 1 page,is included and is an integral part of this report. This entire report was reviewed and approved for release. CASE NARRATIVE SAMPLE RECEIPT: Samples were received intact,at 5°C,on ice'and with chain of custody documentation. ' HOLDING TIMES: All samples were analyzed within prescribed holding times and/or in accordance with the Del Mar Analytical Sample Acceptance Policy unless otherwise noted in the report. ' PRESERVATION: Samples requiring preservation were verified prior to sample analysis. QA/QC CRITERIA: All analyses met method criteria,except as noted in the report with data qualifiers. COMMENTS: Results that fall between the MDL and RL are T flagged. ' SUBCONTRACTED: No analyses were subcontracted to an outside laboratory. LABORATORY ID CLIENT ID MATRIX ' IOL2375-01 DS-1-2 Soil IOL2375-02 DS-1-6 Soil IOL2375-03 DS-2-2 Soil ' IOL2375-04 DS-2-6 Soil IOL2375-05 DS-3-2 Soil IOL2375-06 DS-3-6 Soil IOL2375-07 DS-4-2 Soil IOL2375-08 DS-4-6 Soil ' Reviewed By: Del Mar Analytical,Irvine ' Lisa Reightley Project Manager IOL2375 <Page I of 22> 17461 Derian Ave.,Suite 100,Irvine,CA 92614 (949)261-1022 FAX(949)260-3297 1014 E.Cooley Dr.,Suite A,Colton,CA 92324(909)370-4667 FAX(909)370-1046 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123 (858)505-8596 FAX(858)505-9689 r - 9830 South 51st St.,Suite B-120,Phoenix,AZ 85044 (480)785-0043 FAX(480)785-0851 D e I M Q r Analytical ' y 2520 E.Sunset Rd.#3,Las Vegas,NV 89120(702)798-3620 FAX(702)798-3621 SECOR International,Inc.-Thousand Oaks Project ID: 'ARCO 3090 Bakersfield ' 290 Conejo Ridge Avenue,Suite 200 Sampled: 12/27/05 Thousand Oaks,CA 91361 Report Number: IOL2375 Received: 12/28/05 Attention: Andrew Modugno ' VOLATILE FUEL HYDROCARBONS BY GC/MS (EPA 5035/GCMS) ' MDL Reporting Sample Dilution Date Date Data ' Analyte Method. Batch Limit Limit Result Factor, Extracted Analyzed Qualifiers Sample ID:IOL2375-01(DS-1-2-'Soil) Reporting Units: mg/kg ' Volatile Fuel Hydrocarbons TPH by GC/MS 5L29007 0.052 0.091 ND 0.909 12/29/05 -12/29/05 (C4-C12) Surrogate:Dibromofluoromethane(80-1255yo) 1,00% Surrogate: Toluene-d8(80-120%) 94% ' Surrogate:4-Bromofluorobenzene(80-1M016) 86% Sample ID:I01,2375-02(DS-1-6-Soil) Reporting Units: mg/kg, ' Volatile Fuel Hydrocarbons TPH by GC/MS 5L29007 0.049 0.086 ND 0.859 12/29/05 12/29/05 (C4-C12) Surrogate:Dibromofluoromethane(80-125%) 102% .Surrogate: Toluene-d8(80-120%),' 95% Surrogate.;4-Bromofluorobenzehe(80-120%) 89% Sample ID:IOL2375-03(DS-2-2-Soil) ' Reporting Units: mg/kg Volatile Fuel Hydrocarbons TPH by GC/MS 5L28029 84 170 1100 1720 12/28/05 12/29/05 (C4-C12) Surrogate:Dibromofluoromethane(55-14016) . 87% AX ' Surrogate: Toluene-d8(60-140 91o) 89% AX Surrogate:4-Bromofluorobenzene(65-140%) 128% AX Sample ID: IOL2375-04(DS-2-6-Soil) ' Reporting Units: mg/kg Volatile Fuel Hydrocarbons TPH by GC/MS 5L28030 0.048 0.084 0.30 0.843 12/28/05 12/28/05 (C4-C12) Surrogate:Dibromofluoroinethane(80-125 91o) 97% ' Surrogate: Toluene-d8(80-120%) 98% Surrogate:4-Bromofluorobenzene(80-120%) 93% Sample ID:IOL2375-05(DS-3-2-Soil) ' Reporting Units: mg/kg Volatile Fuel Hydrocarbons TPH by GUMS 5L29007 0.050 0.088 ND 0.88 12/29/05 12/29/05 (C4-C I2) ' Surrogate:Dibromofluoromethane(80-125 91o) 103% Surrogate: Toluene-d8(80-120%) 95,% Surrogate:4-Bromofluorobe'nzene(80-120%) 88% ' Sample ID:IOL2315-06(DS-3-6-Soil) Reporting Units: mg/kg Volatile Fuel'Hydrocarbons TPH by GC/MS, 5L29007 0.049 0.086 ND 0.858 12/29/05 12/29/05 (C4-C 12) ' Surrogate:Dibromofluoromethane(80-125%) 105% Surrogate: Toluene-d8(80-120010) 94% Del Mar Analytical,Irvine ' Lisa Reightley Project Manager The results pertain only to the samples tested in the laboratory. This report shall not be reproduced, except injull,without written permission from Del Mar Analytical. IOL2375" GPgge 2 of 22> • 17461 Derian Ave.'Suite 100,Irvine,CA 92614 (949)261-1022 FAX(949)260-3297 1014 E.Cooley Dr.,Suite A,Colton,CA 92324 (909)370-4667 FAX(909)370-1046 � ^ n } - 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123(858)505-8596 FAX(858)505-9689 Del M 1 A 1 1 I y l I C�I 9830 South 51st St.,Suite 8-120,Phoenix,AZ 85044 (480)785-0043 FAX(480)785-0851 ' 2520 E.Suns Las et Rd.#3, Vegas,NV 89120(702)798-3620 FAX(702)798.3621 SECOR International,Inc.-Thousand Oaks Project ID: ARCO 3090 Bakersfield 290 Conejo Ridge Avenue,Suite 200 Sampled: 12/27/05 Thousand Oaks,CA 91361 Report Number: IOL2375 Received: 12/28/05 Attention: Andrew Modugno ' VOLATILE FUEL HYDROCARBONS BY GC/MS (EPA,5035/GCMS) MDL Reporting. Sample -Dilution Date Date Data ' Analyte. Method Batch Limit Limit Result Factor Extracted Analyzed Qualifiers Sample IM 10L2375-06(DS-3-6-Soil)-cont. Reporting Units: mg/kg ' Surrogate:4-Bromofluorobenzene(80-120%) 87 Sample ID: IOL2375-07(DS-4-2-Soil) Reporting Units: mg/kg ' Volatile Fuel Hydrocarbons TPH by GC/MS 5L30025 0.052 0.091 ND 0.914 12/30/05 12/30/05 (C4-C 12) Surrogate:Dibromofluoromethane(80-125%) 101% Surrogate: Toluene-d8(80-120%) 106% ' Surrogate:4-Bromofluorobenzene(80-12091.) 98% Sample ID:IOL2375-08(DS-4-6-Soil) Reporting Units: mg/kg ' Volatile Fuel Hydrocarbons TPH by GC/MS 5L29007 0.065 0.11 ND 1.13 12/29/05 12/29/05 (C4-C12) Surrogate:Dibromofluoromethane(80-125916). 101% ' Surrogate: Toluene-d8(80-120 51o) 94% Surrogate:4-Br6mofluorobenzene(80-120%) 89% 1 Del Mar Analytical,Irvine ' Lisa Reightley Project Manager The results pertain only to the samples tested in the laboratory•. This report shall not be reproduced, 1 except in full,without written permission from Del Mar Analytical. IOL2375 <Page 3-of 22> 1 17461 Derian Ave.,Suite 100,Irvine,CA 92614 (949)261.1022 FAX(949)260.3297 _ 1014 E.Cooley Dr.,Suite A,Colton,CA 92324(909)370-4667 FAX(909)370-1046 Del {" A r'�'] '] - 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123 (858)505.8596 FAX(858)505.9689 .h" D 1.I M d 1 /'\1 1 Q I y�I CQ I "' 9830 South 51st SL,Suite B-120,Phoenix,AZ 85044 (480)785.0043 FAX(480)785.0851- ' 2520 E.Sunset Rd.#3,Las Vegas,NV 89120(702)798-3620 FAX(702)798-3621.. SECOR International,inc.-Thousand Oaks Project ID: ARCO 3090 Bakersfield ' 290 Conejo Ridge Avenue,Suite 200 Sampled: 12/27/05 Thousand Oaks,CA 91361 Report Number: IOL2375 Received: 12/28/05 Attention: Andrew Modugno BTEX/OXYGENATES by GUMS(EPA 5035/8260B) MDL Reporting Sample' Dilution Date Date Data ' Analyte 'Method Batch,, Limit Limit Result Factor Extracted Analyzed Qualifiers Sample ID:IOL2375-01(DS-1-2-Soil) Reporting Units: mg/kg ' Benzene EPA 8260B 5L29007 0.00045 0.0018 ND 0.909 12/29/05 12/29/05 Ethylbenzene EPA'8260B 5L29007 0.00046 0.0018 ND 0.909 12/29/05 12/29/05 Toluene EPA 8260B 5L29007 0.00083 0.0018 ND 0.909 12/29/05 12/29/05 o-Xylene EPA 8260B 5L29007 0.00043 0.0018 ND 0.909 12/29/05 12/29/05 ' m,p-Xylenes EPA 8260B 5L29007 0.00068 0.0018 ND 0.909 12/29/05 12/29/05 Xylenes,Total EPA 8260B 5L29067 0.00068 0.0036 ND 0.909 12/29/05 12/29/05 Di-isopropyl Ether(DIPS) EPA 8260B 5L29007 0.00034 0.0045 ND 0.909 12/29/05 12/29/05 ' Ethyl tert-Butyl Ether(ETBE) EPA 8260B 5L29007 0.00053 0.0045 ND 0.909 12/29/05 12/29/05 tert-Amyl Methyl Ether(TAME) EPA 8260B '5L29007 0.00058 0.0045 ND 0.909 12/29/05 12/29/05 Methyl-tert-butyl Ether(MTBE) EPA 8260B 5L29007 0.00091 0.0045 ND 0.909 12/29/05 12/29/05 " tert-Butanol(TBA) EPA 826013 5L29007 0.0045 0.045 ND 0.909 12/29/05 12/29%05 . ' Ethanol EPA 8260B 5L29007 0.11 0.27 ND 0.909 12/29/05 12/29/05 Surrogate:Dibromofluoromethane(80-125a/o) 100% Surrogate: Toluene-d8(80-120%) 94% ' Surrogate:4-Bromofluorobenzene(80-120%) 86% Sample ID:IOL2375-02(DS-1-6-Soil) Reporting Units: ing/kg ' Benzene EPA 8260B 5L29007 0.00043 0.0017 ND 0.859 .12/29/05 12/29/05 Ethylbenzene EPA 8260B 5L29007 0.00044 . 0.0017 ND 0.859 12/29/05 12/29/05 Toluene' EPA 8260B 5L29007 0.00078 0.0017 ND 0.859 12/29/05 12/29/05 o-Xylene EPA 82608 5L29007 0.00040 0.0017 ND 0.859 12/29/05 12/29/05. ' m,p,Xylenes EPA 8260B 5L29007 0.00064 0.0017 0.00070 0.859 12/29/05 12/29/05 J,DX Xylenes,Total EPA-9260B 5L29007 0.00064 0.0034 0.00096 0.859 12/29/05 12/29/05 J,DX Di-isopropyl Ether(DIPE) EPA 82608 5L29007 0.00032 0.0043 ND 0.859 12/29/05 12/29/05 ' Ethyl tert-Butyl Ether(ETBE) EPA 8260B 5L29007 0.00050 . 0.0043 ND 0.859 12/29/05 12/29/05 ten-Amyl Methyl Ether(TAME) EPA 8260B 5L29007 0.00055 0.0043 ND 0.859 12/29/05 12/29/05 Methyl-tert-butyl Ether(MTBE) EPA 8260B 5L29007 0.00086 0.0043 ND 0.859 12/29/05 12/29/05 tert-Butanol(TBA) EPA 8260B 5L29007 0.0043 0.043 ND 0.859 12/29/05 12/29/05 ' Ethanol EPA 8260B 5L29007 0.10 0.26 ND 0.859 12/29/05 12/29/05 Surrogate:DibromgJluoromethane(80-12501o) 102 Surrogate: Toluene-d8(80-120%) 95% ' Surrogate:4-Bromo luorobenzene(80-120 91o) 89% 1 Del Mar Analytical,Irvine ' Lisa Reightley Project Manager The results pertain only to the samples tested in the laboratory. This report shall not be reproduced, except in full,without written permission from Del Mar Analytical. IOL2375 <Page 4 of 22> 1 17461 Derixn Ave.,Suite 100,Irvine,CA 92614 (949)261-1022 FAX(949)260.3297 1014 E.Cooley Dr.,Suite A,Colton,CA 92324 (909)370-4667 FAX(909)370-1046 'Del p 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123 (858)505.8596 FAX(858)505-9689 D 1.I Mar Analytical 9830 South 51 st St.,Suite B-120,Phoenix,AZ 85044 (480)785-0043 FAX(480)785-0851 ' 2520 E.Sunset Rd.#3,Las Vegas,NV 89120(702)798-3620 FAX(702)798-3621 SECOR International,Inc.-Thousand Oaks Project ID: ARCO 3090 Bakersfield t290 Conejo Ridge Avenue,Suite 200 Sampled: 12/27/05 Thousand Oaks,CA 91361 Report Number: IOL2375 Received: 12/28/05 Attention: Andrew Modugno ' BTEX/OXYGENATES by GUMS(EPA 5035/8260B) MDL Reporting Sample Dilution Date Date Data ' Analyte Method Batch Limit Limit Result Factor Extracted Analyzed Qualifiers Sample ID:IOL2375-03(DS-2-2-Soil) Reporting Units: mg/kg ' Benzene EPA•8260B 5L28029 0.58 1.7 ND 1720 12/28/05 12/29/05 Ethylbenzene EPA 8260B 5L28029 0.46 1.7 11 1720 12/28/05 12/29/05 Toluene EPA 8260B 5L28029 0.57 1.7 2.3 1,720 12/28/05 12/29/05 o-Xylene EPA 8260B 51,28029 0.48 1.7 18 1720 12/28/05 12/29/05 m,p-Xylenes EPA 8260B 5L28029 '0.91 1.7 43 1720 12/28/05 12/29/05 Xylenes,Total EPA 8260B '5L28029- 0.91 3.4 61 1720 12/28/05 12/29/05 Di-isopropyl Ether(DIPE) EPA 8260B 5L28029- 0.87 4.3 ND 1720 12/28/05 12/29/05 ' Ethyl tert-Butyl Ether(ETBE) EPA 8260B 5L28029 1.1 4.3 ND 1720 12/28/05 12/29/05 tert-Amyl Methyl Ether(TAME)' EPA 826013 5L28029 1.2 4.3 ND 1720 12/28/05 12/29/05 Methyl-tert-butyl Ether(MTBE) EPA 8260B 5L28029 1.1 4.3 ND .1720 12/28/05 12/29/05 tert-Butanol(TBA) EPA 8260B 5L28029 8.6 86 •ND 1720 12/28/05 12/29/05 ' Ethanol • EPA 8260B 5L28029 170 260 ND 1720 12/28/05 12/29/05 LP Surrogate:Dibromofluoromethane(55-140%) '87% AX Surrogate: Toluene-d8(60-140%) 89% AX ' Surrogate:4-Bromo luorobenzene.(65-140%) 128% AX Sample ID:IOL2375-04(DS-2-6-Soil) Reporting Units: mg/kg ' Benzene EPA 8260B 5L28030 0.00042 0.0017 ND• 0.843 12/28/05 12/28/05 Ethylbenzene EPA 8260B 5L28030 0.00043 0.0017 0.00059 0.843 12/28/05 12/28/05 J,DX Toluene EPA 8266B 5L28030 0.00077 0.0017 ND 0.843' 12/28/05 12/28/05 o-Xylene EPA 8260B 5L28030 0.00040 0.0017 0.0012 0.843 12/28/05 12/28/05 J,DX ' m,p-Xylenes EPA 8260B 5L28030 0.00063 0.0017 0.0026 0.843 12/28/05 12/28/05 Xylenes,Total. EPA 8260B 5L28036 0.00063 -0.0034 0.0039 0.843 12/28/05 12/28/05 Di-isopropyl Ether(DIPE) EPA 8260B 51,28030 0.00031 0.0042 ND - 0.843 12/28/05 12/28/05 ' Ethyl tert-Butyl Ether(ETBE) EPA 8260B 5L28030 :0.00049 0.0042 ND 0.843 12/28/05 12/28/05 tert-Amyl Methyl Ether(TAME) EPA 8260B 5L28030 0.00054 0.0042 ND 0.843 12/28/05 12/28/05 Methyl-tert-butyl Ether(MTBE) ''EPA 8260B• 5L28030 0.00084 0.0042 0.15 0.843 12/28/05 12/28/05 tert-Butanol(TBA) EPA 8260B 5L28030 0.0042 0.042 0.019 0.843 12/28/05 12/28/05 J,DX,ID ' Ethanol . EPA 8260B 5L28030 0.10 0.25 ND 0.843 12/28/05 12/28/05 Surrogate:Dibromofluoromethane(80-125%) 97% Surrogate: Toluene-d8(80-120 91o) 98% ' Surrogate:4-Bromohuorobenzene(80-120%) 93% Del Mar Analytical,Irvine ' Lisa Reightley Project Manager The results pertain only to the samples tested in the laboratory. This report shall not be reproduced, except in full,without written.permission from.Del Mar Analytical. IOL2375 <Page 5 of 22> 1 - t17461 Derian Ave.,Suite 100,Irvine,CA 92614 (949)261-1022 FAX(949)260-3297 1014 E.Cooley Dr.,Suite A,Colton,CA 92324(909)370-4667 FAX(909)370-1046 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123 (858)505-8596 FAX(858)505-9689 l -Mar Analytical a I yti Ca I 9830 South 51st St.,Suite B-120,Phoenix,AZ 85044 (480)785-0043 FAX(480)785-0851 Del 2520 E.Sunset Ril.#3,Las Vegas,NV 89120(702)798-3620 FAX(702)798-3621 SECOR International,Inc.-Thousand Oaks Project ID: ARCO 3090 Bakersfield ' 290 Conejo Ridge Avenue,Suite 200 Sampled: 12/27/05 Thousand Oaks,CA 91361 Report Number: .IOL2375 Received: 12/28/05 Attention: An Modugno ' BTEX/OXYGENATES by GUMS(EPA 5035/8260B) MDL Reporting Sample Dilution Date Date Data ' Analyte Method Batch Limit Limit Result Factor Extracted Analyzed Qualifiers Sample ID:IOL2375-05(DS-3-2-Soil) Reporting Units: mg/kg Benzene EPA 8260B 5L29007 0.00044 0.0018 ND 0.88 12/29/05 12/29/05 Ethylbenzene EPA 8260B , 5L29007 0.00045 . 0.0018 ND 0.88 12/29/05 12/29/05 Toluene EPA 8260B 5L29007 0.00080 . 0.0018 ND 0.88 12/29/05 12/29/05 o-Xylene EPA 8260B 5L29007 0.00041 0.0018 ND 0.88 12/29/05 12/29/05 ' m,p-Xylenes EPA 8260B 5L29007 0.00066 0.0018 ND 0.88 12/29/05 12/29/05 Xylenes,Total EPA 8260B 5L29007 0.00066 0.0035 ND 0.88 12/29/05 12/29/05 Di-isopropyl Ether(DIPE) EPA 8260B 5L29007 0.00033 0.0044 ND' 0.88 12/29/05 12/29/05 ' Ethyl tert-Butyl Ether(ETBE) EPA 8260B 5L29007 0.00051 0.0044 ND 0.88 12/29/05 12/29/05 tert-Amyl Methyl Ether(TAME) EPA 8260B 5L29007 0.00056 '0.0044 ND 0.88 12/29/05 12/29/05 Methyl-tert-butyl Ether(MTBE) EPA 8260B 5L29007 '0.00088 0.0044. ND 0.88 12/29/05 12/29/05 tert-Butanol(TBA) EPA 8260B 5L29007 010044 0.044 ND 0.88 12/29/05 '12/29/05 ' Ethanol EPA 8260B 5L29007 0.11 0.26 ND 0.88 12/29/05 12/29/05 Surrogate:Dibromd luoromethane(80-125%) 103% Surrogate: Toluene-d8(80-120%) 95% ' Surrogate:.4-Bromofluorobenzene(80-120%) 88% Sample ID:IOL2375=06(DS-3-6-Soil) Reporting Units: mg/kg ' Benzene EPA 8260B 5L29007 0.00043 0.0017 ND 0.858 12/29/05 12/29/05 Ethylbenzene EPA'8260B 5L29007 0.00044 0.0017 ND 0.858 12/29/05 12/29/05 Toluene EPA 8260B 5L29007 0.00078 0.0017 ND 0.858 12/29/05 12/29/05 o-Xylene EPA 8260B 5L29007 0.00040 0.0017 ND 0.858 12/29/05 12/29/05 ' m,p-Xylenes EPA 8260B 5L29007 0.00064 0.0017 ND 0.858 12/29/05 12/29/05 Xylenes,Total EPA 8260B 5L29007 0.00064 0.0034 ND 0.858 12/29/05 12/29/05 Di-isopropyl Ether(DIPE) EPA 8260B 5L29007 0.00032 0.0043 ND 0.858 .12/29/05 12/29/05 ' Ethyl tert-Butyl Ether(ETBE) EPA 8260B 5L29007 0.00050 0.0043 ND 0.858 12/29/05 12/29/05 tert-Amyl Methyl Ether(TAME) EPA 8260B 5L29007 0.00055 0.0043 ND 0:858 12/29/05 12/29/05 Methyl-tert-butyl Ether(MTBE) EPA 8260B 5L29007 0.00086 0.0043 ND 0.858 12/29/05 12/29/05 teit-Butanol(TBA) EPA 8260B 5L29007 0.0043 0.043 ND 0.858 12/29/05 12/29/05 ' Ethanol EPA 8260B 5L29007 0.10 0.26 ND '0.858 12/29/05 12/29/05 Surrogate:Dibromq/luoromethane(80-125%) 105% Surrogate: Toluene-d8(80-120%) 94% ' Surrogate:4-Bromq/luorobenzene(80-120%) 87% Del Mar Analytical,Irvine ' Lisa Reightley Project Manager The results pertain only to the samples tested in the laboratory. This report shall not be reproduced, except in full,without written permission from Del Mar Analytical. IOL2375 <Page 6 of 22> ' 17461 Derian Ave.,Suite 100,Irvine,CA 92614 (949)261-1022 FAX(949)260-3297 1014 E.Cooley Dr.,Suite A,Colton,CA 92324(909)370-4667 FAX(909)370-1046 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123 (858)505-8596 FAX(858)505-9689 Del Mar Analytical _ 9830 Soot'51 st St.,Suite B-120,Phoenix,AZ 85044 (480)785.0043 FAX(480)785-0851 2520 E:Sunset Rd.#3,Las Vegas,NV 89120(702)798-3620 FAX(702)798-3621 SECOR International,Inc.-Thousand Oaks Project ID: ARCO 3090 Bakersfield ' 290 Conejo Ridge Avenue,Suite 200 Sampled: 12/27/05 Thousand Oaks,CA 91361 Report Number: IOL2375 Received: 12/28/05 Attention: Andrew Modugno ' BTEX/OXYGENATES by GUMS(EPA 5035/8260B) MDL Reporting Sample Dilution Date Date Data ' Analyte Method Batch Limit Limit Result Factor Extracted Analyzed Qualifiers Sample ID:IOL2375-07(DS-4-2-Soil) Reporting Units: mg/kg ' Benzene EPA 8260B 5L30025 0.00046 0.0018 ND 0.914 12/30/05 12/30/05 Ethylbenzene EPA 8260B 5L30025 0.00047 0.0018 ND 0.914 12/30/05 12/30/05 Toluene EPA 8260B 5L30025 0.00083 0.0018 ND 0.914 12/30/05 12/30/05 o-Xylene EPA 8260B 5L30025 0.00043 0.0018 ND 0.914 12/30/05 12/30/05 ' m,p-Xylenes EPA 8260B 5L30025 0.00069 0.0018 ND 0.914 12/30/05 12/30/05 Xylenes;Total . EPA-8260B 5L30025 0.00069 0.0037 ND 0.914 12/30/05 12/30/05 Di-isopropyl Ether(DIPE) EPA 8260B 5L30025 0.00034 0.0046 ND 0.914 12/30/05 12/30/05 ' Ethyl tert-Butyl Ether(ETBE) EPA 8260B 5L30025 0:00053 0.0046 ND 0.914 12/30/05 12/30/05 tert-Amyl Methyl-Ether(TAME) EPA 8260B 5L30025 0.00059 0.0046 ND 0.914 12/30/05 12/30/05 Methyl-tert-butyl Ether(MTBE) EPA 8260B 5L30025 0.00091 0.0046 ND 0.914 12/30/05 12/30/05 tert-Butanol(TBA)' EPA 8260B 5L30025 0.0046 0.046 ND 0.914 12/30/05 12/30/05 ' Ethanol EPA 8260B 5L30025 0.11 0.27 ND 0.914 12/30/05 12/30/05 Surrogate:Dibromofluoromethane(80-125%) 101 Surrogate: Toluene-d8(80-120%) 106% ' Surrogate:4-Bromofluorobenzene(80-120 91o) 98% Sample ID: IOL2375-08(DS-4-6:Soil) Reporting Units: mg/kg ' Benzene EPA 8260B 5L29007 0.00057 0.0023 ND 1.13 12/29/05 12/29/05 Ethylbenzene EPA 8260B 5L29007 0.0005& 0.0023 ND 1.13 12/29/05 12/29/05 Toluene EPA 8260B 5L29007 0.0010 0.0023 ND 1.13 12/29/05 12/29/05 o-Xylene EPA 8260B 5L29007 0.00053 0.0023 ND 1.13 12/29/05 12/29/05 ' m,p-Xylenes EPA 8260B 5L29007 0.00085 0.0023 ND 1.13 12/29/05 12/29/05 Xylenes,Total EPA 8260B 5L29007 0.00085 0.0045 ND 1.13 12/29/05 12/29/05 Di-isopropyl Ether(DIPE) EPA 8260B 5L29007 0.00042 0.0057 ND 1.13 12/29/05 12/29/05 ' Ethyl tert-Butyl Ether(ETBE) EPA 8260B 5L29007 0.00066 0.0057 ND 1.13 12/29/05 12/29/05 tert-Amyl Methyl Ether(TAME) EPA 8260B 5L29007 '0.00073 0.0057 ND 1.13 12/29/05 12/29/05 Methyl-tert-butyl Ether(MTBE) EPA 8260B 5L29007 0.0011 0.0057 ND 1.13 12/29/05 12/29/05 tert-Butanol(TBA) EPA 8260B 5L29007 0.0057 0.057 ND 1.13 12/29/05 12/29/05 ' Ethanol EPA'8260B 5L29007 0.14 0.34 ND 1.13 12/29/05 12/29/05 Surrogate:Dibromofluoromethane(80-125 91o) 101 % Surrogate: Toluene-d8(80-120%) 94% ' Surrogate:4-Bromofluorobenzene(80-110%) 89% 1 Del Mar Analytical,Irvine ' Lisa Reightley Project Manager The results pertain only to the samples tested in the laboratory. This report shall not be reproduced, except in full,without written permission from Del Mar Analytical. IOL23�5 <Page 7 Of 12> _ 17461 Derian Ave.,Suite 100,Irvine,CA 92614 (949)261-1022 FAX(949)260.3297 1014 E.Cooley Dr.,Suite A,Colton,CA 92324 (909)370.4667 FAX(909)370-1046 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123 (858)505-8596 FAX(858)505-9689 9830 South 51 st St.,Suite B-120,Phoenix,AZ 85044 (480)785-0043 FAX(480)785-0851 Del Mar Analytical ' 2520 E.Sunset Rd.#3,Las Vegas,NV 89120(702)798-3620 FAX(702)798-3621 SECOR International,Inc.-Thousand Oaks Project ID: ARCO 3090 Bakersfield ' 290 Conejo Ridge Avenue,Suite 200 Sampled: 12/27/05 Thousand Oaks,CA 91361 Report Number: IOL2375 Received: 12/28/05 Attention: Andrew Modugno METHOD BLANK/QC=DATA, ' VOLATILE FUEL HYDROCARBONS BY GC/MS (EPA 5035/GCMS) ' Reporting Spike Source' %REC RPD Data Analyte Result Limit MDL Units Level Result %REC Limits RPD Limit Qualifiers Batch: 5L28029 Extracted: 12/28/05 ' Blank Analyzed: 12/28/2005(k28029-BLKI) Volatile Fuel Hydrocarbons(C4-C 12) . ND 10 4.9 mg/kg Surrogate:Dibromofluoromethane' 2.96 mg/kg 2.50 118 55-140 ' Surrogate:Toluene-d8 3.02 mg/kg 2.50 121 60-140 Surrogate:4-Brorn6luoroben.ene 2.93 mg/kg 2.50 ' 117 65-140 LCS Analyzed: 12/28%2005(5L28029-BS2) ' Volatile Fuel Hydrocarbons(C4-C 12) 53.6 10 4.9 mg/kg 50.0. 107 60-130 Surrogate:Dibromojluoromethane 2.88 mg/kg 2.50 115 55-140 Surrogate:Toluene-d8 2.96 mg/kg 2.50 118 60-140 ' Surrogate:4-BromoJluorobenaene 2.94 mg/kg 2.50 118 65-140 LCS Dup Analyzed: 12/29/2005(5L28029-BSD2) Volatile Fuel Hydrocarbons(C4-C 12) 53.5 10 4.9 mg/kg 50.0 107 60-130 0 25 ' Surrogate:Dibromofluoromethane 2.87 mg/kg' 2.50 115 55-140 Surrogate:Toluene-d8 3.02 mg/kg 2.50 111 60-140 Surrogate:4-BromoJluorobenaene 2.90 Mg/kg 2.50 116 65-140 Matrix Spike Analyzed: 12/29/2005(k28029-MS1) Source:IOL2114-06RE2 Volatile Fuel Hydrocarbons(C4-C 12) 119 10 4.9 mg/kg 111 13 95 55-140 Surrogate:DibromoJluoromethane 2.49 mg/kg 2.49 100 55-140 Surrogate:Toluene-d8 2.58 mg/kg 2.49 104 60-140 Surrogate:4-BromoJluorobenzene" 2.48 mg/kg 1.49 100 65-140 Matrix Spike Dup Analyzed: 12/29/2005(SL28029-MSD1) Source:IOL2114-06RE2 Volatile Fuel Hydrocarbons(C4-C 12) 94.4 9.8 4.8 mg/kg 110 13', 74 55-140 23 25 ' Surrogate:Dibromofluoromethane 1.86 mg/kg 1.45 76 55-140 Surrogate:Toluene-d8 1.05 mg/kg 2.45 84 60-140 Surrogate:4-Bromofluorobenzene 1.92 mg/kg 2.45 78 65-140 1 ' Del Mar Analytical,Irvine ' Lisa Reightley Project Manager The results pertain only 7o the sampler tested in the laboratory. This report shall not be reproduced, IOL2375 <Pa g g 8 0 I 22> except in full,without written permission from Del Mar Analytical. , ' 17461 Derian Ave.,Suite 100,Irvine,CA 92614(949)261-1022 FAX(949)260.3297 1014.E.Cooley Dr.,Suite A,Colton,CA 92324 (909)370-4667 FAX(909)370-1046 ' pp �]r �] {' �] 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123(858)505-8596 FAX(858)505-9689 D 1.I MCA 1 A Q I y lI CQ I 9830 South 51st St.,Suite B-120,Phoenix,AZ 85044 (480)785-0043 FAX(480)785-0851 . 2520 E.Sunset Rd.#3,Las Vegas,NV 89120(702)798-3620 FAX(702)798-3621 SECOR International,Inc.-Thousand Oaks Project ID: ARCO 3090 Bakersfield ' 290 Conejo Ridge Avenue,Suite 200 Sampled: 12/27/05 Thousand Oaks,CA 91361 Report Number: IOL2375 Received: 12/28/05 Attention: Andrew Modugno - . x * , ,Myi'yETHOD BL,AN�Kr/QC»�DkAT�A� t�� ' VOL'ATILE FUEL HYDROCARBONS BY GC/MS(EPA 5035/GCMS) ' 'Reporting Spike Source %REC RPD Data Analyte Result Limit MDL Units Level Result %REC Limits RPD Limit Qualifiers Batch: 5L28030 Extracted: 12/28/05 Blank Analyzed: 12/28/2005(5L28030-BLKI) Volatile Fuel Hydrocarbons(C4-C 12)t ND 0.10 0.057 rng/kg Surrogate:Dibromofluoroinethane 0.0481 mg/kg 0.0500 96 80-125 ' Surrogate:Toluene-d8 0.0476 mg/kg 0.0500 95' 80-120 Surrogate:4-Bromofluoroben.ene 0.0449 mg/kg 0.0500 90 80-120 LCS Analyzed: 12/28%2005(SL28030-11S2) ' Volatile Fuel Hydrocarbons(C4--C 12) 1.22 0.10 0.057 mg/kg 1.00 122 60-130 Surrogate:.Dibromofluoromethane 0.0501 mg/kg 0.0500 100 80-125 Surrogate:Toluene-d8 0.0487 mg/kg 0.0500 97. 80-120 ' Surrogate:4-Bromofluorobemene 0.0481 L mg/kg 0.0500 96 80-120 Matrix Spike Analyzed: 12/28/2005(5L28030-MS1) Source:IOL1830-01 Volatile Fuel Hydrocarbons(C4-C 12) 2.74 0.10 0.059 mg/kg 2.30 ND 119 60-135 ' Surrogate:Dibromofluoromethane 0.6482 mg/kg 0.0513 94 80-125 Surrogate:Toluene-d8 0.0496 mg/kg 0.0513 97 80-120 Surrogate:4-Bromofluorobenaene 0.0499 mg/kg 0.0513 97 80-120 , Matrix Spike Dup Analyzed: 12/28/2005(5L28030-MSDI) Source:IOL1830-01 Volatile Fuel Hydrocarbons(C4-C 12) 3.05 0.10 0.059 mg/kg 2.32• ND 131 60-135 11 25 Surrogate:Dibromofluorometha'ne 0.0505 mg/kg 0.0519 97 80-125 Surrogate:Toluene-d8 0.0509 mg/kg 0.0519 98- 80-110 ' Surrogate:4-Bromofluorobensene 0.0506 mg/kg 0.0519 97 80-120 Batch:5L29007 Extracted: 12%29/05 ' Blank Analyzed: 12/29/2005(5L29007-BLKI) - Volatile Fuel Hydrocarbons(C'4-C 12) ND 0.10 0.057 mg/kg Surrogate:Dibronlofluoromethane 0.0473 mg/kg 0.0500 95 80-125 ' Surrogate:Toluene-d8 0.0475 mg/kg 0.0500 95 80-120 Surrogate:4-Bromofluorobenaene 0.0447 mg/kg 0.0500 89 80-120 Del Mar Analytical,Irvine ' Lisa Reightley Project Manager The results pertain only to the samples tested in the laboratory. This report shall not,be reproduced, ' except in full,without written permissionfrom Del Mar Analytical. �OL237S <P age 9 of 22> 1 1 - 17461 Derian Ave.,Suite 100,Irvine,CA 92614 (949)261.1022 FAX(949)260-3297 "- 1014 E.Cooley Dr.,Suite A,Colton,CA 92324(909)370-4667 FAX(909)370-1046 pp ��]]r 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123 (858)505-8596 FAX(858)505-9689 .. - D e I M Q 1 Analytical 9830 South 51st St.,Suite B-120,Phoenix,AZ 85044 (480)785-0043 FAX(480)785-0851 ' 2520 E.Sunset R,Las Vegas,NV 89120(702)798-3620 FAX(702)798.3621 SECOR International,Inc.-Thousand Oaks Project ID: ARCO 3090 Bakersfield ' 290 Conejo Ridge Avenue,Suite 200 Sampled: 12/27/05 Thousand Oaks,CA 91361 Report Number: IOL2375 Received: 12/28/05 Attention: Andrew Modugno 1VI!ETH11D. VOLATILE FUEL HYDROCARBONS BY GC/MS(EPA 5035/GCMS) ' Reporting Spike Source %REC RPD Data Analyte Result" Limit MDL Units Level Result- '%REC Limits RPD Limit Qualifiers Batch: 5L29007 Extracted: 12/29/05 LCS Analyzed: 12/29/2005(5L29007-BS2) Volatile Fuel Hydrocarbons(C4-C12) • 1.12 0.10 0.057 mg/kg 1.00 112 60-130 Surrogate:Dibromofluoromethane 0.0481' mg/kg 0.0500 96 80-125 ' Surrogate:Toluene-d8 0:0482 mg/kg 0.0500 96 80-110 Surrogate:4-Bromofhtorobeniene 0.0475 mg/kg 0.0500 95 80-120 Matrix Spike Analyzed: 12/29/2005(SL29007-MS1) Source:I0L1707-03 Volatile Fuel Hydrocarbons'(C4-C12) 2.55 0.11 0.061 . mg/kg 2.41 ND 106 60-135 Surrogate:Dibromofluoromethane 0.0503 mg/kg 0.0538 93 80-125 Surrogate:Toluene-d8 0.0515 mg/kg 0.0538' 98 80-110 Surrogate:4-Brontofluorobenzene 0.0517 mg/kg 0.0538 96' 80-110 Matrix Spike Dup Analyzed: 12/29/2005(5L29007-MSDI) Source:IOL1707-03 Volatile Fuel Hydrocarbons(C4-C 12) 2.85 0.12 0.068 mg/kg 2.69 ND 106 60-135 11 25 ' Surrogate:Dibromofluoromethane 0.0553 mg/kg 0.0600 91 80-115 Surrogate:Toluene 48 0.0581 mg/kg 0.0600 97 80-120 Surrogate:4-Bromofluorobenzene • 0.0576 mg/kg '0.0600 96 80-110 Batch: 5L30025 .Extracted: 12/30/05 Blank Analyzed: 12/30/2005(5L30025-BLKI) Volatile Fuel Hydrocarbons(C4-C 12) ND 0.10 0.057 mg/kg ' Surrogate:Dibromofluoromethane 0.0510 mg/kg 0:0500 102 80-125 Surrogate:Toluene-d8 0.0518 mg/kg 0.0500 104 80-120 Surrogate:4-Bromofluorobenzene 0.0485 mg/kg 0.0500 97 80-120 LCS Analyzed: 12/30/2005(5L30025-BS2) _. Volatile Fuel Hydrocarbons(C4-C 12) 0.732 0.10 0.057 mg/kg 1.00 73 60-130 Surrogate:Dibromofluoromethane 0.0512 mg/kg 0.0500 102 80-125 ' Surrogate:Toluene-d8 0.0528 mg/kg 0.0500 106 80-120 Surrogate:4-Brontofluorobenzene 0.0510 mg/kg 0.0500 102 80-110 Del Mar Analytical,Irvine Lisa Reightley Project Manager The results pertain only to the samples tested in the laboratory. This report shall not be reproduced, except in full,without written permission from Del Mar Analytical. IOL2375 <Page 10'Of 22> 17461 Derian Ave.,Suite 100,Irvine,CA 92614 (949)261-1022 FAX(949)260-3297 1014 E.Cooley Dr.,Suite A,Colton,CA 92324 (909)370-4667 FAX(909)370-1646 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123(858)505-8596 FAX(858)505-9689 ^ D e I Mar A n a I yti Ca I 9830 South 51st St:,Suite 8.120,Phoenix,AZ 85044 (480)785-0043 FAX(480)785-0851 ' 2520 E.Sunset Rd.#3,Las Vegas,NV 89120(702)798.3620 FAX(702)798-3621 SECOR International,Inc.-Thousand Oaks Project ID: ARCO 3090 Bakersfield ' 290 Conejo Ridge Avenue,Suite 200 Sampled: 12/27/05 Thousand Oaks,CA 91361 Report Number: IOL2375. Received: 12/28/05 Attention: Andrew Modugno METHOD BLANK/QC DATA ' VOLATILE FUEL HYDROCARBONS BY GC/MS EPA 5035/GCMS ' Reporting Spike Source %REC RPD Data Analyte Result Limit MDL Units Level Result •%REC Limits RPD Limit Qualifiers Batch: 5L30025 Extracted: 12/30/05 Matrix Spike Analyzed: 12/30/2005(5L30025-MSI) Source:IOL2304-07 Volatile Fuel Hydrocarbons(C4-C 12) 2.62 0.12 0.067 mg/kg 2.62 ND 100 60-135 Surrogate:Dibromofluoromethane 0.0597 thglkg 0.0585 102 80-125 ' Surrogate:Toluene-d8 0.0615 mg/kg 0.0585 105 80-110 Surrogate:4-Bromofluorobehzene 0.0589 mg/kg -0.0585 101 80-120 Matrix Spike Dup Analyzed: 123012005(k30025-MSDI) Source:IOL2304-07 ' Volatile Fuel Hydrocarbons(C4-C12)- 2.70 0.12 0.070 mg/kg' 2.74 ND '99 60-135 . 3 25 Surrogate:Dibromofluoromethane 0.0621 mg/kg 0.0611 101 80-115 Surrogate:Toluene-d8 0.0642 mg/kg 0.0611 105 80-110 ' Surrogate:4-Brontojluorobenaene 0.0628 mg/kg 0.0611 103 80-120 1 t „ 1 Del Mar Analytical,Irvine ' Lisa Reightley Project Manager The results pertain only to the samples tested in the laboratory. This report shall not be reproduced, except in full,without written permission from Del Mar Analytical.• 1OL2375 <Pgge 11 Of 22> t - 17461 Derian Ave.,Suite 100,Irvine,CA 92614 (949)261.1022 FAX(949)260-3297 1014 E.Cooley Dr.,Suite A,Colton,CA 92324(909)370-4667 FAX(909)370-1046 Mar Analytical 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123 (858)505.8596 FAX(858)505-9689 D l..Qp I M d( 9830 South 51 st St.,Suite B-120,Phoenix,AZ 85044 (480)785-0043 FAX(480)785-0851 ' - 2520 E.Sunset Rd.#3,Las Vegas,NV 89120(702)798-3620 FAX(702)798-3621 SECOR International,Inc.-Thousand Oaks Project ID: ARC 3090 Bakersfield ' 290 Conejo Ridge Avenue,Suite 200 Sampled: 12/27/05 Thousand Oaks,CA 91361 Report Number: IOL2375 Received: 12/28/05 Attention: Andrew Modugno a METHOD BLAN�K�/QC DATA E ssr Rg ' BTEX/OXYGENATES by GUMS(EPA 5035/826013) ' Reporting Spike Source %REC RPD Data Analyte Result Limit MDL Units . Level Result %REC Limits RPD Limit Qualifiers Batch: 5L28029 Extracted: 12/28/05 ' Blank Analyzed: 12/28/2005(5L28029-13LK1) Benzene ND 0.10 0.034 mg/kg Ethylbenzene ND 0.10 0.027 mg/kg ' Toluene ND 0.10 0.033 mg/kg o-Xylene ND 0.10 0.028 mg/kg m,p-Xylenes ND 0.10 0.053 mg/kg ' Xylenes,Total ND 0,20 0.053 mg/kg Di-isopropyl Ether(DIPE) ND 0.25 0.051 mg/kg Ethyl tert-Butyl Ether(ETBE) ND 0.25 0.066 mg/kg tert-Amyl Methyl Ether(TAME) ND 0.25 0.068 rng/kg ' Methyl-tert-butyl Ether(MTBE) ND 0.25 0.062 mg/kg tert-Butanol(TBA) ND 5.0 0.50 mg/kg Ethanol ND 15 10 mg/kg ' Surrogate:Dibromofluoromethane 2.96 mg/kg 1.50 118, 55-140 Surrogate:Toluene-d8 3.02 mg/kg 2.50 121 60-140 Surrogate:4-Bromofluorobenzene 2.93 mg/kg 2.50 117 65-140 ' LCS Analyzed: 12/29/2005(5L28029-BSI) Benzene 2.26 0.10 0.034 mg/kg 2.50 90 65-120 Ethylbenzene 2.34 . 0.10 0.027 mg/kg 2.50 94 80-120 Toluene 2.26 0.10 0.033 mg/kg 2.50 90 80-120 ' o-Xylene 2.42 0.10 0.028 mg/kg 2.50 97 70-125 m,p-Xylenes 4.66 0.10 0.053 mg/kg 5.00 93 70-125 Xylenes,Total 7.08 0.20 0.053 mg/kg 7.50 94 70-125 ' Di-isopropyl Ether(DIPE) 2.32 0.25 0.051 mg/kg 2.50 93 60-140 Ethyl tert-Butyl Ether(ETBE) 2.32 0.25 0.066 mg/kg 2.50 93 66-i40 tert-Amyl Methyl Ether(TAME) 2.50 0.25 0.068 mg/kg 2.50 100 60-145 Methyl-teri-butyl Ether(MTBE) 2.34 0.25 0.062 mg/kg 2.50 94 55-145 ' tert-Butanol(TBA) 13.1 5.0 0.50 mg/kg 12.5 105 65-140 Ethanol 44.1 15 10 mg/kg 25.0 176 35-160 LP Surrogate:Dibromofluoromethane 2.41 mg/kg 2.50 96 55-140 Surrogate:Toluene-d8 1.46 mg/kg 2.50" 98 60-140 Surrogate:4-Bronlofluorobenzene 2.39 mg/kg 2.50 96 65-140 1 Del Mar Analytical,Irvine ' Lisa Reightley Project Manager The results pertain only to the samples tested in the laboratory. This report shall not be reproduced, except in full,without written permission from Del Mar Analytical. IOL2375 <Page 12 Of 22> C 17461 Derian Ave.,Suite 100,Irvine,CA 92614 (949)261-1022 FAX(949)260-3297 1014 E.Cooley Dr.,Suite A,Colton,CA 92324 (909)370-4667 FAX(909)370-1046 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123 (858)505-8596 FAX(858)505-9689 D e^I Mar � 9830 South 51st SL,Suite B-120,Phoenix,AZ 85044 (480)785-0043 FAX(480)785-0851 ' .I`I I 1 Analytical 2520 E.Sunset Rd.#3,Las Vegas,NV 89120(702)798-3620 FAX(702)798-3621 =Ridge nal,Inc.-Thousand Oaks Project ID: ARCO 3090 Bakersfield ' Avenue,Suite 200 Sampled: 12/27/05 A 91361 Report Number: IOL2375 Received: 12/28/05 Modugno 1VIE-TH0QiBE-ANWQC DATA ' BTEX/OXYGENATES by GUMS(EPA 5035/8260B) ' Reporting Spike Source %REC RPD Data Analyte Result Limit MDL Units Level Result %REC Limits RPD Limit Qualifiers Batch: 5L28029 Extracted: 12/28/05 ' LCS Dup Analyzed: 12/29/2005(5L28029-BSD1) Benzene 2.29 0.10 0.034 mg/kg 2.50 92 65-120 1 20 Ethylbenzene 2.38 0.10 . 0.027 mg/kg 2.50 95 80-120 2 20 ' Toluene 2.29 0.10 0.033 mg/kg 2.50 92 80-120 1 20 o-Xylene 2.44 0.10 0.028 mg/kg 2.50 98 70-125 1 20 m,p-Xylenes 4.79 0.10 0.053 mg/kg 5.00 96 70-125 3 20 ' Xylenes,Total 7.23 0.20 0.053 mg/kg 7.50 96 70-125 2 20 Di-isopropyl Ether(DIPE) 2.26 0.25 0.051 mg/kg 2.50 90 60-140 3 20 Ethyl tert-Butyl Ether(ETBE) 2.17 0.25 0.066 mg/kg 2.50 87 60-140 7 20 tert-Amyl Methyl Ether(TAME) 2.18 0.25 0.068 mg/kg 2.50 87 60-145 14 25 ' Methyl-tert-butyl Ether(MTBE) 2.01 0.25 0.062 mg/kg 2.50 80 55-145 15 25 tert-Butanol(TBA) 12.5 5.0 0.50 mg/kg 12.5 100 65-140 5 20 Ethanol 27.0 15 10 mg/kg 25.0 108 35-160 48 30 BA ' Surrogate:Dibromofluoromethane 2.42 mg/kg 2.50 97 55-140 Surrogate:Toluene-d8 1 1 2.46 mg/kg 1.50 98 60-140 Surrogate:4-Brorhofluorobemene 2.38 mg/kg 2.50 95 65-140 ' Matrix Spike Analyzed: 12/29/2005(5L28029-MS1) Source:IOL2114-06RE2 Benzene 2.41 0.10 0.034 mg/kg 2.49 ND 97 55-140 Ethylbenzene 2.46 0.10 0.027 mg/kg 2.49 ND 99 50-150 Toluene 2.44 0.10 0.033 mg/kg 2.49 ND 98 55-140 o-Xylene 2.53 0.10 0.028 mg/kg 2.49 ND 102 55-145 m,p-Xylenes 5.00 0.10 0.053 mg/kg 4.98 ND 100 60-145 Xylenes,Total 7.53 0.20 0.053 mg/kg 7.46 ND 101 55-145 ' Di-isopropyl Ether(DIPE) 2.42 0.25 0.051 mg/kg 2.49 ND 97 60-150 Ethyl tert-Butyl Ether(ETBE) 2.43 0.25 0.066 mg/kg 2.49 ND 98 60-150 tert-Amyl Methyl Ether(TAME) 2.58 0.25 0.068 mg/kg 2.49 ND 104 60-150 Methyl-tert-butyl Ether(MTBE) 2.42 . 0.25 0.062 mg/kg 2.49 ND 97 55-155 ' tert-Butanol(TBA) 13.8 5.0 0.50 mg/kg 12.4 3,7 81 60-155 Ethanol 38.9 15 10 mg/kg 24.9 13 104 .30-160 Surrogate:Dibromofluoromethane 1.49 mg/kg 2.49 100 55-140 ' Surrogate:Toluene-d8 1.58, mg/kg 2.49 104 60-140 Surrogate:4-Brontofluorobenzene 2.48 mg/kg 2.49 100 65-140 Del Mar Analytical,Irvine Lisa Reightley Project Manager The results pertain only to the sampler tested in the laboratory. This report shall not be reproduced, except infull,without written permission from Del Mar Analytical. IOL23 75 <Page 13 of 22> 17461 Derian Ave.,Suite 100,Irvine,CA 92614 (949)261-1022 FAX(949)260.3297 1014 E.Cooley Dr.,Suite A,Colton,CA 92324(909)370-4667 FAX(909)370-1046 Del r '�] /'��] 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123 (858)505-8596 FAX(858)505-9689 D 1.I Mar 1 A Q I I l:Cl I - 9830 South 51st St.,Suite B-120,Phoenix,AZ 85044 (480)785-0043 FAX(480)785-0851 ' 2520 E.Sunset Rd.#3,Las Vegas,NV 89120(702)798.3620 FAX(702)798.3621 SECOR International,Inc.-Thousand Oaks Project ID: ARCO 3090 Bakersfield ' 290 Conejo Ridge Avenue,Suite 200 Sampled: 12/27/05 Thousand Oaks,CA 91361 Report Number: IOL2375 Received: 12/28/05 Attention: Andrew Modugno 1 s - METrHOO D BLA'NK'/QC'DATrA'�� ' BTEX/OXYGENATES by GUMS (EPA 5035/8260B) ' Reporting Spike Source %REC RPD Data Analyte Result Limit MDL Units Level Result %REC Limits RPD Limit Qualifiers Batch: 5L28029 Extracted: 12/28/05 ' Matrix Spike Dup Analyzed: 12/29/2005(5L28029-MSDI) Source:IOL2114-06RE2 Benzene 2.11 0.098 0.033 mg/kg 2.45 ND 86 55-140 13 25 Ethylbenzene 2.28 0.098 0.026 nig/kg 2.45. ND 93 50-150 8 25 ' Toluene 2.68 0.098 0.032 mg/kg 2.45 ND 109 55-140 9 25 o-Xylene 2.39 0.098 0.027 mg/kg 2.45 ND 98 55-145 6 25 m,p-Xylenes 4.85 0.098 0.052 mg/kg, 4.90 ND 99 60-145 3 25 ' Xylenes,Total 7.25 0.20 0.052 rng/kg 7.35 ND 99 55-145 4 25 Di-isopropyl Ether(DIPE) 1.74 0.25 0.050 mg/kg 2.45 ND 71 60-150 33 25 RA Ethyl tert-Butyl Ether(ETBE) 1.54 0.25 0.065 mg/kg 2.45 ND 63 60-150 45 25 "RA tert-Amyl Methyl Ether(TAME) 1.50 0.25 0.067 mg/kg 2.45 ND 61 60-150 53 25 RA ' Methyl-tert-butyl Ether(MTBE) 1.29 0.25 0.061 mg/kg 2.45 ND 53 55-155 61 30 LN,AY;BA,AY tert-Butanol(TBA) 6.70 4.9 0.49 mg/kg 12.3 3.7 24 60-155 69 25 LN,AY,BA,AY. Ethanol 46.5. 15 9.8 mg/kg 24.5 13 137 30-160 18 40 ' Surrogate:Dibromofluoromethane 1.86 mg/kg 1.45 76 55-140 Surrogate:Toluene-d8 2.05 mg/kg 2.45 ' 84 60-140 Surrogate:4-Bromofluorobensene 1.92 mg/kg 1.45 78 65-140 ' Batch: 5L28030 Extracted: 12/28/05 Blank Analyzed: 12/28/2005(5L28030-BLK1) Benzene ND 0.0020 0.00050 mg/kg Ethylbenzene ND 0.0020 0.00051 mg/kg Toluene ND 0.0020 0.00091 mg/kg o-Xylene ND 0.0020 0.00047 mg/kg ' m,p-Xylenes ND 0.0020 0.00075 mg/kg Xylenes,Total ND 0.0040 0.00075 . mg/kg Di-isopropyl Ether(DIPE) ND 0.0050 0.00037 mg/kg Ethyl tert-Butyl Ether(ETBE) ND 0.0050 0.00058 mg/kg ' tert-Amyl Methyl Ether(TAME) ND 0.0050 0.00064 mg/kg Methyl-tert-butyl Ether(MTBE) ND 0.0050 0.0010. mg/kg tert-Butanol(TBA) ND 0.050. 0.0050 mg/kg ' Ethanol ND 0.30 0.12 mg/kg Surrogate:Dibromofluoromethane 0.0481 ing/kg 0.0500 96 80-125 Surrogate:Toluene-d8 0.0476 mg/kg 0.0500 95 80-110 Surrogate:4-Brontofluoroben;ene 6.0449 mg/kg 0.0500 90 80-110 't Del Mar Analytical,Irvine ' Lisa Reightley Project Manager The results pertain only to the samples tested in the laboratory. This report shall not be reproduced, except in full,without written permission from Del Mar Analytical. IOL2375 <Page 14 pf 22> 17461 Derian Ave.,Suite 100,Irvine,CA 92614 (949)261-1022 FAX(949)260-3297, 1014 E.Cooley Dr.,Suite A,Colton,CA 92324(909)376.4667 FAA(909)370-1046 Del r� } '] 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123 (858)505-8596 FAX(858)505.9689 D 1.I Mar A 1 I I y lI CCl I 9830 South 51st SL,Suite B-120,Phoenix,AZ 85044 (480)785-0043 FAX(480)785-0851 ' ' 2520 E.Sunset Rd.#3,Las Vegas,NV 89120(702)798.3620 FAX(702)798.3621 SECOR International,Itic.-Thousand Oaks Project ID: ARCO 3090 Bakersfield 290 Conejo Ridge Avenue,Suite 200 Sampled: 12/27/05 Thousand Oaks,CA 91361 Report Number: IOL2375 Received: 12/28/05 Attention: Andrew Modugno • Ind Fl�"t^�s iI• r r a;, �1,,=.�� y rr ^m� - ., - - METHOD BLANK/QC'-!111W 1 • ;I ' BTEX/OXYGENATESp%b GC/MS EPA 5035/8260B Reporting Spike Source %REC RPD Data Analyte Result Limit tM DL Units Level Result %REC Limits RPD.. Limit Qualifiers Batch: 5L28030 Extracted: 12/28/05 ' LCS Analyzed: 12/28/2005(5L28030-BSI) Benzene 0.0554, 0.0020• 0.00050 mg/kg 0.0500 111 65-120 Ethylbenzene 0.0556 0.0020 0.00051,. ,mg/kg 0.0500 111 70-125 ' Toluene 0.0564 0.0020 0.00091 mg/kg 0.0500 113 70-125 o-Xylene 0.0548 0.0020 0.00047 '' mg/kg 0.0500 . 110 70-125 m,p-Xylenes 0.111 0.0020 0.00075 mg/kg 0.100 111 70-125 ' Xylenes,Total 0.166 0.0040 0,00075 mg/kg 0.150 111 70-125 Di-isopropyl Ether(DIPE) 0.0630 0.0050 0.00037 mg/kg 0.0500 126 60-135 Ethyl tert-Butyl,Ether(ETBE) 0.0627 0.0050 0.00058 mg/kg 0.0500 125 60-135 tert-Amyl Methyl Ether(TAME) 0.0652 0.0050 0.00064 mg/kg 0.6500-. 130 60-140 ' Methyl-tert-butyl Ether(MTBE) 0.0609 0.0050 .0.0010 mg/kg 0.0500 122 55-140 tert-Butanol(TBA) 0.288 0.050 0.0050 mg/kg 0.250 115 65-135 Ethanol 0.508 0.30 0.12 mg/kg 0.500 102 35-160 ' Surrogate:Dibromofluoromethane 0.0516 mg/kk 0.0500 103 86-125 Surrogate:Toluene-d8 0.0487 mg/kg 0.0500 97 80-120 Surrogate:4-Bromofluorobenzene 0.0494 mg/kg 0.0500 99 80-120 ' Matrix Spike Analyzed:,12/28/2005(5L28030-MS1) Source:I0L1830-01 Benzene 0.0533 0.0021 0.00051 mg/kg 0.0513 ND 104 65-130 Ethylbenzene 0.0547 0.0021 0.00052 mg/kg 0.0513 ND 107 70-130 Toluene 0.0537 0.0021 0.00093 mg/kg 0.0513 ND 105 70-125 ' o-Xylene 0.0543• 0.0021 0.00048 mg/kg 0.0513 ND 106 70-125 m,p-Xylenes 0.110 0.0021 0.00077 mg/kg, 0.103 ND 107 70-125 Xylenes,Total 0:164 0.0041 0.00077 'mg/kg 0.154 ND 106 70-125 ' Di-isopropyl Ether(DIPE) 0.0572 0.0051 0.00038 . mg/kg 0.0513 ND 112 60-145 Ethyl tert-Butyl Ether(ETBE) 0.0560. 0.0051 0.00060 mg/kg 0.0513 ND 109 60-140 teit-Amyl Methyl Ether(TAME) 0.0580. 0.0051 0.00066 mg/kg 0.0513 ND 113 60-145 Methyl-tert-butyl Ether(MTBE) 0.0532 0.0051 0.0010 mg/kg 0.0513 ND 104 55-150 ' tert-Butanol(TBA) 0.305 0.051 0.0051 mg/kg 0.257 ND� 1191 65-140 Ethanol 0.553. 0.31 0.12 mg/kg 0.513 ND 108 25-160 Surrogate:Dibromofluoromethane 0.0482 mg/kg 0.0513 94 86-125 ' Surrogate:Toluene-d8 0.0496 mg/kg 0.0513 97 80-120 Surrogate:4-Bromofluorobenaene 0.0499 mg4g 0.0513 97 80-120 Del Mar Analytical,Irvine ' Lisa Reightley Project Manager The results pertain only to the samples tested in the laboratory. This report shall not be reproduced, except in full,without written permission from Del Mar Analytical. IOL2375 <Page 15 of 22> 17461 Derian Ave.Suite 100 Irvine,CA 92614(949)261-1022 FAX(949)260-3297 1014 E.Cooley Dr.,Suite A,Colton,CA 92324 (909)370-4667 FAX(909)370-1046 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123(858)505-8596 FAX(858)505-9689 Del Mar Analytical "• 9x30 South 51st St.,Suite B-120,Phoenix,AZ 85044 (480)785-0043 FAX(480)785-0851 ' 2520 E Sunset Rd.#3,Las Vegas,NV 89120(702)798-3620 FAX(702)798-3621 SECOR International,Inc.-Thousand Oaks Project ID: ARCO 3090 Bakersfield ' 290 Conejo Ridge Avenue,Suite 200 Sampled: 12/27/05 Thousand Oaks,CA 91361 Report Number: IOL2375 Received: 12/28/05 Attention: Andrew Modugno MUTI OD BLANK/QCo,"E TVA) BTEX/OXYGENATES by GUMS EPA 5035/8260B Y � ) . Reporting Spike Source %REC RPD Data Analyte Result Limit MDL Units Level Result %REC Limits RPD Limit Qualifiers Batch:5L28030 Extracted: 12/28/05 ' Matrix Spike Dup Analyzed: 12/28/2005(5L28030-MSDI) Source:IOL1830-01 Benzene 6.0586 0:0021 0.00052 mg/kg 0.0519 ND 113 65-130 9 20 Ethylbenzene 0.0590 0.0021 0.00053 . mg/kg 0.0519 ND 114 70-130 8 25 ' Toluene 0.0600 0.0021 0.00094 mg/kg 0.0519 ND 116 70-125 11 20 o-Xylene 0.0590 0.0021 0.00049 mg/kg 0.0519 ND 114 70-125 8 25 m,p-Xylenes 0.119 0.0021 0.00078 mg/kg 0.104 ND 114 70-125 8 25' ' Xylenes,Total 0.178 0.0041 0.00078 mg/kg 0.156 ND 114 70-125 8 25 Di-isopropyl Ether(DIPE) 0.0648 6.0052 0.00038 mg/kg 0.0519 ND 125 60-145 12 25 Ethyl tert-Butyl Ether(ETBE) 0.0636 0.0052 0.00060 mg/kg 0.0519 ND 123 60-140 13 30 tert-Amyl Methyl Ether(TAME) 0.0660 0.0052 0.00066 mg/kg 0.0519 ND 127 60-145 13 25 Methyl-tert-butyl Ether(MTBE) 0.0616 0.0052 0.0010 mg/kg 0.0519 ND 119 55-150 15 35 tert-Butanol(TBA) 0.285 0.052 0.0052 mg/kg. 0.259 ND 110 65-140 7 30 Ethanol 0.498 0.31 0.12 mg/kg 0.519 ND 96 25-160 10 40 ' Surrogate:Dibromofluoromethane 0.0505 mg/kg 0.0519 97 80-125. Surrogate:Toluene-d8 0.0509 mg/kg 0.0519 98 80-120 Surrogate:4-Bromofluorobenzene 0.0506 mg/kg 0.0519 97 80-120 ' Batch:5L29007 Extracted: 12/29/05 Blank Analyzed: 12/29/2005(5L29007-BLKI) Benzene ND 0.0020 0.00050 mg/kg Ethylbenzene ND 0.0020 0.00051 mg/kg Toluene ND 0.0020 0.00091 mg/kg o-Xylene ND 0.0020 0.00047 mg/kg ' m,p-Xylenes ND 0.0020 0.00075 mg/kg Xylenes,Total ND •0.6040 0.00075 mg/kg Di-isopropyl Ether(DIPE) ND 0.0050 0.00037 mg/kg Ethyl tert-Butyl Ether(ETBE) ND 0.0050 0.00058 mg/kg ' tert-Amyl Methyl Ether(TAME) ND 0.0050 0.00064 mg/kg Methyl-tert-butyl Ether(MTBE) ND 0.0050 0.0010 mg/kg tert-Butanol(TBA) ND 0.050 0.0050 mg/kg ' Ethanol ND 0.30 0.12 mg/kg Surrogate:Dibromofluoromethane 0.0473 mg/kg 0.0500 95 80-125 Surrogate:Toluene-d8 0.0475 mg/kg. 0.0500 95 80-120 Surrogate:4-Bromofluorobenzene 0.0447 mg/kg 0.0500 89 80-120 Del Mar Analytical,Irvine . ' Lisa Reightley Project Manager The results pertain only to the samples tested in the laboratory. This report shall not be reproduced, except in full,without written permission from Del Mar Analytical. /OL237$ <Page 16 of 22> 17461 Dorian Ave.,Suite 100,Irvine,CA 92614 (949)261-1022 FAX(949)260-3297 1014 E.Cooley Dr.,Suite A,Colton,CA 92324 (909)370-4667 FAX(909)370-1046 - 9484 Chesapeake Dr.;Suite 805,San Diego,CA 92123(858)505-8596 FAX(858)505-9689 t• 9830 South 51st SC,Suite B-120,Phoenix,AZ 85044 (480)785.0043 FAX(480)785-0851 ? Del M d Analytical ,2520 E.Sunset Rd.#3,W Vegas,NV 89120 1702)798-3620 FAX(702)798-3621 SECOR International,Inc.-Thousand Oaks Project ID: ARCO 3090 Bakersfield ' 290 Conejo Ridge Avenue,Suite 200 Sampled: 12/27/05 Thousand Oaks,CA 91361 Report Number: IOL2375' Received: 12/28/05 Attention:,.Andrew Modugno i { lta�: • s i1 A, MEVTH®D BL'AIYIK/QCDAT=A ' BTEX/OXYGENATES by GUMS (EPA 5035/8260B) Reporting Spike Source %REC RPD Data ' Analyte Result Limit MDL Units Level Result. %REC Limits RPD Limit Qualifiers Batch: 5L29007.Extracted: 12/29/05 ' LCS Analyzed: 12/29/2005(5L29007-BSI) Benzene 0.0480 0.0020 0.00050 mg/kg 0.0500 96 65-120 Ethylbenzene 0.0497 0.0020 0.00051 mg/kg 0.0500 99. 70-125 ' Toluene 0.0489 0.0020 0.00091 mg/kg 0.0500 98 70-125 o-Xylene 0.0484 0.0020 0.00047 mg/kg 0.0500 97 70-125 m,p-Xylenes 0.0984 0.0020 0.00075 mg/kg 0.100 98 70-125 ' Xylenes,Total 0.147 0.0040 0.00075 mg/kg 0.150 98 70-125 Di-isopropyl Ether(DIPE) 0.0524 0.0050 0.00037 mg/kg 0.0500 105 60-135 Ethyl tert-Butyl Ether(ETBE) 0.0501 0.0050 0.00058 mg/kg 0.0500 100 60-135 tert-Amyl Methyl Ether(TAME) 0.0518 .0.0050 0.00064 mg/kg 0.0500 104 60-140 ' Methyl-tert-butyl Ether(MTBE) 0.0489 0.0050 . 0.0010 mg/kg 0.0500 98 55-140 tert-Butanol(TBA) 0.271 0.050 0.0050 mg/kg 0.250 108 65-135 Ethanol 0.522 0.30 0.12 mg/kg 0.500 104 35-166 ' Surrogate:DibromoJluoromethane 0.0491 mg/kg 0.0500' 98 80-125 Surrogate:Toluene-d8 0.0488 mg/kg 0.0500 98 80-120 Surrogate:4-Bromofluorobenaene 0.0483 mg/kg 0.0500 97 80-120 ' Matrix Spike Analyzed: 12/29/2005(509007-MSl) Source:IOL1707-03 Benzene 0.0565 0.0022 0.00054 mg/kg 0.0538 ND 94 65-130 Ethylbenzene 0.0528 0.0022 0.00055 mg/kg' 0.0538 ND 98 70-130 Toluene 0.0513 0.0022 0.00098 mg/kg 0.0538 ND 95 70-125 ' o-Xylene 0.0515 0.0022 0.00051 mg/kg • 0.0538 ND 96 -70-125 m,p-Xylenes 0.104 0.0022 0.00081 mg/kg 0.108 ND 96 70-125 Xylenes,Total 0.156 0.0043 0.00081 mg/kg 0.161 ND 97 70-125 ' Di-isopropyl Ether(DIPE) 0.0544 0.0054 0.00040 mg/kg 0.0538 ND 101 60-145 Ethyl tert-Butyl Ether(ETBE) 0.0525 0.0054 0.00062 mg/kg 0.0538 ND .98 60-140 tert-Amyl Methyl Ether(TAME) 0.0536 0.0054 0.00069 mg/kg 0.0538 ND 100 60-145 Methyl-tert-butyl Ether(MTBE) 0.0506 0.0054 0.0011` mg/kg., 0.0538 ND 94 55-150 ' tert-Butanol(TBA) 0.284 0.054 0.0054 mg/kg 0.269. ND 106 65-140 • Ethanol 0.524 0.32 0.13 mg/kg, 0.538 ND 97 25-160 Surrogate:Di bromofluoromethane 0.0503 mg/kg. 0.0538 93 80-125 tSurrogate:Toluene-d8 0.0525 'mg/kg 0.0538 98 80-120 Surrogate:4-Bromofluoroben_ene 0.0517 mg/kg 0.0538 96 80-120 Del Mar Analytical,Irvine ' Lisa Reightley Project Manager The results pertain only to the samples tested in the laboratory. This report shall not be reproduced, except in full,without written permission from Del Mar Analytical. IOL2375 <Ppge 17 Of 22> 17461 Derian Ave.,Suite 100,Irvine,CA 92614 (949)261-1022 FAX(949)260-3297 1014 E.Cooley Dr.,Suite A,Colton,CA 92324'(909)370-4667 FAX(909)370-1046 e 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123(858)505.8596 FAX(858)505-9689 9830 South 51st St-,Suite B-120,Phoenix,AZ 85044 (480)785-0043 FAX(480)785-0851 Del Mar Analytical ' 2520 E.Sunset Rd.#3,Las Vegas,NV 89120(702)798-3620 FAX(702)798-3621 SECOR International,Inc.-Thousand Oaks Project ID: ARCO 3090 Bakersfield ' 290 Conejo-Ridge Avenue,Suite 200 Sampled: 12/27/05 Thousand Oaks,CA 91361 Report Number: IOL2375 Received: 12/28/05 Attention: Andrew Modugno 'd„METHOD- BL�A�NKt/�QCDA�T�A BTEX/OXYGENATES by GUMS(EPA•5035/8260B) ' Reporting Spike Source %REC RPD Data Analyte Result Limit MDL Units Level Result. %REC Limits RPD Limit Qualifiers Batch: 5L29001.Extracted: 12/29/05 ' Matrix Spike Dup Analyzed: 12/29/2005(5L29007-MSD1) Source:IOL1707-03 Benzene 0.0561 0.0024 0.00060 mg/kg 0.0600 ND 94 65-130 11 20 Ethylbenzene 0.0586 0.0024 0.00061 mg/kg 0.0600 ND 98 70-130 10 25 ' Toluene ! 0.0576 0.0024 0.0011 mg/kg 0.0600 ND 96. 70-125 12 20 o-Xylene 0.0563 0.0024 0.00056 mg/kg 0.0600 ND 94 70-125 9 25 m,p-Xylenes 0.115 0.0024 0.00090 mg/kg 0.120 ND 96 70-125 10 25 ' Xylenes,Total 0.172 0.0048 0.00090 mg/kg 0.180 ' ND 96 70-125 10 25 Di-isopropyl Ether(DIPE) 0.0603 0.0060 0.00044 'mg/kg' 0.0600 ND 100 60-145 10 25 Ethyl tert-Butyl Ether(ETBE) 0.0590 0.0060 0.00070 mg/kg 0.0600 ND 98 60-140 12 30 ter-Amyl Methyl Ether(TAME) 0.0607 0.0060 0.00077 mg/kg 0.0600 ND 101 60-145 12 25 ' Methyl-tert-butyl Ether(MTBE) 0.0570 0.0060 0.0012 mg/kg 0.0600 ND 95 55-150 12 35 tert-Butanol(TBA) 0.308 0.060 0.0060 mg/kg 0.300 ND 103 65-140 8 30 Ethanol 0.547 0.36 0.14 mg/kg 0.600 ND 91 25-160 4 40 ' Surrogate:Dibromofluoromethane 0.0553 mg/kg 0.0600 92 80-125 Surrogate:Toluene-d8 0.0582 mg/kg 0.0600 97 80-120 Surrogate:4-Bromofluorobeti:ene 0.0576 mg/kg 0.0600 96 80-120 ' Batch: 5L30025 Extracted: 12/30/05 Blank Analyzed: 12/30/2005(5L30025-BLKI) Benzene ND 0.0020 0.00050 mg/kg ' Ethylbenzene ND 0.0020 0.00051 mg/kg Toluene ND 0.0020 0.00091 mg/kg o-Xylene ND. 0.0020 0.00047 mg/kg ' m,p-Xylenes ND 0.0020 0.00075 mg/kg Xylenes,Total ND 6.0040 0.00075 mg/kg Di-isopropyl Ether(DIPE) ND 0.0050 0.00037 mg/kg Ethyl tart-Butyl Ether(ETBE) ND 0.0050 0.06058 mg/kg tert-Amyl Methyl Ether(TAME) ND 0.0050 0.00064 mg/kg Methyl-tert-butyl Ether(MTBE) ND 0.0050 0.0010 mg/kg tert-Butanol(TBA) ND 0.050 0.0050 mg/kg ' Ethanol ND 0.30 0.12 mg/kg Surrogate:Dibromofluoromethane 0.0510 mg/kg 0.0500 102 80-125 Surrogate:Toluene-d8 . 0.0518 mg/kg 0.0500 104 80-120 Surrogate:4-Bromofluorobenzene 0.0485 mg/kg 0.0500 97 80-120 Del Mar Analytical,Irvine ' Lisa Reightley 'Project Manager The results pertain only to the samples tested in the laboratory. This report shall not be reproduced, except in full,without written permission from Del Mar Analytical. IOL2375 <page I8 o,f 22> 1 ' 17461 Derian Ave.,Suite 100,Irvine,CA 92614 (949)261-1022 FAX(949)260-3297 1014 E.Cooley Dr.,Suite A,Colton,CA 92324(909)370-4667 FAX(909)370-1046 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123 (858)505.8596 FAX(858)505-9689 9830 South 51st SL,Suite B-120,Phoenix,AZ 85044 (480)785-0043 FAX(480)785-0851 Del M a r A n a I yti ea I ' 2520 E.Sunset Rd.#3,Las Vegas,NV 89120(702)798-3620 FAX(702)798-3621 SECOR International,Inc.-Thousand Oaks Project ID: ARCO 3090 Bakersfield ' 290 Conejo Ridge Avenue,Suite 200 Sampled: 12/27/05 Thousand Oaks,CA 91361 Report Number: IOL2375 Received: 12/28/05 Attention: Andrew Modugno ��� METHOD BLANK/QCDA'aTA �. BTEX/OXYGENATES by GUMS(EPA 5035/8260B) ' Reporting Spike Source %REC RPD Data Analytc Result Limit MDL Units Level ' Result %REC Limits RPD Limit Qualifiers Batch: 51L30025 Extracted: 12/30/05 ' LCS Analyzed: 12/30/2005(5L30025-BSl) Benzene 0.0449 0.0020 0.00050 mg/kg 0.0500 90 65-120 Ethylbenzene 0.0503 0.0020 0.00051 mg/kg 0.0500 101 70-125 ' Toluene 0.0466 0.0020 0.00091 mg/kg 0.0500 93 70-125 o-Xylene 0.0519 0.0020 0.00047 mg/kg 0.0500 104 70-125 m,p-Xylenes 0.102 0.0020 0.00075 mg/kg 0.100 102 70-125 ' Xylenes,Total 0.154 0.0040 0.00075 mg/kg 0.150 103 70-125 Di-isopropyl Ether(DIPE) 0.0441 0.0050 0.00037 mg/kg 0.0500 88 60-135 Ethyl tert-Butyl Ether(ETBE) 0.0431 0.0050 0.00058 mg/kg 0.0500 86 60-135 tert-Amyl Methyl Ether(TAME) 0.0458 0.0050 0.00064 mg/kg 0.0500 92 60-140 Methyl-tert-butyl Ether(MTBE) 0.0406 0.0050 0.0010 mg/kg 0.0500 81 55-140 tert-Butanol(TBA) 0.266 0.050 0.0050 mg/kg 0.250 106 65-135 Ethanol 0.714 0.30 0.12 mg/kg 0.500 143 35-160 ' Surrogate:Dibromofluoromethane 0.0495 mg/kg 0.0500 99 80-125 Surrogate:Toluene-d8 0.0520 mg/kg 0.0500 104 80-120 Surrogate:4-Bronlofluorobertaene 0.0499 mg/kg 0.0500 100 80-120 ' Matrix Spike Analyzed: 12/30/2005(5L30025-MS1) Source:1[OL2304-07 Benzene 0.0547 0.0023 0.00059 mg/kg 0.0585 ND 94 65-130 Ethylbenzene 0.0600 0.0023 0.00060 mg/kg 0.0585 ND 103 70-130 Toluene 0.0560 0.0023 0.0011 mg/kg 0.0585 ND 96 70-125 ' o-Xylene 0.0622 0.0023 0.00055 mg/kg 0.0585 ND 106 70-125 m,p-Xylenes 0.121 0.0023 0.00088 mg/kg 0.117 ND 103 70-125 Xylenes,Total 0.183 0.0047 0.00088 mg/kg 0.176 ND 104 70-125 ' Di-isopropyl Ether(DIPE) 0.0544 0.0059 0.00043 mg/kg 0.0585 ND '. 93 60-145 Ethyl tert-Butyl Ether(ETBE) 0.0530 0.0059 0.00068 mg/kg 0.0585 ND 91 60-140 tert-Amyl Methyl Ether(TAME) 0.0564 0.0059 0.00075 mg/kg 0.0585 ND 96 60-145 Methyl-tert-butyl Ether(MTBE) 0.0512 0.0059 0:0012 mg/kg 0.0585 ND 88 55-150 ' tert-Butanol(TBA) 0.322 0.059 0.0059 mg/kg 0.293. ND 110 65-140 Ethanol 0.602 0.35 0.14 mg/kg 0.585 ND 103 25-160 Surrogate:Dibromofluoromethane 6.0597 mg/kg 0.0585 102 80-125 ' Surrogate:Toluene-d8 0.0615 mg/kg 0.0585 105 80-120 Surrogate.4-Bromofluorobemene 0.0589 mg/kg 0.0585 /01 80-120 1 Del Mar Analytical,Irvine ' Lisa Reightley Project Manager The results pertain only to the samples tested in the laboratory. This report shall not be reproduced, except in full,without written permission from Del Mar Analytical. 1OL2375 <Page 19 Of 22> ( 17461 Derian Ave.,Suite 100,Irvine,CA 92614 (949)261-1022 FAX(949)260-3297 1014 E.Cooley Dr.,Suite A,Colton,CA 92324(909)370-4667 FAX(909)370-1046 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123 (858)505-8596 FAX(858)505-9689 i' 9830 South 51st St,Suite 8-120,Phoenix,AZ 85044,(480)785-0043 FAX(480)785.0851 ' Del M Analytical .2520 E.Sunset Rd.#3,Las Vegas,NV 89120(702)798-3620 FAX(702)798-3621 i L SECOR International,Inc.-Thousand Oaks Project ID: ARCO 3090 Bakersfield 290 Conejo Ridge Avenue,Suite 200 Sampled: 12/27/05 Thousand Oaks,CA 91361 Report Number: IOL2375 Received: 12/28/05 Attention: Andrew Modugno ¢ lit . METHOD BLANK/QC DATA 5 ' MX/OXYGENATES by GUMS(EPA 5035/8260B) ' Reporting Spike Source %REC RPD Data Analyte Result Limit MDL Units Level Result %REC Limits RPD Limit Qualifiers Batch: 5L30025 Extracted: 12/30/05 ' Matrix Spike Dup'Analyzed: 12/30/2009(5L30025-MSD1) Source:IOL2304-07 Benzene 0.0565 0.0024 0.00061 mg/kg 0.0611 ND 92 65-130 3 20 Ethylbenzene 0.0644 0.0024 0.00062 mg/kg 0.0611 ND 105 70-130 7 25 ' Toluene 0.0587 0.0024 0.0011 mg/kg 0,0611 ND 96 70-125 5 20 o-Xylene 0.0664 0.0024 0.00057 mg/kg 0.0611 ND 109 70-125 7 25 m,p-Xylenes 0.129. 0.0024 0.00092 mg/kg 0.122 ND 106 70-125 6 25 Xylenes,Total 0.196 0.0049 0.00092 mg/kg 0.183' ND 107 70-125 7 �5 Di-isopropyl Ether(Dlk) -0.0559 0.0061 0.00045 mg/kg 0.0611 ND 91 60-145 3 25 Ethyl tert-Butyl Ether(ETBE) 0.0551 0.0061 0.00071 mg/kg 0.0611 ND 90 60-140 4 30 tert-Amyl Methyl Ether(TAME) 0.0602 0.0061 0.00078 mg/kg, .0.0611 ND 99 60-145 7 25 ' M ethyl-tert-butyl Ether(MTBE) 0.0542 0.0061 0.0012 mg/kg 0.0611 ND 89 55-150 6 35 tert-Butanol(TBA) 0.336 0.061 0.0061 mg/kg 0.306 ND 110 65-140 4 30 Ethanol 0.544 0.37 0.15 mg/kg 0.611 ND 89 25-160 10 40 ' Surrogate:Dibromofluoromethane 0.0621 mg/kg 0.0611 . 102 80-125 Surrogate:Toluene-d8 0.0642 mg/kg 0.0611 105 80-120 Surrogate:4-Bromofluorobertsene 0.0628 mg/kg 0.0611 103 80-120 1 Del Mar Analytical,Irvine ' Lisa Reightley Project Manager The results pertain only to the samples tested in the laboratory. This report shall not be reproduced, exec ept in full,without written permission from Del Mar Analytical. IOL2375 <Page 2Q of 22> 1 17461 Derian Ave.,Suite 100,Irvine,CA 92614 (949)261-1022 FAX(949)260-3297 1014 E.Cooley Dr.,Suite A,Colton,CA 92324(909)370-4667 FAX(909)370-1046 Q �] �] �] 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123'(858)505-8596 FAX(858)505-9689 -,• D e I M d C A n d I yt I C 1 I 9830 South 51 a SL,Suite B-120,Phoenix,AZ 85044 (480)785-0043 FAX(480)785-0851 - 1 2520 E.Sunset Rd.#3,Las Vegas,NV 89120(702)798.3620 FAX(702)798.3621 SECOR International,Inc.-Thousand Oaks Project ID: ARCO 3090 Bakersfield ' 290 Conejo Ridge Avenue;Suite 200 Sampled: 12/27/05 . Thousand Oaks,CA 91.361 Report Number: IOL2375 Received: 12/28/05 Attention: Andrew Modugno 1 DATA QUALIFIERS AND DEFINITIONS ' AX Sample too dilute to.quantify surrogate BA Relative percent difference out of control BA,AV The RPD exceeded the method control limit due to sample matrix effects ' 1D Analyte identified by RT&presence of single mass ion J,DX EPA Flag-Estimated value,Value<lowest standard(MQL),but>than MDL LN,AV The MS and/or MSD were below the acceptance limits due to sample matrix interference. See Blank Spike(LCS). LP Laboratory Control Sample recovery was above,method control limits.Analyte not detected,data not impacted. RA RPD exceeds limit due to matrix•interf.;%recovs.within limits ND Analyte NOT DETECTED at or above the reporting limit or MDL,if MDL is specified. '. RPD Relative Percent Difference ADDITIONAL COMMENTS ' For 8260 analyse§: Due to the high water solubility of alcohols and ketones,the calibration criteria for these compounds is<30%RSD. The average%RSD of all compounds in the calibration is 15%,in accordance with EPA methods. ' For Volatile Fuel Hydrocarbons(C4-C12): . Volatile Fuel Hydrocarbons(C4-C12).are quantitated against a gasoline standard. Quantitation begins immediately before TBA-d9. 1 1 ' 1 - Del Mar Analytical,Irvine ' Lisa Reightley Project Manager The results pertain only to the samples tested in the laboratory. T his report shall not be reproduced, except in full,without written permission from Del Mar Analytical. IOL2375 <Page 2I,of 22> - 17461 Derian Ave.,Suite 100,Irvine,CA 92614 (949)261-1022 FAX(949)260-3297 1014 E.Cooley Dr.,Suite A,Colton,CA 92324(909)370-0667 FAX(909)370-1.046 9484 Chesapeake Dr.,Suite 805,San Diego,CA 92123(858)505-8596 FAX(858)505-9689 D e I Mar A n 9830 South 51st St.,Suite B-120,Phoenix,AZ 85044(480)785-0043 FAX(480)785-0851 a.l vti Ca I ' 2520 E.Sunset Rd.#3,Las Vegas,NV 89120(702)798-3620 FAX(702)798-3621 SECOR International,Inc.-Thousand Oaks Project ID: ARCO 3090 Bakersfield ' 290 Conejo Ridge Avenue,Suite 200 Sampled: 12/27/05 Thousand Oaks,CA 91361 Report Number: IOL2375 Received: 12/28/05 Attention: Andrew Modugno ' Certification Summary Del Mar Analytical,Irvine Method Matrix Nelac California ' EPA 8260B Soil X X. EPA 8260B Soil-extr X X TPH by GC/MS Soil X X ' TPH by GC/MS Soil-extr X X Nevada and NELAP provide analyte specific accreditation. Analyze specific information for Del Mar Analytical maybe obtained by contacting the laboratory or visiting our websize at www.dmalabs.com. 1 A Del Mar Analytical,Irvine ' Lisa Reightley Project Manager The results pertain only to the samples tested in the laboratory. This report shall not be reproduced, except in full,without written permission from Del Mar Analytical. 1OL2375 <Page 22 of 22> Page_of A ;<: Chain of Custody Record Oil-site Titre: Tenp: Project Name Despenser Removal and Upgrade Off-site Titre: Temp: BP BU/GEM CO Portfolio: Retail(Coastal+C. LA) Sky Conditions: BP Laboratory Contract Number: Atlantic Richfield Meteorological Events:. Requested Due Date(umddd/yy) Standard TAT Wind Speed: Direction: Send To: BP/GEM Facility No.: 3090 Consultant/Contractor: SECOR International,Inc. w Lab Name: Del Mar Analytical BP/GFM Facility Addretc: 3333 Union Ave.Bakersfield,CA Address: 290 Cone•o Ridge Ave.,Suite 200 Lab Address: 2852 Alton"Ave. Site ID No. Thousand Oaks,CA 91361 Irvine,CA92606 Sitclat/L.o Lat.35.3893422 Long*-119.0029319 -rmilEDD: bauchard @secor.com California Global ID#: T0602900569 Consultant/Contractor Project No.: 37BP 9962 112 Lab PA 4j ap +=t Z k;4 &hris Roberts BP/GEM PM Contact: Roy Thun Consultant/Contractor Tele/Fax: ' 805 230-1266 TPt. 949-261-1022/949-261-1228 Address:_ 4 Center point Dr. Consultant/Contractor PM: Anity Modu no Report Type&QC Level: Standard La Palrna,CA 11invoicc to: Consultant BP/GEM Account No:: ele/Faa: 661 287-3855 JJBPIGETM Work Release Nor lab Bottle Order No: Matrix Preservatives Requested Analysis N '.Vr C - Field Point Name! No. Sample Description 5 O Laboratory No. "� q > . (+�— Comments F v T > x0 o � , y = O x" x x cco t- 1 TES _ N.'�.� 124-7 X I I 3 X �.cA5t - = n- TLA A a14 4 - S - G LG , ( Z-7 s _ _ Z 6 <' — w :.Ti-t� 9 _ 10 Samplees Name: Relin ulsbedB /AMliation Daft Time Ace ted By Afrdiation.' ate Tina Samples C 6 Shp [Went Da►e: 2 ^'Z Shipment Method: Shipment Tracking No: Special.Instr-uctions: Custody Seals In Place Yes_No ✓ TerrW Blank Yes_No Cooler Temperattire on Receipt °F/C -Trip Blank Yes_No BP COC Rev.3 12/15103 1 ' APPENDIX D ' Underground Storage Tank Unauthorized Release Report 1 1 , 1 BP West Coast Products LLC by 4 Centerpo)nte Drive La Palma,CA 90623-1066 Mailing Address: PO Box 6038 Artesia.CA, 90702-6038 voice (714)670-3958 Fax (714)670.5420 Emall Tglesa.Miierj ba•�om .lanuary 18,2006 VIA US MAIL Inspector Steve Underwood Bakersfield Fire Department ' 1715 Chester Ave.,3rd Floor Bakersfield, CA 93301 RE: Arco Facility No. 03090 3333 Union Avenue Bakersfield, CA 93305 Dear Mr_ Underwood, With this, I am transmitting an Underground Storage Tank.Unauthorized Release Report in connection with a incident at the facility noted above. Please feel free to call me at (714) 670- 3958 with any questions. Sincerely, Teresa S.Miles Environmental Compliance Specialist U.S. Convenience Operations TM/cc cc: Central Valley RWQCB (Region 5) ' Andrew Modugno/SECOR Jack Oman File 3090 ' DISCLAIMER: This message (including"attachments, if any) contains confidential proprietary information, some. or all of which may be legally privileged or otherwise protected from unauthorized use,di3closure, distribution or copying. It is for the intended recipient only. If you ' are not the intended recipient, you may not use, disclose, distribute, copy, print or retain this message or any part of it.If you have received this message in error,please notify us immediately by calling(714)670-5423 collect. NDERGROUND STORAGE TANK UNAUTHORIZED RELEASE (LEAK)/ CONTAMINATION SITE REPORT ERGENCY HAS STATE OFFICE OF EMERGENCY SERVICES :FpR'l.QCAb,PG.�rN�Y'�SE'GNGYy '. REPORT BEEN FILED? j,NEREE)Y¢GRTIFY THlSr 1 HAVF�D,($TRIDUTED THIS INF,ORMATjO{1 ACCgROING TO T'HE'• [DYES ®NO ❑YES ®NO •DISTRIBUTION:SHI�WN•.ONTHE,I N$TRUCT)ONSHE�TONTME,BACK PAGE OF.THI$,FORM ORT OATS CASE t M M 0 �) Y Y d SIwNED ,' 'I• �AT� . NAME OF INDIVIDUAL FILING REPORT PHONE SIGNATURE Teresa S.Miles 714-570-3958 REPRESENTING OWNERIOPERATOR ❑REGIONAL BOARD COMPANY OR AGENCY NAME p ❑LOCAL AGENCY ❑OTHER BP West Coast Products LLC a ADDRESS 4 Centerpointe Dr. La Palma CA 90622 STREET CITY STATE ZIP w NAME CONTACT PERSON PHONE e i= BP West Coast Products LLC UNKNOWN Teresa S.Miles 714-670-3958 ADDRESS 4 Centerpointe Dr. La Palma CA 90622 STREET CITY STATE ZIP FACILITY NAME(IF APPLICABLE) OPERA'(OR PHONE Arco Facility No. 03090 ' Munther Hawatmeh 661-324-8517 ¢ ADDRESS , b 3333 Union Avenue Bakersfield Kern 93305 STREET CITY COUNTY ZIP CROSS STREET 34th LOCAL AGENCY AGENCY NAME CONTACT PERSON PHONE y E5 Bakersfield Fire Department Inspector Steve Underwood (661)326-3979 w W REGIONAL BOARD P14ONE a 4 Central Valle RWOCB!Region 5) 559)445-5116 w (1) NAME QUANTITY LOST(GALLONS) v° ® UNKNOWN m_ y ❑ uwwowN 2 DATE DISCOVERED ISCOVERED ❑ INVENTORY CONTROL ❑ SUBSURFACE MONITORING NUISANCE CONDITIONS f O 1 1 2 O NK TEST ❑ TANK REMOVAL ® OTHER Secondary containment upgrade 11 DATE DISCHARGE BEGAN Y TY �� METHOD U SED T, ,STOP DISCHARGE(CHECK ALL THAT APPLY) d ❑ REMOVE CONTENTS ❑ CLOSE TANK&REMOVE ❑REPAIR PIPING M M o p Y Y UNKNOWN HAS DISCHARGE BEEN STOPPED? ❑ REPAIR TANI(' ❑ CLOSE TANK&FILL IN PLACE ❑ CHANGE PROCEDURE q M p p Y Y ❑ REPLACE TANK OTHER Secondary containment upgrade ❑YES ❑NO IF YES.DATE M SOURCE OF DISCHARGE CAUSE(S) ' N ❑ TANK LEAK ® UNKNOWN ❑ OVERFILL ❑ RUPTUREIFAILURE ❑ SPILL ° ❑ PIPING LEAK ❑ OTHER N ❑ CORROSION ® UNKNOWN ❑ OTHER ' CHECK ONLY ONE CL Ww ❑ UNDETERMINED ® SOIL ONLY ❑ GROUNDWATER © DRINKING WATER-(CHECK ONLY IF WATER WELLS HAVE ACTUALLY BEEN AFFECTED) CHECK ONLY ONE ' z N ❑ NO ACTION TAKEN ❑ PRELIMINARY SITE ASSESSMENT WORKPLAN SUBMITTED POLLUTION CHARACTERIZATION ❑ LEAK BEING CONFIRMED ❑ PRELIMINARY SITE ASSESSMENT UNDERWAY ❑ P0S7 CLEANUP MONITORING IN PROGRESS °m ❑ REMEDIATION PLAN ❑ CASE CLOSED(CLEANUP COMPL&EO OR UNNECE GSARY) ❑ CLEANUP UNDERWAY ' CHECK APPROPRIATE ACTIONS) ❑ EXCAVATE d DISPOSE(ED) REMOVE FREE PRODUCT(FP) ❑ ENHANCED BtO pEGRADATION(1T) J=C BACA FOR DETAIL[) 0 0 ❑ CAP SITE(CD) ❑ EXCAVATE&TREAT(ET) ❑ PUMP&TREAT GROUNDWATER(GR) ❑ REPLACE SUPPLY(RS) W F �� ❑ CONTAINMENT BARRIER(CB) ❑ NO ACTION REQUIRED(NA) ❑ TREATMENT AT HOOKUP(HU) ❑ VENT SOIL(VS) ' ❑ VACUUM EXTRACT(VE) ® OTHER TBD Soil sample results from beneath dispensers during secondary containment upgrade activities are as follows:Max,TPH9 In 1,100 mg/kg,Max. Benzene<1:7 mg/kg,Max,MTSE c 0.15 mg/kg,Max.Ethanol c 260 mg/kg. Soil concentrations limited to w just below the dispenser area, L) HAZAI\-. OUS MATERIALS Dl ISION d - " •�, TIME CHARGED . BUSINESS/DEAPRTMENT NAME: w ologo ADDRESS: 3333 U„rto,-J Ai PROJECT DESCRIPTION: P,P-J& af&zA46 c-ca < PROJECT NUMBER: TIME DATE: NAME: CHGD: COMMENTS: 4 wt.. ?C�V*Lj 12CRf2T - baAF-, LT2- GST FrCe MAY 0' 4 7006 W ��lV�-@ �p.'� s 0�� . �b . . r/'� 21 �oG u2 (fPb4ri1E c�22C��cr�1 S� � ccc�sE sass AUG 0 9 1006 � �.� Io 7 � •�.� - GY )S3v GtoS�r.i C.ETT62 .SEP t 4 2006 l' (P.101 T\Tl /l T T/-1T !1/%1 Ar T T TT/N Y. /��1 E R I D August 25,2006 B F/RE IA R TM T Mr.Ray Vose BP West Coast Products,LLC 4 Centerpointe Drive La Palma,CA 90623 RE: No Further Action Required for ARCO AM/PM No. 3090 RONALD J.FRAZE 3333 Union Avenue.in Bakersfield,California FIRE CHIEF Gary Hutton, Dear Mr.Modugno, Senior Deputy Chief Administration This is to inform you that this department has reviewed the Revision to 326-3650 Dispenser Secondary Containment Upgrade Report,dated May 11, 2006,prepared by SECOR International,Incorporated. Based upon the information provided,this Deputy Chief Dean Clason department-has determined that the assessment is complete,and that at this time, no Operations/Training further investigation,remedial or removal action is required in this instance at the 326-3652 above referenced site. Deputy Chief Kirk Blair Fire Safety/Prevention Services Nothing in this determination shall constitute or be construed as a 326-3653 satisfaction or release from liability for any conditions or claims arising as a result of past,current, or future operations at this location. Nothing in this determination 2101 "H"Street is intended or shall be construed to limit the rights of any parties with respect to Bakersfield,CA 93301 claims arising out of or relating to deposit or disposal at any other location of OFFICE: (661)326-3941 substances removed from the site. Nothing in this determination is intended or FAX: (661)852-2170 shall be construed to limit or preclude the Regional Water Quality Control Board or any other agency from taking any further enforcement actions. RALPH E.HUEY,DIRECTOR This letter does not relieve the parties involved of any responsibilities PREVENTION SERVICES mandated under the California Health and Safety Code and California Water Code FIRE SAFETY SERVICES•ENVIRONMENTAL SERVICES if existing, additional,or previously unidentified contamination at the site causes or 900 Truxtun Avenue, Suite 210 Bakersfield,CA 93301 threatens to cause pollution or nuisance or is found to pose a threat to public health OFFICE: (661)326-3979 or water quality. FAX: (661)852-2171 David Weirather If you have any questions regarding this matter,please contact me at(66 1) Fire Plans Examiner 326-3649. 326-3706 Sincerely, Howard H.Wines, III Hazardous Materials Specialist 326-3649 Howard H.Wines,III Hazardous Materials Specialist Professional Geologist No.7239 Office of Environmental Services cc: A.Modugno, SECOR "Searing the Community For9Vlore TfianA Century" SECOR www.secorcom INTERNATIONAL 290 Conejo Ridge Ave.,Suite 200 S .E C OR INCORPORATED Thousand Oaks,California 91361 805-230-1266 TEL 805-230-1277 FAX May 11,2006 Mr. Howard Wines III Bakersfield Fire Department 900 Truxton Avenue, Suite 210 Bakersfield, California 93301 Subject: REVISION TO DISPENSER SECONDARY CONTAE"MNT UPGRADE REPORT ARCO Service Station No. 3090 3333 Union Avenue Bakersfield, California Dear Mr. Wines: SECOR International Incorporated (SECOR), on behalf of the Atlantic Richfield Company (Atlantic Richfield), submitted a Dispenser Secondary Containment Upgrade Report dated January 24, 2006. SECOR has amended page 2 of the report in which the sentence states that SECOR collected soil samples under the direction of Inspector Steve Underwood. SECOR changed the sentence to reflect that the soil sampling was completed under the direction of the BFD Hazardous Materials Specialist Howard Wines. Please replace page 2 of the report with the attached revised page 2. If you have any questions regarding this letter, please do not hesitate to me at(805)230-1266 ext 237 Sincerely, t j0 b SECOR International Incorporated .ate �l b� �'n � c 960L'ON r o a Andrew Modugno ��p�0 a Senior Geologist R.G. 7036 Attachment: page 2 Dispenser Secondary Containment Upgrade Report dated January 24,2006. CC: Ray Vose Dispenser Secondary Containment Upgrade Report Atlantic Richfield Station No. 3090 Bakersfield, California Page 2 DISPENSER REMOVAL AND REPLACEMENT Belshire Environmental Services (Belshire) was contracted by Atlantic Richfield to make all required preliminary notifications, as well as,'remove penetration fittings below the dispensers and replace them with pan entry fittings. The Construction Permit for the replacement of penetration fittings with pan entry fittings is included in Appendix A. The following section summarizes the replacement activities: On December.27, 2005,'Belshire completed the removal of all penetration fittings below the, dispensers and replaced them with P.iciesTM pan entry fittings, as well as replacing both sump 89 and the turbine sumps with fiberglass sumps. The dispenser locations are shown in Figure 2. Pea gravel was removed and re-used and,placed into the'trenches upon completion of the replacement activities. SOIL SAMPLING SECOR collected soil samples under the direction of the BFD Hazardous Materials Specialist Mr. Howard Wines III. Field activities were conducted in accordance with the procedures for soil sampling included in Appendix B. The dispenser sample locations are indicated on Figure 3. This section summarizes the results of the soil sampling activities. Lead Agencies: Bakersfield Fire Department Permit No. MOD-0390 Agency Contact Name: Howard Wines III, Hazardous Materials Specialist (661)326-3649 Number of Dispenser Samples: 8 Dispenser Sample Names: D-1-2; D-1-6, D-2-2, D-2-6, D-3-2, D-3-6, D-4-2, D-4-6, D-5-2, D-5-6, D-6-2, and D-6-6. ANALYTICAL RESULTS All soil samples were relinquished to Del Mar Analytical of Irvine, California (Del Mar) for chemical analysis. Del Mar is an Atlantic Richfield-contracted and California Department of Health Services certified laboratory. SECOR and Del Mar adhered to strict chain-of-custody procedures from sample collection to sample analysis. All soil samples were analyzed in accordance with the appropriate.Environmental Protection Agency(EPA) method and for the following analytes.- • Gasoline Range Organics(GRO C4—C,Z) by EPA Test Method 8260B; and • Benzene, toluene, ethylbenzene, and xylenes (BTEX), disopropyl ether (DIPE), ethyl tertiary-butyl ether (ETBE), tertiary-amyl methyl ether (TAME),, methyl tertiary-butyl ether (MTBE), tertiary-butanol (TBA), and ethanol by EPA.Test Method 8260B. A total of eight soil samples were collected from beneath the dispensers. Detectable concentrations of petroleum hydrocarbon constituents above the laboratory reporting limit (RL) were identified in one of the eight samples. Concentrations qualified by a "J-flag" are estimated values detected at a level below the RL and above the method detection limit (MDL). EPA-certified labs therefore advise that users of these data should be aware that these data'are of unknown quality. Benzene, MTBE, TBA, and ethanol were B E R S F I D RECEIVED MAY 0 ,0. 2006 FIRE ARTM T RONALD J.FRAZE. May 1,2006 FIRE CHIEF Mr.Andrew Modugno,P.G. Gary Hutton, SECOR International,Ilse. Senior Deputy Chief 290 Conejo Ridge Avenue Administration Thousand Oaks,CA 91361 326650 Deputy Chief Dean Chwon Operations/Training RE: ARCO No. 3090,3333 Union Avenue in Bakersfield, CA 326-3652 Dispenser Secondary Containment Upgrade Report Deputy Chief Kirk Blair Fire Safety/Prevention Services 326-3653 Dear.Mr.Modugno, 2101"H„Stmt I have reviewed the above referenced report,dated January 24,2006. Bakersfield,CA 93301 Please amend page 2 of the report,under the Soil Sampling section, OFFICE: (661)326-3941 to show that SECOR collected soil samples under the direction of the FAH: (661)852-2170 BFD Hazardous Materiels Specialist Howard Wines in this instance. RALPH E.HUEY,DIRECTOR Upon receipt of the amended report,I will continue with my intent to PREVENTION.SERVICES issue a no farther action i equired letter in this case. PIRE SAFETY SERVICES•ENVIRONMENTAL SERVICES 900 Tnnctun Avenue,Suite 210 Bakersfteld,CA 93301 If you have any questiorls,please call me at(661)326-3649. OFFICE: (661)326-3979 FAX: (661)852-2171 Sincerely, David Weirather 'RALPH E.HUEY,Director of Prevention Services Fire Plans Examiner 326-3706 Howard H.Wines,ill � w Hazardous Materials Specialist 326-3649 Howard H.Wines, III Hazardous Materials Specialist Professional Geologist NO.' 7239.. reve erviaes Divi ian 1 �� BP West Coast Products LLC 4 Centerpointe Drive La Palma,CA 90623-1066 Mailing Address: writ .x. PO Box 6038 Artesia,CA 90702-6038 Voice (714)670-3958 Fax (714)670-5420 Email Teresa.Milesa-).bp.com January 18, 2006 VIA US MAIL Inspector Stev nderwood ltd Bakersfie ire Department 1715 ester Ave., 3rd Floor ersfield, CA 93301 RE: Arco Facility No. 03090 J 3333 Union Avenue Bakersfield, CA 93305 Dear Mr. Underwood, With this, I am transmitting an Underground Storage Tank Unauthorized Release Report in connection with a incident at the facility noted above. Please feel free to call me at (714) 670- 3958 with any questions. Sincerely, Teresa S. Miles Environmental Compliance Specialist U.S. Convenience Operations TM/cc cc: Central Valley RWQCB (Region 5) Andrew Modugno/SECOR Jack Oman File 3090 DISCLAIMER: This message (including attachments, if any) contains confidential proprietary information, some or all of which may be legally privileged or otherwise protected from unauthorized use, disclosure, distribution or copying. It is for the intended recipient only. If you are not the intended recipient, you may not use, disclose, distribute, copy, print or retain this message or any part of it. If you have received this message in error, please notify us immediately by calling(714)670-5423 collect. UNDERGROUND STORAGE TANK UNAUTHORIZED RELEASE (LEAK) / CONTAMINATION SITE REPORT EMERGENCY ' HAS STATE OFFICE OF EMERGENCY SERVICES FOR4LOCAL AGENCYfUSE ONLY w s t REPORT BEEN FILED? 1 HEREBY CERTIFY THAT I HAVE DISTRIBUTED THIS NFORMATION ACCORDI G TO THE z x —]YES ONO —]YES ONO DISTRIBUTION SHOWN ONsTHE INSTRUCTION SHEET,ONrTHE BACKI PAGE OF THIS FORM REPORT DATE CASE# 0 1 1 8 0 6t .. _ ... a , s M M D 0 V V ..'SIGNED ;f d .;3F"r�, .., SJ,snre¢ . NAME OF INDIVIDUAL FILING REPORT PHONE SIGNATURE m Teresa S. Miles 714-670-3958 W REPRESENTING ®OWNER/OPERATOR ❑ REGIONAL BOARD COMPANY OR AGENCY NAME O ❑LOCAL AGENCY ❑ OTHER BP West Coast Products LLC CL ADDRESS 4 Centerpointe Dr. La Palma CA 90622 STREET CITY STATE ZIP w NAME CONTACT,PERSON PHONE J Z i= BP West Coast Products LLC ❑ UNKNOWN Teresa S. Miles 714-670-3958 O < ADDRESS _ z a 4 Centerpointe Dr. La Palma CA 90622 STREET CITY STATE ZIP FACILITY NAME(IF APPLICABLE) OPERATOR PHONE Z Arco Facilit No.03090 Munther Hawatmeh 661-324-8517 ADDRESS 0 3333 Union Avenue Bakersfield Kern 93305 w STREET CITY COUNTY ZIP ~ CROSS STREET rn 34th LOCAL AGENCY AGENCY NAME CONTACT PERSON PHONE Z Z r, Bakersfield Fire Department Inspector Steve Underwood 661 326-3979 w w REGIONAL BOARD PHONE a.a Central Valley RWQCB (Region 5) (559)445-5116 N (1) NAME QUANTITY LOST(GALLONS) W p ® UNKNOWN y (2) m_ ❑ UNKNOWN Z DATE DISCOVERED HOW DISCOVERED ❑ INVENTORY CONTROL ❑ SUBSURFACE MONITORING ❑ NUISANCE CONDITIONS w0 1 1 2 0 6 [:1 TANK TEST ❑ TANK REMOVAL ® OTHER Secondary containment upgrade H M1 M1 D [)1 V < DATE DISCHARGE BEGAN METHOD USED TO STOP DISCHARGE(CHECK ALL THAT APPLY) M M D D v v UNKNOWN ❑ REMOVE CONTENTS [:1 CLOSE TANK&REMOVE ❑ REPAIR PIPING HAS DISCHARGE BEEN STOPPED? ❑ REPAIR TANK ❑ CLOSE TANK&FILL IN PLACE ❑ CHANGE PROCEDURE p ❑ YES ❑ NO IF YES,DATE M1 M DI Y ❑ REPLACE TANK ® OTHER Secondary containment upgrade SOURCE OF DISCHARGE CAUSE(S) ❑ TANK LEAK ® UNKNOWN ❑ OVERFILL ❑ RUPTURE/FAILURE -1 SPILL U ❑ PIPING LEAK ❑ OTHER ❑ CORROSION ® UNKNOWN ❑ OTHER CHECK ONLY ONE ww L) ❑ UNDETERMINED ® SOIL ONLY F1 GROUNDWATER [:1 DRINKING WATER-(CHECK ONLY IF WATER WELLS HAVE ACTUALLY BEEN AFFECTED) CHECK ONLY ONE Z j ❑ NO ACTION TAKEN ED PRELIMINARY SITE ASSESSMENT WORKPLAN SUBMITTED ® POLLUTION CHARACTERIZATION ❑ LEAK BEING CONFIRMED ❑ PRELIMINARY SITE ASSESSMENT UNDERWAY ❑ POST CLEANUP MONITORING IN PROGRESS U ❑ REMEDIATION PLAN ❑ CASE CLOSED(CLEANUP COMPLETED OR UNNECESSARY) ❑ CLEANUP UNDERWAY CHECK APPROPRIATE ACTION(S) ❑ EXCAVATE&DISPOSE(ED) El REMOVE FREE PRODUCT(FP) [:1 ENHANCED BIO DEGRADATION(IT) J (SEE UCK FOR DETMLS) <Z p O CAP SITE(CD) EXCAVATE&TREAT(ET) PUMP&TREAT GROUNDWATER(GR) ❑ REPLACE SUPPLY(RS) w< ❑ CONTAINMENT BARRIER(CB) ❑ NO ACTION REQUIRED(NA) ❑ TREATMENT AT HOOKUP(HU) [3 VENT SOIL(VS) ❑ VACUUM EXTRACT(VE) ® OTHER TBD Soil sample results from beneath dispensers during secondary containment upgrade activities are as follows: Max.TPHg 1,100 mg/kg, Max. Benzene< 1.7 mg/kg, Max. MTBE <0.15 mg/kg, Max. Ethanol < 260 mg/kg. Soil concentrations limited to Z just below the dispenser area. UJ f f 0 U , 4 December 1'5,2008 B E R S F I D Mr.Roy Sanders F/RE JACO Oil Company A R rM r 3101 State Road Bakersfield,CA 93308 RE: Preliminary Investigation and Evaluation Report for the Fastrip located at 3501 Mt.Vernon,Bakersfield,CA. Dear Mr. Sanders; Ronald J. Fraze ! This is to inform you that this department has reviewed the results of the Fire Chief Site Investigation Report, dated December 2008, prepared by RAM Environmental Engineering Inc.for the above referenced site. Gary Hutton Tyler Hartley Based upon the information provided in the Site Investigation Report, Douglas Greener this department is in concurrence with the recommendation as presented Deputy Chiefs by RAM Environmental Engineering Inc. and it has determined that appropriate actions have been completed, and that at this time, no further investigation, remedial or removal action or monitoring is required at the site. Nothing in this determination shall constitute or be construed as a satisfaction or release from liability for any conditions or claims arising as a result of past, current, or future operations at this location. Nothing HOWARD H.WINES,III in this determination is intended or shall be construed to limit the rights DIRECTOR of any parties with respect to claims arising out of or relating to deposit PREVENTION SERVICES or disposal at any other location of substances removed from the site. Nothing in this determination is intended or shall be construed to limit or 1501 Truxtun Ave. preclude the Regional Water Quality Control Board or any other agency Bakersfield,CA 93301 from taking any further enforcement actions. VOICE: (661)326-3979 FAX: (661)852-2171 This letter does not relieve the parties involved of any responsibilities mandated under the California Health and Safety Code and California Water Code if existing, additional, or previously unidentified contamination at the site causes or threatens to cause pollution or nuisance or is found to pose a threat to public health or water quality. If you have any questions regarding this matter, please contact me at (661)326-3684. Sincerely, Craig Perkins REA Hazardous Materials Specialist cc: M. Jane Ellis-McNaboe, RAM Environmental :�. Jcp v� ., R ENVIRONMENTAL D ENGINEERING SERVICES, INC. November 24, 2008 Mr. Craig Perkins Fire Prevention Officer Bakersfield Fire Prevention Services 1501 Truxtun Avenue Bakersfield, CA 93301 Re: Jaco Oil, lFastrip at 3501 Mt. Vernon Avenue,Bakersfield, Preliminary Investigation and Evaluation Report Dear Mr. Perkins, On behalf of Jaco Oil Company, RAM Environmental Engineering Services, Inc. is pleased to present his Preliminary Investigation and Evaluation Report for the Fastrip service station located at 3501 Mt. Vernon Avenue, Bakersfield. One soil sample collected in May 2008 below a section of product distribution piping that was being replaced indicated a possible gasoline leak. As requested by Bakersfield Fire Department(BFD),three borings were drilled at the site in September 2008. None of the soil samples collected and analyzed from within the borings contained concentrations of chemicals of concern above the EPA recommended action levels, indicting that groundwater below the site is not threatened. RAM recommends that a `no further action required' letter be sent by BFD to Jaco Oil for this site. Please contact RAM at the phone number below if you need any additional information. Regards, M. J Ellis-McNaboe, PG Project Manager (661) 324-6152 cc: Mr. Roy Saunders, Jaco 2103 20th Street o Bakersfield, CA 93301 (661) 324-6152 o FAX (661) 324-6172 _r JACO OIL COMPANY 1 _ I j FASTRIP SELF-SERVE GAS STATION & CONVENIENCE STORE 3501 MT. VERNON AVENUE BAKERSFIELD, CA. � ' PRELIMINARY i INVESTIGATION AND EVALUATION REPORT PROJECT # 200370 NOVEMBER, 2008 f ENVIRONMENTAL i ENGINEERING SERVICES, INC. 2115 201h Street • Bakersfield, CA 93301 (661) 324-6152 • FAX (661) 324-6172 1 ' PRELIMINARY INVESTIGATION AND EVALUATION REPORT ' Jaco Oil Company Fastrip . 3501 Mt. Vernon Avenue Bakersfield, California November 24,2008 Prepared by; RAM Environmental Engineering Services, Inc. ' Project Number 200370 QA/QC ' R:\2000_08070_PIER_3501 Mt.Vemon Ave.doc 2 TABLE OF CONTENTS 1.0 INTRODUCTION..........................................................................................................................4 1.1 RESPONSIBLE PARTY/CONTACT INFORMATION...................................................................4 1.2 SITE HISTORY.......................................................................................................................4 2.0 INVESTIGATION PURPOSE AND SCOPE..............................................................................6. 3.0 SITE DESCRIPTION......................................................................................................................6 3.1 SITE DESCRIPTION...............................................................................................................6 4.0 TOPOGRAPHY,GEOLOGY AND HYDROGEOLOGY.........................................................6 4.1 TOPOGRAPHY......................................................................................................................6 4.2 GEOLOGY.......................................................................................:....................................7 43 HYDROGEOLOGY.... ......**'*'***".:.................................................7 4.4 PAST LEAK, 1994.,...............................................................................................................7 4.5 PUBLIC DRINKING WATER WELLS........................................................................................7 5.0 QUANTITY OF CONTAMINANT RELEASED...........;.............................................................7 6.0 SITE INVESTIGATION..........;.....................................................................................................8 6.1 BORING CLOSURE...............................................................................................................8 6.2 WASTE MANAGEMENT........................................................................................................8 7.0 RESULTS........................................................................................................................................8 8*0 DISCUSSION AND RECOMMENDATIONS.............................................................................9 9.0 LIMITATIONS.............................................................................................................................10 10.0 REFERENCES.................................. ........................................................11 11.0 SIGNATURE PAGE.....................................................................................................................12 FIGURES Figure I Area Map Figure 2 Plot Plan Figure 3 Boring Locations and Analytical Results TABLES Table I Summary Soil Sample Analytical Results ATTACHMENTS Attachment A Copies of BFD Correspondence Attachment B Boring Logs Attachment C Laboratory Reports Attachment D Copies of Non-Hazardous Waste Manifests ' 3501 Mt.Vernon Avenue,Bakersfield RAM Environmental Engineering,Inc. Project#200370 Site Investigation Report ' November 2008' SITE INVESTIGATION REPORT FASTRIP#773,3501 Mt.VERNON AVENUE,BAKERSFIELD, CALIFORNIA 1.0 INTRODUCTION ' RAM Environmental Engineering, Inc. (RAM) is pleased to present this Preliminary Investigation and Evaluation Report (PIER) for the JACO OIL owned Fastrip (# 773) self-serve gas station and convenience store. This gas station is located at ' 3501 Mt. Vernon-Avenue, Bakersfield, California,(Site), (see Figure 1 for an Area Map and Figure 2 for a Plot Plan of the Site). ' This PIER follows the guidelines presented in Appendix A Reports, Tri-Regional Board Staff Recommendations for Preliminary Investigation and Evaluation of Underground Tank Sites (April 2004). 1 1.1 Responsible Party/Contact Information The responsible party for the Site.is JACO OIL. The company contact person is ' Mr. Roy Saunders, 3101!State Rd.,Bakersfield, California,telephone (661) 428- 5761, FAX(661)',393-8738. The consultant contact is RAM Environmental Engineering Services,Inc.,Richard Casagrande or Jane McNaboe, 2115 20`h ' Street, Bakersfield, California, 93301, telephone (661) 324-6152, FAX (661) 324- 6172. ' 1.2 Site History . On May 6, 2008 RAM conducted soil sampling at the Fastri market and gas station located at 3501 Mt. Vernon, Bakersfield, California(Site), as noted in ' Figure 1,Area Map. Soil samples were taken from beneath piping that was being replaced. The sampling was conducted to assess the potential presence of petroleum hydrocarbons in soils beneath former piping at the station as the ' equipment was modified under Bakersfield Fire Department(BFD)Permit to Modify Underground Storage Facility,permit number MD0407. tAn excavation was developed to expose and replace piping leading from the underground storage tanks (USTs)to-ihe dispenser islands, as shown on Figure 3, ' Boring Locations and Analytical Results.- The underlying soils were sands, clays and gravels. Soil samples were taken under the direction of BFD from below the former piping at the ends and in the center of the piping run. The soil samples were collected from between 9 inches and 20 inches below the piping. It was not possible to obtain deeper samples due to the gravel in the soil, and the position of the piping above the UST's. A summary of soil sample analytical results is ' presented in Table.1 following the text, and on Figure 3. R:\2000_08\370_PIER_3501 Mt.Vernon Ave.doc 4 ' 3501 Mt.Vernon Avenue Bakersfield RAM Environmental Engineering,Inc. Project#200370 Site Investigation Report ' November.2008 ' In the'soil sample collected from below the south end of the piping, hydrocarbons were detected in one.sample as follows. ' Sample 1-20"S Soil sample 1-20" S, collected from 20 inches-below the south end of the piping contained significant concentrations of benzene, toluene, ethylbenzene, xylenes ' and TPH-g. The key points of this sample's analytical'results are: 0 the concentration of benzene in the soil, 1,600 gg/Kg, exceeds the ' Preliminary Remediation Goals(PRG, EPA 2004)for industrial soil of 1,400 µg/Kg, • the concentrations of toluene, ethylbenzene, and xylenes did not exceed the ' 2004 PRG values, and 0 the concentration of TPH-g exceeds the LUFT value. No PRG value has been established for gasoline. A Site Investigation Workplan was submitted to BFD b RAM on Jul 18 2008. g p Y Y On August 25, 2008 BFD responded to the Site Investigation Workplan and ' requested a Revised Site Investigation Workplan to include a third boring to define the subsurface hydrocarbon plume. A Revised Site Investigation Workplan was submitted to the BFD on August 28; 2008. This Report presents the results of the Preliminary Site Investigation conducted in ' September 2008. R:\2000_08\370_PIER_3501 Mt.Vemon Ave.doc 5 ' 3501 Mt.Vernon Avenue,Bakersfield RAM Environmental Engineering,Inc. Project#200370 Site Investigation Report November 2008 2.0 INVESTIGATION PURPOSE AND SCOPE ' The objective of the Preliminary Site Investigation was to: • define the vertical and horizontal extent of possible hydrocarbon impacted soils within the proximity of the known pipe leak; ' • obtain certified analytical data on hydrocarbon.concentrations in soil samples; • if groundwater was encountered, collect grab samples for analysis of potential impacts from the fuel leak; • evaluate the-Site Investigation results to determine if further investigation or remediation is necessary; and • present the findings of the Site Investigation.and recommendations to the BFD. ' To meet these objectives the Site Investigation.included the following tasks: J g • sample soils at five-foot intervals from three borings drilled with a hollow-stem auger to evaluate the extent of hydrocarbon containing soils at the Site; • record soil characteristics and field PID measurements in field boring logs; and • . analyze selected soil samples for TPH-g, BTEX; and fuel oxygenates. This Report presents and evaluates the findings of the Preliminary Site Investigation ' conducted on September 24, 2008. 3.0 SITE DESCRIPTION ' 3.1 Site Description Currently,the Jaco Owned Fastrip mini-market and self-serve gas station operate ' on the Site. The gas station distributes gasoline and diesel from 2 dispenser islands with 2 dispensers per island and 3 underground storage tanks(USTs), consisting of one 12,000-gallon regular unleaded gasoline, one 12,000-gallon premium gasoline,.and one 12,000-gallon diesel UST. The service station is located on the northeast corner of the intersection of Mt. Vernon Avenue and University Avenue in Bakersfield, California. Adjacent to the service station to ' the south is a residential area, and to.the north east and west are parking areas associated with the adjacent Bakersfield College. ' 4.0 TOPOGRAPHY,GEOLOGY AND HYDROGEOLOGY 4.1 Topography The Site is at an elevation of approximately 700-feet above sea level. The topography slopes moderately to the southwest(see Figure 1 —Area Map). R:\2000_081370_PIER_3501 Mt.Vemon Ave.doc 6 3501 Mt.Vernon Avenue,Bakersfield RAM Environmental Engineering,Inc. Project#200370 Site Investigation Report November 2008 4.2 Geology The Site is located in the San Joaquin Valley, which is the southern portion of the Great Valley geomorphic province. The Great Valley is a large alluvial plain approximately 50-miles wide and 400-miles long; it is a trough in which sediments have been deposited almost continuously since the Jurassic (about 160 million years ago). Granitic and metamorphic rocks outcrop along most of the eastern and southeastern flanks of the Great Valley, while marine rocks of pre- Tertiary age outcrop along most of the western flank. The post-Eocene-aged continental rocks and deposits in the valley trough contain most of the fresh ' ground water, and are underlain by or contain saline water at depth in most places. They,range in thickness from zero along the flanks,of the Great Valley to more than 15,000 feet in the extreme southern part,where the base of the fresh water ' lies at a maximum depth of about 4,700 feet. The uppermost sedimentary units in the vicinity of,the Site are Quaternary, ' Recent.fan deposits. Subsurface soils at the site are sands containing gravels and cobbles. ' 4.3 Hydrogeology. Groundwater within the southern San Joaquin Valley is derived from rivers . flowing from the`.Sierra Nevada Mountains to the east. The closest-river to the ' Site is the Kern River located approximately 4,700 feet to the northwest. ' There are no surface waters in the immediate Site area. The regional unconfined groundwater at the Site is at approximately 480 feet below ground service(bgs); the groundwater flows to the north(KCWA 2004). ' 4.4 Past leak,.1994 A survey of Leaking Underground Fuel Tank(LUFT) sites in the area on the California State Water Resources web site"GeoTracker" shows that a leak was ' discovered at the Site in 1994. According to Mr. Craig Perkins of the BFD,the leak was a"non-petroleum spill". The case was closed in 1995. ' 4.5 Public drinking water wells The Kern County Water Agency map of Water Wells and Spreading Areas (April ' 2004, Plate 3) shows no water wells in the Site vicinity: 5.0 QUANTITY OF CONTAMINANT RELEASED The'quantity'of contaminant released is unknown. ' R:\2000_08\370_PIER_3501 Mt.Vernon Ave.doc 7 3501 Mt. Vernon Avenue,Bakersfield RAM Environmental Engineering,Inc. Project#200370 Site Investigation Report November 2008 ^ 6.0 SITE INVESTIGATION Three borings were developed at the Site with a hollow-stem auger drilling rig on September 24, 2008. All three borings(Borings B-1,B-2 and B-3)were drilled to 20 feet ' below ground surface (bgs): Soil samples were collected at five-foot intervals and selected soil samples were analyzed as follows: ' • Total petroleum hydrocarbons as.gasoline (TPH-g, carbon range C6-C10)by EPA Method 8015M, ' • Total petroleum hydrocarbons as diesel (TPH-d, carbon range C 1 o-C28) by EPA Method 8015M, ' i Benzene, Toluene, Ethyl-benzene and Xylene (BTEX) by EPA Method 8260B, and • Oxygenates,t-Butanol (TBA) Tert-Butyl Alcohol, Methyl Tert-Butyl Ether (MTBE), Diisopropyl Ether(DIPE), Ethyl Tert=Butyl Ether(ETBE), Tert-Amyl Methyl Ether(TAME), by EPA Method 8260B. 6.1 Boring Closure ' When the total depth'of the boring was reached, as determined in the field from observations,the boring was backfilled with cement grout. The surface was be compacted and covered with asphalt to match existing grade. ' 6.2 Waste.Management Drill cuttings'(soil)generated by drilling soil borings were placed in labeled drums and left on-site. The drum contents were transported by Coles Services under non-hazardous waste manifest to the Coles Services facility located at 1620E. Brundage Lane on October 20, 2008. Please see Attachment D for ' copies of the non-hazardous waste manifests. 7.0 RESULTS Lithologic logs were constructed from each boring, and are included in Attachment-B. Field observations did not indicate the presence of hydrocarbons in any of the borings or soil samples collected. ' To confirm the field observations, analyses were,requested_on the lowermost two soil samples from each boring only. The two deepest soil samples from Boring B-3 contained MTBE at concentrations equal to.or just above the laboratory reporting limit. Analyses were then requested for the shallow soil samples from Boring B-3, the analytical results indicated that there were no chemicals of concern present above the laboratory detection ' limit. A summary of analytical results is shown in Table 1 following the text; complete laboratory reports are included in Attachment C. R:\2000_08\370_PIER_3501 Mt.Vernon Ave.doc 8 ' 3501 Mt.Vernon Avenue,Bakersfield RAM Environmental Engineering,Inc. Project#200370 Site Investigation Report ' November 2008 8.0 DISCUSSION and RECOMMENDATIONS ' Low concentrations of MTBE, 5.7 and 5.0 ug/Kg, were found in two soil samples collected in Boring B-3. The industrial soil screening level guideline established by the US EPA (September.2008) for MTBE is 1,900,000 ug/Kg; the concentration of MTBE found at the Site is well below the soil screening guidelines. No odor or visible staining was noted in any of the borings developed at the Site. ' Based on the following points, RAM recommends that no further action be required at this Site: • The vertical separation between the low concentration of MTBE found in the soil and the underlying groundwater is approximately 450 feet, • the concentrations of MTBE found are well below the soil screening levels established by the.US EPA, • the impacted soils are not located close to a building, and • the impacted soils are,covered by asphalt. t 1 1 . R:\2000_081370_PIER_3501 Mt.Vemon Ave.doc 9 ' 3501 Mt.Vernon Avenue Bakersfield RAM Environmental g En ineerin' g ,Inc. Project#200370 Site Investigation Report ' November 2008 : ' 9.0 LIMITATIONS RAM Environrimental Engineering Services, Inc: has prepared this Preliminary Site Investigation and Evaluation Report for the exclusive use of Jaco Oil Company as it ' pertains to'the property located at 3501 Mt. Vernon Avenue,.in Bakersfield, California. Our professional services have been performed using the degree of care.and skill ordinarily exercised under similar circumstances by other professionals practicing in this ' field. No other warranty, expressed or implied, is made as to the professional advice in the Workplan. Any.use of or reliance on this Report by a third party shall be at such party's sole risk. ' RAM assumes no responsibility for site conditions or activities that were outside the P tY scope of the inquiry requested.by Jaco Oil Company. It is recognized that regulaiory ' requirements may change, including the revision of accepted action levels, which could necessitate a review of the discussion, findings, recommendations or opinions of the Report. 1 1 ' R:\2000_08\370_PIER_3501 Mt.Vernon Ave.doc 10 ' M Environmental En in ri 3501 Mt.Vernon Avenue,Bakersfield RA g ee mg,Inc. Project#200370 Site Investigation Report ' November 2008 10.0 REFERENCES Department of Water Resources(DWR), 1975, California's Ground Water, DWR Bulletin No. 118. ' Kern County Water Agency, 2003 Report on Water Conditions, April 1, 2004. Kern County Environmental Health Services Department. Handbook U.T. 50, Ground- , Water and Vadose Zone Monitoring;Revised February 1993. Appendix A—Reports Tri-Regional Board Staff, Recommendations for Preliminary Investigation and Evaluation of Underground Tank Sites (April 2004). RAM Environmental Engineering Services; Inc., Soil Sampling Report, Fastrip,'3501 Mt. ' Vernon Avenue. June 2008. RAM'Environmental Engineering Services, Inc., Site Investigation Workplan, Fastrip,, ' 3501 Mt. Vern on Avenue. July 2008. RAM Environmental Engineering Services, Inc., Revised Site Investigation Workplan, ' Fastrip, 3501 Mt. Vernon Avenue. August 2008. United States Environmental Protection Agency, Regional Screening Level Table. ' September 2008. http://www.epa.gov/region09/waste/sf md/prg/xls/master sl table run I2SEP2008.xls 1 ' R:\2000_08\370_PIER._3501 Mt.Vernon Ave.doc 1 1 3501 Mt. Vernon Avenue,Bakersfield RAM Environmental Engineering,Inc. .Project#200370 Site Investigation Report ' November 2008 11.0 SIGNATURE PAGE This Site Investigation Report prepared-for Jaco Oil Company, dated November 2008, was prepared by RAM Environmental Engineering Services, Inc. under the responsible charge of the following professional's: y ' or/w M. J e Ellis'McNaboe, PG �\ Q r Project Manager D WRD.3380 t� !ql Richard M. Casagrande HS cy,0 ' President ' R:\2000_08\370_PIER_3501 Mi.Vernon Ave.doc 12 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 FIGURES 1 f • 1 , XMap®4.8 �s°�FIF� �t' JIF� I\• / . � �. b�1 c '�°/Yto ,s (� �-t fa"'- . ( 'fa l�:t•,.°lo' °X�y2" .y� a `03'- o ,f-'�aL:;% �r� ro rtt ° L1ftlr vim. rl•a _ � z _ �° J° e o.,. °s�I / P^\s1 l � ° `..�+ •u °. ,Jc _,,. �... Q..`�—�c�OflcC �a^o.ic° ��`C`--TI /�D t a .I�•.o�. .° ,.° •ytE°� orOWUA.o nii�r a I ° ti.. + • I __ v6 FAST o •�' I I et /' Wit! ', V � \��y C� ,. ° ° f \�`II �_ -f �?. •_�;_,.-.r%°.� �,! •-•.�'�..,;.� •�� ];C�_ �'�iii ~�� � �_ i �✓ mss:ti ra. ''etae.+a: •';I� s Data use subject to license. ©2004 DeLOrtne.XMap®4.5. I 0 8130 1600 2400 3200 400 www.delorme.com MN(0.0'W) Data Zoom 130 JACO OIL COMPANY FIGURE.I RAM ENVIRONMENTAL NOVEMBER 2008 AREA MAP ENGINEERING SERVICES, Project#200370 INC. ' PRELIMINARY INVESTIGATION and 3501 Mount Vernon Avenue 2115 20 10 STREET . EVALUATION REPORT BAKERSFIELD,CA BAKERSFIELD,'CA. ' R:\2000-08\370—PIER—FIG 1 AREA MAP.doc Faztpup9 3601 M. Vernon Avenue - - - - - - - - I � 1 ( .. �` ulti `!I Canopy Market Building o Address Points 1 Roads 04 ;Al I� Arterial h — I Collector Highway Local Kemp Z1 P---- Underground Unpaved u z Y Storage Tanks County of Kern, �II �,. L� �lL I Assessment Parcels Aerial Photography 2006 r UNIVERSITY AV 76 R Feet "07 it 4 �— y LEGEND PRELIMINARY INVESTIGATION RAM and EVALUATION REPORT ENVIRONMENTAL JACO OIL COMPANY ENGINEERING SERVICES, INC. FASTRIP# 773 I\ 3501 Mt. Vernon Avenue F)«1< RE 2 - PILOT PLAN 2008 370 PTERai Fastrip, 3501 Mt. Vernon Avenue L� F �i tr., f � + Canopy Market Building Legend o Address Points N Roads _ i I Arterial Preliminary Analytical = _ _ _ i ^/ collector Results —-- I h/Highway Local Sample I TPH TPHd/MTBE 350;"' y {' "� I ,/Ramp 3-21"NJ ND/ND/ND $ ; r-- ' I Underground 1 //� Unpaved ¢) Storage Sample I TPH TPHd/MTBE ''�� ,r �� Tanks ®County of Kem 2-9"C 1.6/110*/ND Assessment Parcels 1 ' Sample TPHWTPH&MTBE ( Aerial Photography 2006 Sample TPH TPHd/MTBE __ _B-2 B-1 all ND 1-20"S 1,700/61*/ND ' 1 �..e -3 r B-2 all ND _. Sample TPHg/TPHd/MTBE B-3-3 ND/ND/ND _0 38 76 1 B-3-10 ND/ND/ND B-3-15 ND/ND/5.7 Feel' B-3-20 ND/ND/5.0 y A N LEGEND PRELIMINARY Concentration of TPHg/TPHd(mg/Kg)/ INVESTIGATION RAM Sample ID MTBE u C Preliminary soil sample locations, and EVALUATION REPORT ��j ENVIRONMENTAL below pipeline JACO OIL COMPANY �/1-20"S ENGINEERING SERVICES, INC. * The sample chromatographic pattern for TPH does not Boring locations FASTRIP# 773 match the chromatographic pattem of the specified standard. B-1 Boring number 3501 Mt.Vernon Avenue FIGURE 3 -ANALYTICAL RESULTS 2008 370 PIER.ai 1 1 1 1 1 1 � TABLES 1 1 1 1 1 1 1 1 1 1 1 1 TABLE 1 Summary of Soil Sample Analytical Results Jaco Oil Company Fastrip-3501 Mt..Vernon Avenue - � p a Fa- F m u] a o Fm- FQ- UN1TS PPM mg/Kg(PPm) ug/Kg(PPb) EPA ANALYTICAL METHOD 8015B(M) 8260B PRGs(u - ) No PRG value 11400 520,000 400,000 420,000 I: 70,000 No PRG value establised REPORTING•LIMIT Reporting limits vary, lease see laboratory re oft§ o . 1-20"S 0.0 1,700 61^ .1,600 1 76,000 12,000 76,000 I <120 . I <1200 I <250 I <250 I <250 Q .2-9"C 0.0 1.6 I :.110^ _<5.0 <5.0 <5.0 I •<5.0 <5.0 I <50 I <10 I <10 I <10 3-21"N 0.0 I <0.50 I <5:0^ <5.0 I <5.0 <5.0 <5.0 I <5.0 I <50 I <10 <10 I <10 B-1-5• - 0.0 NA I NA- NA NA NA NA NA I NA NA NA I NA I NA 13-140 0.0 NA NA - NA NA NA NA NA - NA NA NA I NA I NA B-1-15 0.0'- <0.50 I <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 I <50 <10 I <10 I <10 c B-1-20 0.0 <0.50 <5.0 <5.0 <5.0 <5-.0 .<5.0 <5.0• <5.0 <50 .� _ <10 <10 I. <10 B-2-5 0.0 NA I NA NA NA NA NA I NA NA ,I NA I NA NA NA - N B-2-10 0.0" NA ( NA I NA NA I NA NA I NA NA I NA I NA I NA I NA B-2=15 0.0 <0.50 <5.0 I <5.0 <5.0 I <5.0 I <5.0 <5.0 I <5.0 <50 <10 <10 <10 B-2-20 0.0 <0.50 <5.0 I <5.0 -I <5.0 I <5.0 <5.0 I <5.0 I <5.0 I <50 <10 I <10 I <10 a v, B-3-5 0.0 <0.50,-1 <5.0 1 <5.0 1 <5.0 <5.0 I <5.0 1 <5.0 I <5.0 1 <50 I <10 I <10 <10 .13-3-10 0.0 <0.50 <5.0: <5.0 <5.0 <5.0 <5.0 I <5.0 1 <5.0 1 <50 1 <10 ' 1 <10 I <10 B-3-15 0.0 <0.50 I <5.0 _ <5.0 <5.0 <5.0 <5.0 �. <5.0 5.7 <50 <10 <10 I <10 B-3-20 = 0.0 <0.50. <5.0 <5:0 <5.0 <5:0 , <5.0 ._I <5.0 5.0 <50 <10 <10 <10 Sample Number-Boring number-depth below ground surface in feet or inches where shown. TPH-Total Petroleum Hydrocarbons '-There is no PRG for TPH as gasoline. <5.0-compound was not detected in the sample extract at the laboratory detection limit shown. mg(Kg-milligrams per kilogram u -micrograms per kilogram NA-not analyzed ^-The sample chromatographic pattern for TPH does not match the chromatographic pattern of the specified standard.-Quantitation of the unknown hydrocarbon(s)i the sample was based upon the specified standard. R:\2000_08\370_SI workplan lab results table.xls Attachment A ' COPY of BFD CORRESPONDENCE 1 1 1 1 1 1 1 1 1 COB 8/25/2008 'L0:24 :53 AM PACE 3/003 Fax Server B A'_.ICf FIRE 'FA R MEN T August 25, 2078 1 Roy Sanders JA�O Oii Company ' Ronald J. Froze 3101 State Road Fire Chief Bakersfield, Ca 93308 ' G ary Hutton RE: Work plan modifications for 3501 Mount Vernon Ave, Bakersfield, Ca. Tyler Hartley Douglas Greener Deputy Chiefs Dear.Roy Saunders: Upon.review of the recently submitted work plan for your facility, this office has ' determined ;teat the extent of thG contamination' plume will not be, fully defined without an additional bore hole. This boring should be located southwest of bore HOWARD H.WIi�tIv5,III hole# 2 and maintain the same standards for vertical extension as proposed in the ' DIRECTOR Work plan of Jury 2408, PREVENTION This office requires (in accordance with Chapter 6,7 of the California Health and SERVICES S Safety Code and Chapter 16, Title 23 of the California Code of Regulations) that ' ISQI Truxtun av°.,I'Fltc: further assessment be done to define the vertical and horizontal extant of the Bakersfield,CA 93301 contarr ination plume. VOICE: (661)326-3979 ' FAX (661)352-71711 Please submit the revised work plan for further assessment, tc this office, within, 30 days from receipt of this letter. The work plan should follow guidelines found in: Appendix A-Reports. Th -Reaiotial Board Staff Recommendations for Preliminaa �vatuation and lnvestigation of Underground Tank Sites;April 16, 2004. ' Additionally, be advised that oversight cost for this project will be billed to you at a rate of$112.00 per hour. If you have any questions; please call me at(661) 326-3979. Sincerely, f Craig erkins REA-1 ' Fire Prevention/Environmental Officer CC: M. Jane Ellis-McNaboe, F:W E,nvironrnental 1 ' B E R S F I D FIRE R IrAI T June 17, 2008 ' Roy Sanders JACO Oil Company Ronald J. Fraze 3101 State Road Fire Chief Bakersfield, Ca 93308 Gary Hutton RE: Laboratory results from preliminary site assessment conducted at 3501 ' Tyler Hartley Mount Vernon Ave, Bakersfield, Ca. Permit# MD 0407 Douglas Greener Deputy Chiefs Dear Roy Saunders: ' Upon review of the recently submitted laboratory results from your facility, this office has determined that the extent of the contamination plume, associated with sample HOWARD H.WINES,III 1-20"S (the southern most bore sample), has,not been adequately defined. ' DIRECTOR This office'requires (in accordance with Chapter 6.7 of the California Health and PREVENTION Safety Code and Chapter 16, Title 23 of the California Code of Regulations) that SERVICES further assessment be done to define the vertical and horizontal extent of the ' 1501 Truxtun Ave., I'Floor contamination plume. Bakersfield,CA 93301 VOICE: (661)326-3979 Please submit a work plan for further assessment, to this office, within 30 days from FAX: (661)852-2171 receipt of this letter. The work plan should follow guidelines found in: Appendix A- ' Reports. Tri - Regional Board Staff Recommendations for Preliminary evaluation and Investigation of Underground Tank'Sites; April 16, 2004. ' Additionally, be advised that oversight cost for this project will be billed to you at a rate of$112.00 per hour. , tIf you have any questions, please call meat (661) 326-3979. Sincerely, Craig Perkins REA-1 Fire Prevention /Environmental Officer CC: M. Jane Ellis-McNaboe, RAM Environmental 1 1 1 1 1 Attachment B BORING LOGS 1 1 1 1 1 1 1 1 1 1 1 1 1 ' SAMPLE CLIENT:Jaco,RAM Project No.200370 ° BOREHOLE PROJECT:Preliminary Site Investigation n COMPLETION LOCATION: 3501 Mt.Vernon Ave.,Bakersfield :� E v B-1 ' Q ~ ! DESCRIPTION AND SOIL CLASSIFICATION NAME: 0- 0 j o a %gravel/sand/fines,gradation/.plasticity,color angularity; w a t°. _"diameter Casing 41J E a. maximum size(gravels),,denisty/consistency,moiture,odor, O U J h?- N 0 stain. m ? 0 ASPHALT 6 inches thick 0' GRAVEL,20/80/0,light brown,with course grained 00 w sand. Gravels and cobbles to 3 inches, rounded, GW o° ' loose no odor,no stain. C3 5 SAND, 10/90/0,light brouwn,loose, no odor, no stain r °:' '; 5 0 2/1/1 1.9 m o s o 0 0 10 10 SAND and GRAVEL,20/80/0,light brown, loose, 0/4/10 0.0 yak o rounded cobbles of decomposed granite,no odor,no SW/G o k stain a °'. E ° LO d 0 15 as above 50/50/0,increasing gravels 13116126 0.0 d3 O t 15 -A, m o o z ° 20 20 SANDY CLAY, 10/40/50,grey,plastic,no odor,no 38./50 0.0 Y stain. Underlain by decomposed granite,white,no odor, no stain ' 25 25 30 30 1 35 35 40 40 ' 45 45 ' 50 50 ' DRILLING METHOD:Hollow Stem Auger DA E I D:9/24/2509 SAMPLER TYPE:Split spoon LOGGED BY:J.Ellis-McNaboe,PG TOTAL BORING DEPTH:20-feet APPROVED BY: ' No groundwater encountered. DRILLED BY:Gonsolidated Testing,David Lopez LOG OF EXPLORATORY RAM ENVIRONMENTAL B-1 BORING ENGINEERING SERVICES, INC. Page_1_of_1_ RA2000_08\370_PIER_lith log&1 0-50 1 ' SAMPLE CLIENT:Jaco,RAM Project No.200370 BOREHOLE u• PROJECT:Preliminary Site Investigation a COMPLETION LOCATION: 3501 Mt.Vernon Ave.,Bakersfield E U) c� B-2 t U Q H � DESCRIPTION AND SOIL CLASSIFICATION NAME: a m 0 j o d 2 %gravel/sand/fines,gradation/plasticity,color angularity, N w a o o H Y _"diameter casing F E a maximum size(gravels),denisty/consistency,moiture,odor, O U Z slain. m Z J 0 ASPHALT, 6 inches thick 0 SAND,0/100/0,red,fill material. SW 3 v large gravels at 3 feet. GW 6 °A? v' SAND,CLAY,GRAVEL, 10/80/10,light brouwn, x ° 5 loose,dry,no odor,no stain won 0.0 SW/GW :::b:.:. 5 0 . o ' r . Q � o 10 v. 10 difficulty with sampling due to rock,grabbed sample SWIGW a:: 0 E ' from cuttings,sand with clay. a:: n 0 E 0 Nr d 15 SAND,30/70/0,gravelly sand,grey,loose,no odor, 12/50 0.0 a::a: t 15 ' no stain (D o Z N 20 13/50 0.0 1 20 ' SAND,GRAVEL,CLAY,30/40/30,gray, DG decomposed granite,no odor,no stain •, 25 25 ' 30 30 ' 35 35 40 40 45 45 50 50 1 DRILLING METHOD:Hollow Stem Auger - DATE DRILLED:9/24/2008 SAMPLER TYPE:Split spoon LOGGED BY:J.Ellis-McNaboe,PG ' TOTAL BORING DEPTH:20-feet APPROVED BY: DEPTH TO WATER: No grou n wa er encountered. onso i a e es m avi o ez LOG OF EXPLORATORY RAM ENVIRONMENTAL B-2 ' BORING ENGINEERING SERVICES, INC. Page-1—of-1— ' R:\2000_08\370_PIER_lith Iog.xlsB-2 0-50 ' SAMPLE CLIENT:Jaco,RAM Project No.200370 BOREHOLE PROJECT:Preliminary Site Investigation a COMPLETION T LOCATION: 3501 Mt.Vemon Ave.,Bakersfield E U) B-3 or U DESCRIPTION AND SOIL CLASSIFICATION NAME: m o,; o _ graveUsandlfines,gradation)plasticity,color angularity, W n. o a H 3= Y _"diameter casing W E a maximum size(gravels),denisty/consistency,moiture,odor, O _ Z i'5 WW stain. m Z J 0 ASPHALT, 6 inches thick 0 SAND,0/100/0,red,fill material. SW GRAVELLY SAND,30170/10,yellow-brown,loose, ' dry,cobbles to 4 inches,no odor,no stain. Ad rn 5 as above 21150 0.0 Sw/GW a:.:. m 5 o sandier r ap y � N 10 °:::: 10 as above,light yellow 38/50 0.0 �::o:: ` d SW/GW o_ E a E d U O 15 SAND,30170/0,gravelly sand,grey,loose,no odor, 17/50 0.0 a::a: t 15 ' no stain >: m a Z Cq ch 20 21/50 0.0 20 as above,large rock in core barrel,6"recovery. 1 25 25 ' 30 30 35 35 ' 40 40 1 45 45 50 50 DRILLING METHOD:Hollow Stem Auger DATE DRILLED:9/24/2008 SAMPLER TYPE:Split spoon LOGGED BY:J.Ellis-McNaboe,PG ' TOTAL BORING DEPTH:20-feet APPROVED BY: No groundwater encoun ere . DRILLED BY:Gonsolidated Testing, avi o ez LOG OF EXPLORATORY RAM ENVIRONMENTAL B-3 ' BORING ENGINEERING SERVICES,.INC. Paget_of_1_ ' R:\2000-08\370—PIER—lith Iog.xlsB-3 0 1 1 1 1 Attachment C � LAaOaArokr REPORTS 1 1 1 1 1 1 1 1 1 1 1 1 1 Page 1 of 18 aiscience ' A,_nvironmental a A6 aboratories, Inc. 1 ' October 03, 2008 ' Jane MCNaboe RAM Environmental Engineering Services, Inc. 2115 20th Street ' Bakersfield, CA 93301•-3710 ' Subject: Calscience Work Order No.: 08-09-2430 Client Reference: Jaco Soil Sampling. 200370. Mt. Vernon Ave. Dear Client: Enclosed is an analytical report for the above-referenced project. The samples ' included in this report were received 9/26/2008 and analyzed in accordance with the attached chain-of-custody. ' Unless otherwise noted, all analytical testing was accomplished in accordance with the guidelines established in our.Quality Systems Manual, applicable standard operating procedures, and other related documentation. The original report of subcontracted analysis, if any, is provided herein, and follows the standard Calscience data package. The results in this analytical report are limited to the samples tested and any reproduction thereof must be.made in its entirety. ' If you have any questions regarding this report, please do not hesitate to contact the undersigned. Sincerely, Calscience Environmental Laboratories, Inc. ' Don Burley Project Manager ' CA-FLAP ID: 1230 NELAP ID: 03220CA CSDLAC ID: 10109 SCAQMD ID: 93LA0830 ' 7440 Lincoln Way, Garden Grove, CA 92841-1427 • TEL:(714)895-5494 FAX: (714) 894-7501 ' Page 2 of 18 a/science Aw nvironmental Analytical Report L aboratories, Inc. - 1 - RAM Environmental Engineering Services, Inc. Date Received: 09/26/08 ' 21.15 20th Street Work Order No: 08-09-2430 Bakersfield; CA 93301-3710 Preparation: EPA 3550B Method: EPA 80158 (M) ' Project: Jaco Soil Sampling: 200370. Mt. Vernon Ave. Page 1.of 2 Lab Sample Daterrime Date Datefrime ' Client Sample Number Number Collected Matrix Instrument Prepared Analyzed QC Batch ID B-1-15 08-09-2430-0-A 09/24/08 : Solid GC 27 09/29/08 09/30/08 080929B08 09:51 : t 21:18 ' Parameter Result RL DF Qual Uni TPH as Diesel ND 5.0 1 mg/kg ' Surroaates: REC °° Control Limits Qual Decachlorobiphenyl 110 61-145 a B 1-20 08-09 24304-A 010 02a Solid. GC 09128 "k •' " � 108 ` 0,921,0378 080929B08 ' s sfi ' Parameter Result RL DF Qual Uni s TPH as Diesel ND 5.0 1 mg/kg ' Surroaates: REC °° Control Limits ual Decachlorobiphenyl 101 61-145 B 2=15 08-092430 7-A X09/24/08 Solid GC 27 = 09/29/08 ► 8 X080929608. ' 09/30 0 t, 11 14. 21:57 Parameter Result RL DF Qual Units ' TPH as Diesel ND 5.0 1 mg/kg Surrogates: REC(%) Control Limits Qual ' Decachlorobiphenyl 105 61-145 B-2-20• 08-09-2430-8-A 08/24/08 Solid GC 27 09129108.,, 09/30/08 0809291308 ' 11.20_ 10:15. Parameter Result RL DF Qual Units ' TPH as Diesel ND 5.0 1 mg/kg Surroaates: REC M Control Limits Qual Decachlorobiphenyl 109 61-145 RL-Reporting Limit DF-Dilution Factor Qual-Qualifiers 7440 Lincoln Way, Garden Grove, CA 92841-1427 - TEL:(714) 895-5494 FAX: (714) 894-7501 ' Page 3 of 18 Q.,=!/science =nvironmental Analytical Report aboratories,-Inc. 1 RAM Environmental Engineering Services, Inc. Date Received: 09/26/08 ' 2115 20th Street Work Order No: 08-09-2430 Bakersfield, CA 93301-3710 Preparation: EPA 35508 Method: EPA 8015B (M) ' Project: Jaco Soil Sampling. 200370. Mt.Vernon Ave. Page 2 of 2 Lab Sample Date/Time Date Date/Time ' Client Sample Number Number Collected Matrix Instrument Prepared Analyzed .QC Batch ID B3-15 08-09-2430-11-A 09/24/08 Solid GC 27 09/29/08 09/30/08 .'080929608 13:01 10:34 ' ' Paramete Result RL DF Qu ll Units TPH as Diesel ND 5.0 1 mg/kg ' Surrogates: REC(%) Control Limits Qual Decachlorobiphenyl 110 61-145 0108 B:3=20 08-08 2430 12 A �13�28 Solid GC>27 09/29/08 0110:53 080929B08' h Parameter Resul RL DF Qual Units TPH as Diesel ND 5.0 1 mg/kg ' Surrogates: REC(%) Control Limits Qual Decachlorobiphenyl 104 61-145 Method?Blank k s "'099 12 2Z5 2,189 , MIA. Solid GC 27 09/29/08 09/30/08 +080929808` ••.. .•5v nvr.a 3o. +. .+„.kp'mu.�'£t..3.n _.-.i/�.ata ? 19:45 Parameter Result RL DF Qual Units TPH as Diesel ND 5.0 1 mg/kg Surrogates: REC(%) Control Limits Qual ' Decachlorobiphenyl 111 61-145 1 ' RL-Reporting Limit DF-Dilution Factor Qual-Qualifiers 7440 Lincoln Way, Garden Grove, CA 92841-1427 TEL:(714) 895-5494 FAX: (714) 894-7501 ' Page 4 of.18, alscience v=nvironmental Analytical Report. �. aboratories, Inca ' RAM Environmental Engineering Services, Inc. Date Received: 09/26/08 ' 2115 20th Street Work Order No. 08-09-2430 Bakersfield,'CA 93301-3710 Preparation: EPA 5030B Method: EPA 8015B (M) Project: .Jaco Soil Sampling. 200370. Mt:•Vernon Ave. . Page 1 of 2 Lab Sample Datefrime Date Datefrime ' Client Sample Number Number Collected Matrix Instrument Prepared Analyzed QC Batch ID B-1-16 08-69-2430-34 09124108 Solld GC 1 .09129108 09129198'*: 080929601 09.61 22:46 A ' Parameter Result RL DFl Uni TPH as Gasoline ND 0.50 1 mg/kg Surrogates: REC(%) Control Limits Qual 1,4-Bromofluorobenzene-FID 82 42-126 B 1-20 08-09 2430-4-A 09124108 Solld GC 1. X09/29/08 09/29108 080929601 10 02, Parameter Result RL DF Qual Units TPH as Gasoline ND 0.50 1 mg/kg ' Surrogates: REC(%) Control Limits Qual 1,4-Bromofluorobenzene-FID 81 42-126 c �g�2=76 g ',08-09-2430-74, �10111 148 �4Solld GC 1s , 09/29/08 ,09/29/08 480929801 23:17 Parameter Result RL DF Qual Units TPH as Gasoline ND 0.50 1 mg/kg Surrogates: REC(%) Control Limits Qual 1,4-Bromofluorobenzene-FID 81 42-126 B-z-20 08-09,2430-8 A'.. 011 20.8 Solld°. GC 1 09/29]08 09/29/008' 080 929BOT ' Parameter Result RL DF Qual Units TPH as Gasoline ND 0.50 1 mg/kg Surrogates: REC(%) Control Limits Qual ' 1,4-Bromofluorobenzene-FID 80 42-126 RL-Reporting Limit DF-Dilution Factor Qua[-Qualifiers 7440 Lincoln Way, Garden Grove, CA 92841-1427 TEL:(714) 895-5494 FAX: (714) 894-7501 ' Page 5 of 18 alscience AN=nvironmental Analytical Report t. A aboratories, Inc. RAM Environmental Engineering Services, Inc. Date Received: 09/26/08 ' 2115 20th Street Work Order No: 08-09-2430 Bakersfield, CA 93301-371.0 Preparation: EPA 50306 Method: EPA 8015B (M) ' Project Jaco Soil Sampling. 200370. Mt. Vernon Ave. Page 2 of 2• Lab Sample Datelrime Date Datelrime ' Client Sample Number Number Collected Matrix Instrument Prepared Analyzed QC Batch ID B-3-16 '08-09-2430-11-A 09/24/08 Solid GC 1 09/29108 09/30/08 080929801 13:01 00:20 ' Parameter Result Rl DF Q au I uafta TPH as Gasoline ND 0.50 1 mg/kg Surrogates: REC °o Control Limits Qual 1,4-Bromofluorobenzene-FID 81 42-126 B`-3=20 08-09`2430 12 A 09/24/08 Solid GC 1 09/29/08 080929601 0913 0 00:63 3. ' Parameter Result RL DF Qual Units TPH as Gasoline ND 0.50 1 mg/kg ' Surrogates: REC(%) Control Limits Qual 1,4-Bromofluorobenzene-FID 82 42-126 M @ttt'o d Blank n 29108 09/28/08 080929601' sW 19:00 k 099 12 279 2 278 NIA Solid GC 1, 091 Parameter Result R DF Qual Units ' TPH as Gasoline ND 0.50 1 mg/kg Surrogates: REC(%) _Control Limits Qual ' 1,4-Bromofluorobenzene-FID 81 42-126 • ' RL-Reporting Limit DF-Dilution Factor Qual-Qualifiers 7440 Lincoln Way, Garden Grove, CA 92841-1427 TEL:(714) 895-5494 FAX: (714) 894-7501 ' Page 6 of 18 & a/science �=nvironmental Analytical Report �. aboratories, Inc. . ''` 1 RAM Environmental Engineering Services, Inc. Date Received: 09/26/08 2115 20th Street Work Order No: 08-09-2430 ' Bakersfield, CA 93301-3710 Preparation: EPA 5030B Method: EPA 8260B ' Units: ug/kg Project: Jaco Soil.Sampling. 200370.Mt. Vernon Ave. Page 1 of 3 Lab Sample Date/Time Matrix Instrument Date Datelrime ' Client Sample Number Number Collected Prepared Analyzed QC Batch.ID B-1-16 08-09 24303-A 09/24/08 Solid GC/MS,EE 09/26/08.,: 09/27/08 .080928L03, 09:51 03:19 . Parameter Resul RL DF Qual Parameter Result RL DF Qual Benzene ND 5.0 1 Methyl-t-Butyl Ether(MTBE) ND 5.0 1 Ethylbenzene ND 5.0 1 Tert-Butyl Alcohol(TBA) ND 50 1 Toluene ND 5.0 1 Diisopropyl Ether(DIPE) ND 10 1 ' p/m-Xylene ND 5.0 1 Ethy.14-Butyl Ether(ETBE) ND 10 1 o-Xylene ND 5.0 1 Tert-Amyl-Methyl Ether(TAME) ND 10 1 Surrogates: REC(%1 Control Qual Surrogates: REC °o Control Qual Limits Limi Dibromofluoromethane 111 73-139 1 2 Dichlorcethane-d4 119 73-145 Toluene-d8 100 90-108 1 4 Bromofluorobenzene 90 71-113 ' - ' '09127/08 .080926L03 13-1-20 �� .•: X08-09 2430�;A 09/24/08 Solid GC/MS EE� 09/28/08 t -10:02 ,Ob 2 a Parameter Result RL DF Qual Parameter Result RL DF Qual Benzene ND 5.0 1 Methyl-t-Butyl Ether(MTBE) ND 5.0 1 Ethylbenzene ND 5.0 1 Tert-Butyl Alcohol(TBA) ND 50 1 ' Toluene ND 5.0. 1 Diisopropyl Ether(DIPE) ND 10 1 p/m-Xylene ND 5.0 1 Ethyl-t-Butyl Ether(ETBE) ND 10 • 1 o-Xylene ND 5.0 1 Tert=Amyl=Methyl Ether(TAME) ND 10 1 Surrogates: REC °o Control Qual Surrogates: RE °o Control Qual Liflik Lim is Dibromofluoromethane '111 73-139 1,2-Dichlorcethane-d4 118 73-145 Toluene-08 100 90-108 1,4-Bromofluorobenzene 89 71-113 B-2=1ti . 0 -0'� .�24�°'" '11:14 .0,/MS S. � �9/a2xe 6/0` 3 f p L Parameter Result RL DF Qual Parameter Result RL DF Qual Benzene ND r5.0 1 Methyl-t-Butyl Ether(MTBE) ND 5.0 1 ' Ethylbenzene ND 5.0 1 Tert-Butyl Alcohol(TBA) ND 50 1 Toluene ND 5.0 1 Diisopropyl Ether(DIPE) ND 10 1 p/m-Xylene ND 5.0 1 Ethyl-t-Butyl Ether(ETBE) ND 10 1 o-Xylene ND 5.0 1 Tert-Amyl-Methyl Ether(TAME) ND 10 1 ' Surrogates: REC °o Control Qual Surrogates: REC °o Control Qual i i s Limits Dibromofluoromethane 110 73-139 1,2-Dichloroethane-l4 123 73-145 Toluene-d8 101 90-108 1,4-Bromofluorobenzene 88 71-113 ' RL-Reporting Limit DF-Dilution Factor Qual-Qualifiers 7440 Lincoln Way, Garden Grove, CA 92841-1427 TEL:(714) 895-5494 • FAX: (714) 894-7501 ' Page 7 of 18 L Science Aw nvironmental Analytical Report aboratories, Inc. RAM Environmental Engineering Services, Inc. Date Received: 09/26/08 2115 20th Street . Work Order No: 08-09-2430 Bakersfield, CA 93301-3710 Preparation: EPA 5030B Method: EPA 8260B ' Units: ug/kg Project: Jaco Soil Sampling. 200370. Mt. Vernon Ave. Page 2 of 3 Lab Sample Date/Time Date Date/rime ' Client Sample Number Number Collected Matrix Instrument Prepared Analyzed QC Batch ID B-2-20 08-09-2430-8-A 09/24/08 Solld GC/MS EE 09/26/08 09/27/08 0810926L03 11:20 06:32 Parameter Result RL DF Qual Parameter Result RL DF Qual Benzene ND 5.0 1 Methyl-t-Butyl Ether(MTBE) ND 5.0 1 Ethylbenzene ND 5.0 1 Tert-Butyl Alcohol(TBA). ND 50 1 Toluene ND 5.0 1 Diisopropyl Ether(DIPE) ND 10 1 ' p/m-Xylene ND 5.0 1 Ethyl-t-Butyl Ether(ETBE) ND 10 • 1 o-Xylene ND 5.0 1 Tert-Amyl-Methyl Ether(TAME), ND 10 1 Surrogates: REC °° Control Qual Surrogates: REC(%) Control Qual L i s Lbih ' Dibromofluoromethane 116 73-139 1,2 Dichloroethane-d4 128 73-145 Toluene-08 101 90-108 1,4 Bromofluorobenzene 88 71-113 8=3=16 09/24/08, a daS61Id ,GC/MS,EE 09/26/08 09/27/08 N,y s080926L03 Parameter Result RL DF Qual Parameter Result RL DF Qual Benzene ND 5.0 1 Methyl-t-Butyl Ether(MTBE) 5.7 5.0 1 Ethylbenzene ND 5:0 1 Tert-Butyl Alcohol(TBA) ND 50 1 ' Toluene ND 5.0 1 Diisopropyl Ether(DIPE) ND 10 1 p/m-Xylene ND 5.0 1 Ethyl-t-Butyl Ether(ETBE) ND 10 1 o-Xylene ND 5.0 1 Tert-Amyl-Methyl Ether(TAME) ND 10 1 Surrogates: REC(%) Control Qual Surrogates: REC(%) Control Qual i i s -1 Dibromofluoromethane 116 73-139 1,2-Dichlorcethane-d4 124 73 45 Toluene-d8 99 90-108 1,4-Bromofluorobenzene 89 71-113 B-3=20 08-09-2430 12 A . .'09124108 ,? Solld GC/MS EE 09/26/08 09/27/08= 080926L03 Parameter .,.Re,u- RL . D,._ r_�.. .. .,.,...,�.• , a.J:. ,�x�'".., F Qual Parameter Result RL DF Clual Benzene ND 5.0 1 Methyl-t-Butyl Ether(MTBE) 5.0 5.0 1 Ethylbenzene ND 5.0 1 Tert-Butyl Alcohol(TBA) ND 50 1 Toluene ND 5.0 1 Diisopropyl Ether(DIPE) ND 10 1 p/m-Xylene ND 5.0 1 Ethyl-t-Butyl Ether(ETBE) ND 10 1 o-Xylene ND. 5.6 1 Tert-Amyl-Methyl Ether(TAME) ND 10 1 ' Surrogates: REC(%) Control Qual Surrogates: REC(%) Control Qual Lirmb Lblik Dibromofluoromethane 116 73-139 1,2-Dichlorcethane-d4 125 73-145 Toluene-d8 101 90-108 1,4-Bromofluorobenzene 89 71-113 ' RL-Reporting Limit DF-Dilution Factor Qual-Qualifiers 7440 Lincoln Way, Garden Grove, CA 92841-1427 - TEL:(714) 895-5494 - FAX: (714) 894-7501 ' Page 8 of 18 & !/science �=nvironmental Analytical Report aboratories, Inc. RAM Environmental Engineering Services, Inc. Date Received: 09/26/08 ' 2115 20th Street - Work Order No: 08-09-2430 Bakersfield, CA 93301-3710 Preparation: EPA 5030B Method: EPA 8260B Units: ug/kg ' Project: Jaco Soil Sampling. 200370. Mt. Vernon Ave. Page 3 of 3 Lab Sample Date rime Matrix Instrument Date Datefrime ' Client Sample Number Number Collected Prepared Analyzed QC Batch ID Method Blank 099-12-796-187 N/A Solid GC/MS EE 09/26/08 09/27/08 08092SL03 02:15 Parameter Result $L DF Qual Parameter Result RL DF Qual Benzene ND 5.0 1 Methyl-t-Butyl Ether(MTBE) ND 5.0 1 Ethylbenzene ND 5.0 1 Tert-Butyl Alcohol(TBA) ND 50 1 Toluene ND 5.0 1 Diisopropyl Ether(DIPE) ND 10 1 ' p/m-Xylene ND 5.0 1 Ethyl-t-Butyl Ether(ETBE) ND 10 1 o-Xylene ND 5.0 1 Tert-Amyl-Methyl Ether(TAME) ND 10 1 SUrrogatM REC(%) Control Qual Surrogates: REC(%) Control Qual i i Li i Dibromofluoromethane 104 73-139 1,2-Dichloroethane-d4 113 73-145 Toluene-d8 99 90-108 1,4-Bromofluorobenzene 89 71-113 1 RL-Reporting Limit DF.-Dilution Factor Qual-Qualifiers 7440 Lincoln Way, Garden Grove, CA 92841-1427 TEL:(714) 895-5494 FAX: (714) 894-7501 ' Page 9 of 18 alscience nv►ronmental Quality Control - Spike/Spike Duplicate ' aboratories, Inc. ' RAM Environmental Engineering Services, Inc. Date Received: 09/26/08 ' 2115 20th Street Work Order No: 08-09-2430 Bakersfield, CA 93301-3710 Preparation: EPA 3550B Method: EPA 8015B (M) ' Proiect Jaco Soil Sampling. 200370. Mt. Vernon Ave. Date Date MS/MSD Batch Quality Control Sample ID Matrix Instrument Prepared Analyzed Number 8-1 4 Solid GC 27 08/29/08 09/30108 080929S08 ' Parameter MS%REC MSD%REC %REC CL RPD RPD CL Qualifiers ' TPH as Diesel 92 90 64-130 2 0-15 1 1 ' t , 1 1 , ' RPD-Relative Percent Difference; CL-Control Limit 7440 Lincoln Way;Garden Grove, CA 92841-1427 . TEL:(714) 895-5494 FAX: (714) 894-7501 ' Page 10 of 18 alscience nvironmental Quality Con_ trol -Spike/Spike Duplicate Aw aboratories, Inc. RAM Environmental Engineering Services, Inc. ' Date Received: 09/26/08 ' 2115 20th Street Work Order No: 08-09-2430 Bakersfield, CA 93301-3710 Preparation: EPA 5030B Method: EPA 8015B (M) ' Pro'ect Jaco Soil Sampling. 200370. Mt. Vernon Ave. I ' Date Date MS/MSD Batch Quality Control Sample ID Matrix Instrument Prepared Analyzed Number rB-1-20 Solid ;;'GC 1 09129108.; 09129/08'. 080929S01 ' Parameter MS%REC MSD%REC %REC CL RPD RPD CL, Qualifiers ' TPH as Gasoline 109 108 48-114 0 0-23 1 1 1 1 • ' RPD-Relative Percent Difference, CL-Control Limit 7440 Lincoln Way, Garden Grove, CA 92841-1427 . TEL:(714) 895-5494 FAX: (714) 894-7501 ' Page 11 of 18 ' aiscience nvironmental Quality Control - Spike/Spike Duplicate fm aboratories, Inc. - ' RAM Environmental Engineering Services, Inc. Date Received: 09/26/08 ' 2115 20th Street Work Order No: 08-09-2430 Bakersfield, CA 93301-3710 Preparation: EPA 5030B Method: EPA 8260B ' Proiect Jaco Soil Sampling. 200370. Mt. Vernon Ave. ' Date Date MS/MSD Batch Quality Control Sample ID Matrix Instrument Prepared Analyzed Number 68-09-2080-6 Solid GC/MVEE 09/28/08 08128108: 080926$01 Parameter MS%REC MSD%REC %REC CL RPD RPD CIL Qualifiers ' Benzene 96 95 79-115 1 0-13 Carbon Tetrachloride 103 105 55-139 2 0-15 Chlorobenzene 97 96 79-115 1 0-17 1,2-Dibromoethane 91 88 70-130 3 0-30 ' 1,2-Dichlorobenzene 92 88 63-123 4 0-23 1,1-Dichloroethene 107 107 69-123 0 0-16 Ethylbenzene 104 103 70-130 1 0-30 ' Toluene 97 94 79-115 3 0-15 Trichloroethene 96 95 66-144 1 0-14 Vinyl Chloride 97 •102 60-126 5 0-14 ' Methyl-t-Butyl Ether(MTBE) 103 101 68-128 1 0-14 Tert-Butyl Alcohol(TBA) 76 72 44-134 6 0-37 Diisopropyl Ether(DIPE) 96 97 75-123 1 0-12 Ethyl-t-Butyl Ether(ETBE) 104 104 75-117 1 0-12 ' Tert-Amyl-Methyl Ether(TAME) 97 95 79-115 2 0-12 Ethanol 79 73 .42-138 8 0-28 1 1 ' RPD-Relative Percent Difference, CL-Control Limit 7440 Lincoln Way, Garden Grove, CA 92841-1427 . TEL:(714) 895-5494 FAX: (714) 894-7501 ' Page 12 of 18 ' & a/science nvironmental Quality Control - LCS/LCS Duplicate 1 aboratories, Inc. RAM Environmental Engineering Services, Inc. Date Received: N/A ' 2115 20th Street Work Order No: 08-09-2430 Bakersfield, CA 93301-371.0 Preparation: EPA 3550B Method: EPA 80158 (M) ' Project: Jaco Soil Sampling. 200370. Mt. Vernon Ave. 1 Date Date LCS/LCSD Batch Quality Control Sample ID Matrix Instrument Prepared Analyzed Number 099-12-276-2,189 Solid GC 27 09/29/08 09/30/08 080929608 1 Parameter LCS%REC LCSD%REC %REC CL RPD RPD CL Qualifiers TPH as Diesel 97 94 75-123 3 0-12 1 1 1 1 1 1 1 1 RPD-Relative Percent Difference, CL-Control Limit is 7440 Lincoln Way, Garden Grove, CA 92841-1427 . TEL:(714) 895-5494 . FAX: (714) 894-7501 1 Page 13 of 18 ' & alscience nvironmental Quality Control - LCS/LCS Duplicate ' . aboratories, Inc. RAM Environmental Engineering Services, Inc. Date Received: N/A ' 2115 20th Street Work Order No: 08-09 72430 Bakersfield, CA 93301-3710 Preparation: EPA 5030B Method: EPA 80156 (M) ' Project: Jaco Soil Sampling. 200370. Mt. Vernon Ave. 1 ' Date Date LCS/LCSD Batch Quality Control Sample ID Matrix Instrument 'Prepared Analyzed Number '099.12-279-2,278 Solid ,GC s1 09/29/08 09130108' 080929601 Parameter LCS%REC LCSD%REC %REC CL RPD RPD CL Qualifiers TPH as Gasoline 108 100 70-124 8 0-18 - RPD-Relative Percent Difference, CL-Control Limit ' 7440 Lincoln Way, Garden Grove, CA 92841-1427 . TEL:(714) 895-5494 . FAX: (714) 894-7501 ' Page 14 of 18 IL!!science nvironmental Quality Control - LCS/LCS Duplicate Aw �e aboratories,.Inc. � � RAM Environmental'Engineering Services, Inc. Date Received: , N/A ' 2115 20th Street Work Order No: 08-09-2430 Bakersfield, CA 93301-3710 Preparation: EPA 5030B Method: EPA 8260B Project: Jaco Soil Sampling. 200370. Mt. Vernon Ave. Date Date LCS/LCSD Batch. ' Quality Control Sample ID Matrix Instrument Prepared Analyzed Number 089 12 796=787 sSolld GC/MS EE, ,09/26/08 09/27/08 080926,03„ Parameter LCS%REC LCSD%REC %REC CL ME _ C4 RPD RPD CL Qualifiers Benzene 88 88 84-114 79-119 1 0-7 Carbon Tetrachloride 94 97 66-132 55-143 2 0-12 Chlorobenzene 87 86 87-111 83-115 0 0-7 ME ' 1,2-Dibromoethane 91 92 80-120 73-127 1 0-20 1,2-Dichlorobenzene 85 83 79-115 73-121 2 0-8 1,1-Dichloroethene 90 90 73-121 65-129 1 0-12 ' Ethylbenzene 92 92 60-120- 73-127 1 0-20 Toluene 87 87 78-114 72=120 0 0-7 Trichloroethene 86 86 84-114 79-119 1 0-8 Vinyl Chloride 83 82 63-129 52-140 1 0-15 Methyl-t-Butyl Ether(MTBE), 90 91 77-125 69-133 0 0-11 Tert-Butyl Alcohol(TBA) 88 91 47-137 32-152 3 0-27 Diisopropyl Ether(DIPE) 91 93 76-130 67-139 2 0-8 Ethyl-t-Butyl Ether(ETBE) 94 97 76-124 68-132 3 0-12 Tert-Amyl-Methyl Ether(TAME) 92 94 82-118 76-124 2 0-11 Ethanol 82 80 59-131 47-143 2 0-21 Total number of LCS compounds: 16 ' Total number of ME compounds: 1. Total number of ME compounds allowed: 1 LCS ME CL validation result: Pass 1 ' RPD-Relative Percent Difference, CL-Control Limit" 7440 Lincoln Way, Garden Grove, CA 92841-1427 . TEL:(714) 895-5494 . FAX: (714) 894-7501 1 ' Page 15 of 18 alscience 1 , nvironmenta/ Glossary of Terms and Qualifiers aboratories, Inc. Work Order Number: 08-09-2430 1 . Qualifier Definition ' See applicable analysis comment. 1 Surrogate compound recovery was out of control due to a required sample dilution, ' therefore, the sample data was reported without further clarification. 2 Surrogate compound recovery was-out of control due to matrix interference. The associated method blank surrogate spike compound was in control and, therefore, the ' sample data was reported without further clarification. 3 Recovery of the Matrix Spike (MS) or Matrix Spike Duplicate (MSD) compound was out of control due to matrix interference. The associated LCS and/or LCSD was'in control and, ' therefore, the sample data was reported without further clarification. 4 The MS/MSD RPD was out of control due to matrix interference. The LCS/LCSD RPD was in control and, therefore, the sample data was reported without further clarification. 5 The PDS/PDSD associated with this batch of samples was out of control due to a matrix interference effect. The associated batch LCS/LCSD was in control and, hence, the associated sample data was reported with no further corrective action required. A Result is the average of all dilutions, as defined by the method. B Analyte was present in the associated method blank. C Analyte presence was not confirmed on primary column. E Concentration exceeds the calibration range. ' H Sample received and/or analyzed past the recommended holding time. J Analyte was detected at a concentration below the reporting limit and above the laboratory method detection limit. Reported value is estimated. ME, LCS Recovery Percentage is within LCS ME Control Limit range. N Nontarget Analyte. 1 ND Parameter not detected at the indicated reporting limit. Q Spike recovery and RPD control limits do not apply resulting from the parameter concentration in the sample exceeding the spike concentration by a factor of four or greater. U Undetected at the laboratory method detection limit. ' X % Recovery and/or RPD out-of-range. Z Analyte presence was not confirmed by second column or GC/MS analysis. 7440 Lincoln Way, Garden Grove, CA 92841-1427 TEL:(714) 895-5494 FAX: (714) 894-7501 ! 48 0 "44o LWN WW ! ! ! ! ! ! ~ MRAIM CWOCRECM ! =ollt8l GARDEN GROVE,CA 92841-1432 DATE: 09/24/08 des,Ina TEL:(714)895-5494.FAX:(714)894-7501 PAGE: 1 OF 2 LABORATORY CLIENT: Jaco Oil Company/RAM Environmental ADDRESS: Jaco soil sampling. 200370. Mt.Vemon Ave. 2115 20th Street PROJECT CONTACT: QUOTE NO: CITY: jmcnaboe @ram-env.com Jane McNaboe Bakersfield,CA 93301 ✓AngPLER(S):(SIGNATURE) TEL FAX: E-MAIL J l 1 661)324-6152 661 324-6172 TURNAROUND TIME ❑SAME DAY ❑ 24 HR C-] 48HR E] 72 HR ® 5 DAYS E] 10 DAYS REQUESTED ANALYSIS SPECIAL REQUIREMENTS(ADDITIONAL COSTS MAY APPLY) ❑ RWQCB REPORTING ❑ ARCHIVE SAMPLES UNTIL _SPECIAL INSTRUCTIONS Please send results via email to Jane McNaboe. Please bill Jaco Oil. Please hold non-analyzed samples pending results. LOCATIONI SAMPLING w K SAMPLE ID DESCRIPTION DATE TIME er o f f m I'— H B-1-5 09/24108 0932 Soil 1 Hold 6-1-10 09/24/08 0943 Soil 1 Hold B-1-15 o9/2a/os 0951 Soil 1 X. X. X X B-1-20 09/24/08 1002 Soil 1 X X X X ' B-2-5 09/24/08 1042 Soil 1 Hold B-2-10 09/24/08 Soil 1 Hold B-2-15 09/24/08 1114 Soil 1 X. X X X B-2-20 09/2`4/08 1120 Soil 1 X X X X 09/24/08 1239 Soil 1 Hold B-3-10 09/24/08 1250 Soil Hold eli hed by. ' nature) 1 Ived by:(Signature) Dat : Rellnqul b :(Si nature) Received by.(Si /nnature) Date: Time: l�rJ I/ ' Relinquished by.(Slg ature) Received by.(Signature) Date: Time: a)0 21: 19 F 1020 o. 00 ftz �40 LWN W GARDEN GROVE,CA 92841-1432 DATE: 09/24/08 TEL(714)89545494.FAX:(714)894-7501 PAGE: 2 OF 2 LABORATORY.CLIENT: Jaco Oil Company/RAM Environmental ADDRESS: - Jaco soil sampling. 200376. Mt.Vernon Ave. 2115 20th Street PROJECT CONTACT: QUOTE NO.: CITY: jmcnaboe @rani-env.com Jane McNaboe Bakersfield CA 93301 R(s� sICNATU I :::�t�.yeQ�LY �:: . TEL FAX EMAIL 661 324-6152 661 324-6172 ` l � : ."'J '` LJ • TURNAROUND TIME ❑SAME DAY ❑ 24 HR [] 48HR [] 72 HR ® 5 DAYS ❑ 10 DAYS REQUESTED ANALYSIS SPECIAL REQUIREMENTS(ADDITIONAL COSTS MAY APPLY) ❑ RWQCS REPORTING ❑ ARCHIVE SAMPLES UNTIL SPECIAL INSTRUCTIONS Please send results via email to Jane McNaboe. Please bill Jaco Oil. Please hold non-analyzed.samples pending results. m a m UsB SAMPLE ID LOCATION! SAMPLING ++ a, = K = • 1iNLY DESCRIPTION DATE TIME �+ ++f F- ED o h ' ( B-3-15 09124108 1301 Soil 1 1 X X X X 3 B-3-20 09/24108 1312 Soil 1 X X X X Relinq : Signatur � ; �yece Da4 2� Ti2.�� i Relinqui by:(Signatur ) Received by:( igna ) Date: Time: Sin vu ^� Relinquished by:(Sig ure) Received by:(Signature) Date: Time: Z /020 O 00 Page 18 of 18 WORK ORDER #: 08 - a F91 - 0 a E 1-0 aailel1rfaj -Inc Cooler l of SAMPLE RECEIPT FORM CLIENT: &t-CO �r DATE: TEMPERATURE'— SAMPLES RECEIVED BY: . ' CALSCIENCE COURIER: LABORATORY (Other than Calscience Courier): Chilled, cooler with temperature blank provided. '_ ` 'C Temperature blank. Chilled, cooler without temperature Blank. __ °C I Thermometer. Chilled and placed in cooler with wet ice. Ambient temperature(For Air&Filter Only). Ambient and placed in cooler with wet ice. Ambient temperature(For Air& Filter Only). °C Temperature blank. Initial: ' CUSTODY SEAL INTACT: Sample(s): Cooler: No(Not Intact) : Not Present: ' Initial: ' SAMPLE CONDITION: Yes No N/A Chain-Of-Custody document(s)received with samples......................... L_... .... 1 Sampler's name indicated on COC.........:...............................I....... ... ... .. Sample container label(s)consistent with custody papers..................... ?\/ ... ... . ... .... Sample container(s)intact and good condition........I.......................... ... .... ' Correct containers and volume for analyses requested....................... Y ... .... ... .... Proper preservation noted on sample label(s)..................................... ... .... ... .... ✓ VOA vial(s)free of headspace. ....................................................... y Tedlar bag(s)free of condensation................................................... ... .... .. ... y Initial: COMMENTS: 1 . 1 SOP T100_081(09/19/08) 1 Page 1 of 15 alscience _nvironmental aboratories, Inc. t Supplemental Report 1 ' October 10, 2008 Additional requested analyses are reported as a stand-alone report. Jane McNaboe RAM Environmental Engineering Services, Inc. 2115 20th Street Bakersfield, CA 93301-3710 ' Subject: Calscience Work Order No.: 08-09-2430 Client Reference: Jaco Soil Sampling. 200370. Mt. Vernon Ave. Dear Client: Enclosed is an analytical report for the above-referenced project. The samples ' included in this report were received 9/26/2008 and analyzed in accordance with the attached chain-of-custody. Unless otherwise noted, all analytical testing was accomplished in accordance with the guidelines established in our Quality,Systems Manual, applicable standard operating procedures, and other related documentation. The original report of ' subcontracted analysis, if any, is provided herein,.and follows the standard Calscience data package. The results in this analytical report are limited to the samples tested and any reproduction thereof must be made in its entirety. . If you have any questions regarding this report, please do not hesitate to contact the undersigned. 1 Sincerely, ' Calscience Environmental Laboratories, Inc. Don Burley Project Manager "-ELAP ID: 1230 NELAP ID. 03220CA CSDLAC ID: 10109 SCAQMD ID. 93LA0830 7440 Lincoln Way, Garden Grove, CA 92841-1427 TEL.(714) 895-5494 FAX (7 14) 894-7501 Page 2 of 15 alscience ' �=nvironmental Analytical Report ' e ort v ' aboratories, Inc. -= RAM Environmental Engineering Services, Inc. Date Received: 09/26/08 ' 2115 20th'Street Work Order No: 08-09-2430 Bakersfield, CA 93301-3710 Preparation: EPA 3550B Method: EPA 8015B (M) ' Project: Jaco Soil Sampling. 200370. Mt. Vernon Ave. Page 1 of 1 Lab Sample Date/Time Date Daterrime ' Client Sample Number Number Collected Matrix Instrument Prepared Analyzed QC Batch ID A-3-5 08-09-2430-9-A 09124108, Solid' GC 15 10106/08 10/07/08 , 081006B02 12;39 06:19 ' parameter Result RL aE Qual Units TPH as Diesel ND 5.0 1 mg/kg ' Surrogates: REC I%) Control Limits Qual Decachlorobiphenyl 121 61-145 B=3-10 08-09 2430=10 :, 09/24108 'V„OSolld 'GC 15' " ;10/06/08 10/07/08' ,081006602. '12-50 q s-� 06.54 Parameter Result RL DF Qual Units ' TPH as Diesel ND 5.0 1 mg/kg ' Surrogates: REC(%) Control Limits Qual Decachlorobiphenyl 120 61-145 Method Blank x 099'42-275-2,206': °N/A F Solid ` GCAV5 -10106108 10/06/08 081006802 Parameter. Result RL DF Qual Units ' TPH as Diesel ND 5.0 1 mg/kg Surrogates: REC(%) Control Limits Qual Decachlorobiphenyl 114 61-145 ' RL-Reporting Limit DF-Dilution Factor Qual-Qualifiers 7440 Lincoln Way, Garden Grove, CA 92841-1427 TEL:(714) 895-5494 FAX: (714) 894-7501 Page 3 of 15 !/science DIM Analytical Report L. aboratories, Inc. ' RAM Environmental En g ineerin g S ervices Inc. Date Received: 09/26/08' 2115 20th Street . Work Order No: 08-09-2430 Bakersfield, CA 93301-3710 Preparation: EPA 50308 Method: EPA 8015B (M) Project: Jaco Soil Sampling. 200370. Mt. Vernon Ave. Page 1 of 1 Lab Sample Date/Time Date 'Date/Time Client Sample Number Number 'Collected Matrix. Instrument Prepared Analyzed QC Batch ID B-3-6 08-09-2430-9-A 09/24/08 Solid GC 1 10106/08 10/07/08 081006802 12:39 06:30 Parameter Result' RL p� Qu II Units TPH as Gasoline ND 0.50 1 mg/kg Surrogates: REC °o Control Limits Qual 1,4-Bromofluoro benzene-FID 79 42-126 8-3 10 f 08-09 2430-10'A 09/24/08. Solid GC 1 x„'10106/08. 10/07/08 081006801, , 12.50 '07 Para r Result RL DF Qual Units ' TPH as Gasoline ND 0.50 1 mg/kg Surrogates: REC °o Control Limits Qual 1,4-Bromofluorobenzene-FID 81 42-126 � �rw> -�5� �r�s -•�'� ' 2 - t�;�.a Method Blank-, + p ,099--'12-279-2,3 00 NIA °' Solid gG 1 10106108-`��10/06108 X081006602 Ns 19:22 .as •r v ' 5 - ._,_c ri�r hrr k'3},`'dsAw7' ,AM� .,t?-. •�'� ,�sASA^.r'�•.> '^'s`..r f.".'.,- . R Parame er Result RL DF Qual Units ' TPH as Gasoline ND 0.50 1 mg/kg Surrogates: ER C(°!01 Control Limits Qual 1,4-Bromofluorobenzene-FID 78 42-126 ' RL-Reporting Limit DF-Dilution Factor Qual-Qualifiers 7440 Lincoln Way, Garden Grove, CA 92841-1427 TEL:(714) 895-5494 FAX: (714) 894-7501 ' Page 4 of.15 a/science Am_nvironmental Analytical Report aboratories, Inc. RAM Environmental Engineering Services, Inc. Date Received: 09/26/08 2115 20th Street Work Order No: 08-09-2430 Bakersfield, CA 93301-3710 Preparation: EPA 5030B Method: EPA 8260B ' Units: ug/kg. Project: Jaco Soil Sampling. 200370. Mt. Vernon Ave. Page 1 of 1 Lab Sample Date/Time Date Datelrime Client Sample Number Number Collected Matrix Instrument Prepared Analyzed. QC Batch ID B-34 08,09-2430-9-A 09124108 Solid GC/Mt3-U '10103108 10103108 081003L01 12:39 19:30 - ' Parameter Result RL DF Qual Parameter Result RL DF Qual Benzene ND 5.0 1 Methyl-t-Butyl Ether(MTBE) ND 5.0 1 Ethylbenzene ND 5.0 1 Tert-Butyl Alcohol(TBA)• ND 50 1 Toluene ND 5.0 1 Diisopropyl Ether(DIPE) ND 10 1 ' p/m-Xylene ND 5.0 1 Ethyl-t-Butyl Ether(ETBE) ND 10 1 o-Xylene ND 5.0 1 Tert-Amyl-Methyl Ether(TAME) ND 10 1 Surrogates: REC(%) Control Qual Surrogates: REC(%) Control Qual Link U11121a Dibromofluoromethane 108 73-139 1,2 Dichloroethane-d4 98 73-145 Toluene-d8 98 90-108 1,4 Bromofluorobenzene 90 71-113 8 =10 k. 108-09 2430=10 A , 4,09/24/08 Solld GC/MS U y 1010310810/03/08 ;'0810031-01 12'50, ' Parameter Result RL DF Qual Parameter Result RL DF Qual Benzene ND 5.0 1 Methyl-t-Butyl Ether(MTBE) ND 5.0 1 Ethylbenzene ND 5.0 1 Tert-Butyl Alcohol(TBA) ND 50 1 Toluene ND 5.0 1 Diisopropyl Ether(DIPE) ND 10 1 p/m-Xylene ND 5.0 1 Ethyl4-Butyl Ether(ETBE) ND 10 1 o-Xylene ND 5.0 1 Tert-Amyl-Methyl Ether(TAME) ND 10 1 Surrogates: REC(%) Control Qual Surrogates: REC(%) Control Qua[ Limk Limits Dibromofluoromethane 111 73-139 1,2-Dichlorcethanetl4 99 73-145 Toluene-d8 99 90-108 1,4-Bromofluorobenzene 89 71-113 Method BIan X 099`72 798=230 NIA, $olld "AGC1M&U q'z' 03108 ,10103108 � 0810031-01 . Parameter Result RL DF Qual Parameter Result RL DF Qual Benzene ND 5.0 1 Methyl-t-Butyl Ether(MTBE) ND 5.0 1 Ethylbenzene ND 5.0 1 Tert-Butyl Alcohol(TBA) ND 50 1 Toluene ND 5.0 1 Diisopropyl Ether(DIPE) ND 10 1 p/m-Xylene ND 5.0 1 Ethyl-t-Butyl Ether(ETBE) ND 10 1 o-Xylene ND 5.0 1 Tert'Amyl-Methyl Ether(TAME) ND, 10 1 ' Surrogates: REC(%) Control ual Surrogates: REC(%) Control Qual Urlih Limi Dibromofluoromethane 121 73-139 1,2-Dichlorcethane-d4 104 73-145 Toluene-d8 102 90-108 1,4-Bromofluorobenzene 87 71-113 ' RL-Reporting Limit DF-Dilution Factor Qual-'Qualifiers 7440 Lincoln Way, Garden Grove, CA 92841-1427 TEL(714) 895-5494 FAX: (714) 894-7501 1 ' Page 5 of 15 .a/science nvironmental Quality Control - Spike/Spike Duplicate 1 &w aboratories, Inc. °° A' ,_• - RAM Environmental Engineering Services, Inc. Date Received: 09/26/08 211.5 20th Street Work Order No: 08-09-2430 Bakersfield, CA 93301-3710 Preparation: EPA 3550B Method: EPA 8015B (M) Proiect Jaco Soil Sampling. 200370. Mt. Vernon Ave. ' Date Date MS/MSD Batch Quality Control Sample ID Matrix Instrument Prepared Analyzed Number 08-10-0271-6 Solid GC,16. •. 10/06/08 10/06/08 08100002 ' Parameter MS%REC MSD%REC %REC CL RPD RPD CL Qualifiers ' TPH as Diesel 105 99 64-130 6 0-15 1 RPD-Relative Percent Difference, CL-Control Limit 7440 Lincoln Way, Garderi Grove, CA 92841-1427 . TEL:(714) 895-5494 FAX: (714) 894-7501 ' Page 6 of 15 alscience =, nvironmental Quality Control- Spike/Spike Duplicate ' aboratories, Inc: RAM Environmental Engineering Services, Inc. Date Received: 09/26/08 2115 20th Street Work Order No: 08-09-2430 Bakersfield., CA 93301-3710 Preparation: EPA 50306 Method: EPA 8015B (M) Protect Jaco Soil Samplinq. 200370. Mt. Vernon Ave. Date Date MS/MSD Batch ' Quality Control Sample ID Matrix Instrument Prepared Analyzed Number 08-10-01264 Solid GC-1 10106108 10/07/08 SO2 081006 Parameter MS%REC MSD%REC %REC CL RPD RPD CL Qualifiers TPH as Gasoline 88 83 48-114 6 0-23 ' RPD-Relative Percent Difference, CL-Control Limit 7440 Lincoln Way, Garden Grove, CA 92841-1427 . TEL:(714) 895-5494 FAX: (714) 894-7501 ' Page 7 of 15 a/science nvironmental Quality Control - Spike/Spike Duplicate LF aboraitodes, Inc. 1 , RAM Environmental Engineering Services, Inc. Date Received: 09/26/08 ' 2115 20th Street Work Order No: 08-09-2430 Bakersfield, CA 93301-3710 Preparation: EPA 5030B Method: EPA 8260B ' Project Jaco Soil Sampling. 200370. Mt. Vernon Ave. Date Date MS/MSD Batch Quality Control Sample ID Matrix Instrument Prepared Analyzed Number 08-10-0086-1 Solid GC/MS U 10/03/08 10/03/08 081663S01 Parameter MS%REC MSD%REC %REC CL RPD RPD CL. Qualifiers Benzene 100 101 79-115 1 0-13 Carbon Tetrachloride 108 105 55-139 3 0-15 Chlorobenzene 100 98 79-115 1 0-17 1,2-Dibromoethane .84 79 70-130 6 0-30 1,2-Dichlorobenzene 94 96 63-123 3 0-23 1,1-Dichloroethene 103 106 69-123 2 0-16 Ethylbenzene 100 100 70-130 0 0-30 Toluene 102 104 79-115 1 0-15 Trichloroethene 93 95 66-144 1 0-14 Vinyl Chloride 118 119 60-126 0 0-14 Methyl-t-Butyl Ether(MTBE) 87 86 68-128 1 0-14 ' Tert-Butyl Alcohol(TBA) 57 51 44-134 11 0-37 Diisopropyl Ether(DIPE) 97 95 75-123 2 0-12 Ethyl-t-Butyl Ether(ETBE) 88 88 75-117 0 0-12 ' Tert-Amyl-Methyl Ether(TAME) 92 89 79-115 3 0-12 Ethanol 50 38 42-138 28 0-28 3 1 ' RPD-Relative Percent Difference, CL-Control Limit 74'40 Lincoln Way, Garden Grove, CA 92841-1427 . TEL:(714) 895-5494 FAX: (714) 894-7501 Page 8 of 15 ' a/science nvironmental Quality Control - LCS/LCS Duplicate aboratories, Inc. RAM Environmental Engineering Services, Inc. Date Received: N/A ' 2115 20th Street Work Order No: 08-09-2430 Bakersfield, CA 93301-3710 Preparation' 3550B Method: EPA 8015B (M) Project: Jaco Soil Sampling. 200370. Mt. Vernon Ave. Date Date LCS/LCSD Batch Quality Control Sample ID Matrix Instrument Prepared Analyzed Number 099-12-276-2,206 Solid GC 1b 10/06/08 10/06/08 081006602 ' Parameter LCS%REC LCSD%REC %REC CL RPD RPD CL Qualifiers TPH as Diesel 104 106 75-123 2 0-12 1 1 1 1 1 ' RPD-Relative Percent Difference, CL-Control Limit 7440 Lincoln Way, Garden Grove, CA 92841-1427 . TEL:(714) 895-5494 .. FAX: (714) 894-7501 ' Page 9 of 15 a/science nvironmental Quality Control - LCSILCS Duplicate g ' am aboratories, Inc. I �- RAM Environmental Engineering Services, Inc. Date Received: N/A ' 2115 20th Street Work Order No: 08-09-2430 Bakersfield, CA 93301-3710 Preparation: EPA 5030B Method: EPA 8015B (M) ' Project: Jaco Soil Sampling. 200370. Mt. Vernon Ave. ' Date Date LCS/LCSD Batch Quality Control Sample ID Matrix Instrument Prepared 'Analyzed Number Fo . Solid GC 1 . 10/66/08 10/06/08 0810061302 tParameter LCS%REC LCSD%REC %REC CL RPD RPD CL Qualifiers TPH as Gasoline 88 89 70-124 1 0-18 1 1 RPD,-Relative Percent Difference, CL-Control Limit 7440 Lincoln Way, Garden Grove, CA 92841-1427 . TEL:(714) 895-5494 . FAX: (714) 894.-7501 ' Page 10 of 15 alscience nvironmental Quality Control - LCS/LCS Duplicate ' F= aboratories, Inc. RAM Environmental Engineering Services, Inc. Date Received: N/A ' 2115 20th Street Work Order No: . 08-09-2430 Bakersfield, CA 93301-3710 Preparation: EPA 5030B Method: EPA 82608 ' it , Project: Jaco So Sampling. 200370. Mt. Vernon Ave. Date Date LCS/LCSD Batch ' Duality Control Sample ID Matrix Instrument Prepared Analyzed Number 089-12-786-230 Solid GUMS U 10/03108 10103108 081003L01 Parameter LCS%REC LCSD%REC %oREC CL ME CL RPD RPD CL Qualifiers ' Benzene 97 96 . 84-114 79-119 1 0-7 Carbon Tetrachloride 107 99 66-132 55-143 7 0-12 Chlorobenzene 96 95 87-111 83-115 2 0-7 ' 1,2=Dibromoethane 91 92 80-120 73-127 1 0-20 1,2-Dichlorobenzene 99 97 79-115 73-121 2 0-8 1,1-Dichloroethene 103 100 73-121 65-129 3 0-12 Ethylbenzene 98 95- 80-120 73-127 3 0-20 ' Toluene 99 100 78-114 72-120 1 0-7 Trichloroethene 95 93 84-114 79-119 2 0-8 Vinyl Chloride 109 110 63-129 52-140 0 0-15 ' Methyl-t-Butyl Ether(MTBE) 101 98 77-125 69-133 3 0-11 Tert-Butyl Alcohol(TBA) 78 78 47-137 32-152 0 0-27 Diisopropyl Ether(DIPE) 97 96 76-130 67-139 1 0-8 Ethyl-t-Butyl Ether(ETBE) 99 95 76-124 68-132 4 0-12 ' Tert-Amyl-Methyl Ether(TAME) 102 101 82-118 76-124 1 0-11 Ethanol 72 75 59-131 47-143 4 0-21 Total number of LCS compounds: 16 ' Total number of ME compounds: 0 Total number of ME compounds allowed: 1 LCS ME CL validation result: Pass Relative Percent Difference, CL-Control Limit 7440 Lincoln Way, Garden Grove, CA 92841-1427 . TEL:(714) 895-5494 . FAX: (714) 894-7501 Page 11 of 15 glllZAIscience nvironmenta/ Glossary of Terms and Qualifiers ' AW aboratories, Inc. Work Order Number: 08-09-2430 Qualifier Definition See applicable'analysis comment. 1 Surrogate compound recovery was out of control due to a required sample dilution, ' therefore, the sample data was reported without further clarification. 2 Surrogate compound recovery was out of control due to matrix interference. The associated method blank surrogate spike compound was in control and, therefore, the ' sample data was,reported without further clarification. 3 Recovery of the Matrix Spike (MS) or Matrix Spike Duplicate (MSD) compound was out of control due to matrix interference. The associated LCS and/or LCSD was in control and, therefore, the sample data was reported without further clarification. 4 The MS/MSD RPD`was out of control due to matrix interference. The LCS/LCSD RPD was in control and, therefore, the sample data was reported without further clarification. 5 The PDS/PDSD associated with this batch of samples was out of control due to a matrix interference effect. The associated batch LCS/LCSD was in control and., hence, the associated sample data was,reported with no further corrective action,required. ' A Result is the average of all dilutions, as defined by the method. B Analyte was present in the associated method blank. ' C Analyte presence was not confirmed on primary column. E Concentration exceeds the calibration range. ' H Sample received and/or analyzed past the recommended holding time. J Analyte was detected at a concentration below the reporting limit and above the laboratory method detection limit. Reported value is estimated. ' ME LCS Recovery Percentage is within LCS ME Control Limit range. N Nontarget Analyte. ' ND Parameter not detected at the indicated reporting limit. Q Spike recovery and RPD control limits do not apply resulting from the parameter concentration in the sample exceeding the spike concentration by a factor of four or ' greater. U Undetected at the laboratory method detection limit. X % Recovery and/or RPD out-of-range. Z Analyte presence was not confirmed by second column or GC/MS analysis. 7440 Lincoln Way, Garden Grove, CA 92841-1427 TEL:(714) 895-5494 FAX: (714) 894-7501 1 ' Page P elofI g 12 0 5 Don Burley From: Jane McNaboe Umcnaboe @ram-env.com] Sent: Friday, October 03, 2008 11:51 AM To: Don Burley Cc: Rena Hamblin ' Subject: Jaco Mt. Vernon additional analyses,request WO No:08-09-2430 Don, 'lease analyze two soil samples that Calscience is holding from Work Order No. 08-09-2430 as follows: • Sample B-3-5(lab number 9), TPHd, TPHg, BTEX and fuel oxygenates, and • Sample B-3-10 (lab number 10), TPHd, TPHg, BTEX and fuel oxygenates. The soil samples should be analyzed on a standard turn around time. 'Thank you, Jane Ellis-McNaboe Professional Geologist NPRAM Environmental Engineering Services, Inc. C'm_cna_boe.@ram,-e_nv.com. 61 324-6162 office 61 324-6172 fax 661 246-9854 cell 'RAM 200370 r '. 10/3/2008 L o MW OWN MM OMMOV CM O�ECN GARDEN GROVE,CA 92841-1432 DATE: 09/24/08 L"awa e%dnr- TEL:(714)895-5494.FAX:(714)894-7501 PAGE: 1 OF 2 LABORATORY CLIENT: •: Jaco Oil Company/RAM Environmental ADDRESS: Jaco soil sampling. 200370. Mt.Vemon Ave. 2115 20th Street PROJECT CONTACT: QUOTE NO.:, CITY: jmcnaboe @ram-env.com Jane McNaboe Bakersfield,CA 93301 S,AAQPLER(s):(SIGNATURE) TEL FAX: E-MAIL 661 3246152 661 324-6172 TURNAROUND TIME ❑SAME DAY ❑ 24 HR ❑ 48HR ❑ 72 HR ® 5 DAYS ❑ 10 DAYS REQUESTED ANALYSIS SPECIAL REQUIREMENTS(ADDITIONAL COSTS MAY APPLY) ❑ RWQCB REPORTING ❑ ARCHIVE SAMPLES UNTIL SPECIAL INSTRUCTIONS Please send results via email to Jane McNaboe. Please bill Jaco Oil. Please hold non-analyzed samples pending results. W v o+ m LOCATION/ SAMPLING w >K w SAMPLE ID a ` .a o DESCRIPTION IME � W- DATE T I = Fm H a B-1-5 09/24/08 0932 Soil 1 Hold `: I B-1-10 09/24/08 0943 Soil 1 Hold B-1-15 09/24/08 0951 Soil 1 X X X X B-1-20 09/24/08 1002 Soil 1 X X X X ". B-2-5 09/24/08 1042 Soil 1 Hold B-2-10 09/24/08 Soil 1 Hold B-2-15 09/24/08 1114 Soil 1 X X X X B-2-20 09/24/08 1120 Soil 1 X X X X B-3-5 09/24/08 1238 Soil 1 Hold B-3-10 09/24/08 1250 Soil Hold eli had by. ' nature) 1 Ived by:(Signature) Dat `x/25 Relinqui �:(Si nature) Received by(Si nature) Date: . G5 9/'2 S S Relinquished by:(Sig ture) Received by:(Signature) Date: Time: I w 0 2G 6 D2 m W 0 ° M440 UWN q= M �1A1_r V L tl� GARDEN GROVE,CA 92841-1432 DATE: 09/24/08 Mtod88r Inm TEL(714)895-5494.FAX:(714)894-7801 PAGE:- 2 OF 2 LABORATORY CLIENT: . Jaco Oil Company/RAM Environmental ADDRESS: Jaco soil sampling. 200370. Mt.Vernon Ave. 2115 20tH Street PROJECT CONTACT: QUOTE NO.: CITY: jmcnaboe @ram-env.com Jane McNaboe. (S' SIGNATU Bakersfield CA 93301 d"T TEL FAX: E-MAIL 661 324-6152 661 324.6172 L�"1rlL7Jl T TURNAROUND TIME SAME DAY [D 24 HR E] 48HR ❑ 72 HR ® 5 DAYS ❑ 10 DAYS REQUESTED ANALYSIS SPECIAL REQUIREMENTS(ADDITIONAL COSTS MAY APPLY) ❑ RWQCB REPORTING ❑ ARCHIVE SAMPLES UNTIL SPECIAL INSTRUCTIONS Please send results via email to Jane McNaboe. Please bill Jaco Oil. Please hold non-analyzed samples pending results. W 00 SAMPLE ID LOCATION/ SAMPLING +� _ _ nN4Y DESCRIPTION DATE TIME 0 0A m B-3-15 09/24/08 1301 Soil 1 X X X X B-3-20 09/24/08 1312 Soil 1 X X X X Relinq : Signatur R y.(Signature) Date: Time: 1;Va S f S 4 Relinqui by:(Signatur ) Received by:( Igna ) Date: Time: Relinquished by:(Sig ure) Received by:(Signature) Date: Ti/me: N i A O 01 ' Page 15 of 15 WORK ORDER #.: 08 - CID- [2-1 R F31 KI l;S . rr Cooler I of ' SAMPLE RECEIPT FORM CLIENT: J CC CO or DATE: q12-VLO TEMPERATURE— SAMPLES RECEIVED BY: ' CALSCIENCE COURIER: LABORATORY (Other than Calscience Courier): Chilled, cooler with temperature blank provided. _ ` °C Temperature blank. ' Chilled, cooler without temperature blank. __ _ 'C IR Thermometer. Chilled and placed in cooler with wet ice. Ambient temperature(For Air&Filter Only). Ambient and placed in cooler with wet ice. ' Ambient temperature,(For Air& Filter Only). °C Temperature blank. Initial: CUSTODY SEAL INTACT: Sample(s): Cooler: No(Not Intact) : Not Present: ✓ ' Initial: ' SAMPLE CONDITION: Yes No N/A . Chain-Of-Custody document(s)received with samples......................... _L,.- _... ... . Sampler's name indicated'on COC.................................................. ... ... . Sample container label(s)consistent with custody papers..................... �/' ... .... ... .... Sample container(s)intact and good condition................................... Nlel ... .... ' Correct containers and volume for analyses requested....:.................. V ... .... ... .... Proper preservation noted on sample label(s)..............:...................... VOA vial(s)free of headspace. ....................................................... ... .... y ' Tedlar bag(s)free of condensation................................................... ... .... : y Initial: COMMENTS: SOP T100_081(09/19/08) 1 . 1 ' 1 Attachment D ' COPIES OF WASTE DISPOSAL MANIFESTS 1 ' 1 1 1 LION-HAZARDOUS 1.Generator ID Number 2.Page 1 of 3.Emergency Response Phone 4.Waste Tracking Number WASTE MANIFEST IraT.dn#An1'2Fk"4 5.Generator's Name and Mailing Address. Generators Site Address(ff different than mailing address) Fart rip 1731 ••• ,�'aco Oil Fa trip X31 - 3161 Nt Vernon Aire 3101 State Ed T3s7cers ae]ti, CA 93306 Bala-ersfi.eld- CA 93308 Generators Phone: n-$ a _-rnxan 6.Transporter 1 Company Name U.S.EPA ID Number Coles Rervir.-P;u Tr%n s:.isB ei�Sraarw ea 7.Transporter 2 Company Name U.S.EPA ID Number 8.Designated Facility Name and Site Address U.S.EPA ID Number Coles Sexvices Inc 1620 E. brundaye Lane Bakersfield, CA 93301 Facility's Phone:R&i 10.Containers 11.Total 12.Unit 9.Waste Shipping Name and Description ~ No. Type Quantity WtNol. ar' , 1'Ttaa�-Files ard��as Waste Solid (Soil. Igo i.ngr-) Fr. ... .. .._ - ._ '' - 0 3X�9E �`(•`i� S ` is'-. f. w � 'Yrt t' � '' W �r. �5 f' ir •���f •..A'S .r w . 23on-Hazardous Waste Solid (Soil c� Boxin�sJDrau19 DN P c iF 3. :,> 4. s .i'. 13. Special Handling Instructions and Additional Information 1) Soil_ )5ori q.% (Non- aiz) - Profs.left0:1808-01 t ' :ES foil �a9r�.41rq� �($10T;:-3Cst<�?�`'�$'tsiHi~ •° Y?x6:i:i.r!��fY�.CTi9�1»-t,�;e'.' 14.GENERATOR'S CERTIFICATION:I certify the materials described above on this manifest are not subject to federal regulations for reporting proper disposal of Hazardous Waste. nere ors/0 erors Printed/Typed� y�me f Sign ft Month Day Year J 15.In atfonal Shipments � // t F ❑I Port to U.S. ❑Export from U:�. Port of entry/exit: - ? Transporter Signature for exports only): Date leaving U.S.:. W 16.Transporter Acknowledgment of Receipt of Materials Trans er 1 Printed/Typed Name ! Signature // l ) Month Day Year w I�_ '(o�lt�C ` r��• r G�fy _ to lU oil . a Transporter 2 Printed/Typed Name Signature Month Day. .Year F 17.Discrepancy 17a.Discrepancy Indication Space ❑Quantity ❑Type ❑Residue ❑Partial Rejection ❑Full Rejection Manifest Reference Number. 17b.Alternate Facility(or Generator) U.S.EPA ID Number C) LL Facility's Phone: w "17c.Signature of Alternate Facility(or Generator) Month Day Year N _ + 1 r ' +�� s,�t � � ��• 'T w s`+l � � t r ^� 1', f a .+ r+r r � f sr' •t � �( 4r-u S ! t s i n r r c. -t �G �• r .. 3 "-A i w.�if ,L i 4 x r ry } r 18.Designated Facility Owner or Operator:Certification of receipt of materials covered by the manifest except as noted in Item 17a (. , Printed/TypedName _�', Signature `��� Month . Day Year 69-BLC-0 5 11977(Rev.8106) DESIGNATED FACILITY'S COPY