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REMOVAL 2009
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2300 - Underground Storage Tank Program
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PR0231482
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REMOVAL 2009
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Entry Properties
Last modified
9/12/2018 5:08:40 PM
Creation date
9/12/2018 5:00:40 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2300 - Underground Storage Tank Program
File Section
REMOVAL 2009
FileName_PostFix
2009
RECORD_ID
PR0231482
PE
2361
FACILITY_ID
FA0000720
FACILITY_NAME
MADSENS SUNRISE DAIRY
STREET_NUMBER
239
Direction
S
STREET_NAME
STOCKTON
STREET_TYPE
ST
City
RIPON
Zip
95366
APN
25927805
CURRENT_STATUS
02
SITE_LOCATION
239 S STOCKTON ST
P_LOCATION
05
P_DISTRICT
005
QC Status
Approved
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WNg
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EHD - Public
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• <br />Limited Subsurface Investigation Report — City of Ripon / Madsen Sunrise Dairy, Ripon, California <br />September 30. 2010 <br />USTs were reported as not detected for Total Petroleum Hydrocarbons as gasoline (TPHg) and Benzene, <br />Toluene; Ethylbenzene, and Xylenes (BTEX). Inspection records provided by the SJCEHD show the former <br />fuel UST pit located approximately 100 feet north of 2nd Street and 5 feet west of Stockton Street (presumably <br />5 feet west of the property line). <br />On November 12, 2009, GR observed the removal of one 12,000 -gallon UST by Speehnan Excavation at the <br />site. No observable holes were noted in the UST. Following UST removal, GA collected soil samples TW -13 <br />and TE -13 at a depth of approximately 13 feet bgs from the beneath each end of the former UST. GR also <br />collected soil sample TM -13 from beneath the tank midpoint at a depth of 13 feet bgs. <br />Soil samples TE -13, TM -13, and TW -13 were analyzed for Total Petroleum Hydrocarbons as diesel (TPHd) by <br />EPA Method modified 8015, for TPHg, BTEX, Methyl tert-Butyl Ether (MtBE), Ethyl tert-Butyl Ether (ETRE), <br />Di -Isopropyl Ether (RIPE), Tert-Amyl Methyl Ether (TAME), and Tert-Butanol (TBA), 1,2-Dichloroethane (1,2- <br />DCA), and Ethylene Dibromide (EDB) by EPA Method 8260B. <br />BTEX, MtBE ETBE, DIPE, TAME, TBA; 1,2 -DCA and EDB were reported as below the laboratory method <br />reporting limits in samples TE -13, TM -13 and TW-13.TPHg was detected in soil sample TW -13 at a <br />concentration of 77 parts per million (ppm) and was reported as below the laboratory method reporting limits in <br />samples TM -13 and TE -13. TPHd was detected in soil sample TW -13 ata concentration of2,000 ppm and was <br />reported as below the laboratory method reporting limits in sample TM -13 and TE -13. <br />3.0 FIELD WORK <br />Fieldwork was conducted in accordance with GR's Field Methods and Procedures (Appendix A), the GR <br />Health and Safety Plan and the Site Specific Safety Plan dated August 3, 2010. Geoprobes® were advanced <br />under well permit number 60610, issued by the SJCEHD on July 28, 2010 (Appendix B). Underground <br />Service Alert (USA) was notified prior to probing at the site. <br />3.1 Geoprobe® Advancement <br />On August 5, 2010, a GR geologist observed Gregg Drilling Inc. (C-57 #485165) advance four Geoprobe® <br />soil borings (GP -1 through GP -4). The borings were hand excavated for the fust four feet bgs to insure that no <br />utilities were disturbed. The borings were advanced with a truck -mounted rig utilizing direct push technology. <br />The Geoprobe locations are shown on Figure 3. <br />All Geoprobes® were advanced to 32 feet bgs. Soil sampling for lithologic logging was conducted <br />continuously beginning at four feet bgs and soil samples from selected depths were collected for chemical <br />analysis. The soil samples were handled in accordance with GR's Field Methods and Procedures (Appendix <br />A). The samples were not screened in the field for the presence of volatile organic compounds (VOCs) due to <br />instrument malfunction. The GR geologist prepared logs of the Geoprobes with lithologic descriptions and the <br />depths at which soil and groundwater samples were collected. The logs are presented in Appendix B. <br />25-948223.1.3 <br />
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