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ARCHIVED REPORTS_ROY'S AUTO - HISTORICAL
Environmental Health - Public
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EHD Program Facility Records by Street Name
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M
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MINER
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3570
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2900 - Site Mitigation Program
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PR0527444
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ARCHIVED REPORTS_ROY'S AUTO - HISTORICAL
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Last modified
4/10/2020 4:53:44 PM
Creation date
4/10/2020 4:05:28 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
ROY'S AUTO - HISTORICAL
RECORD_ID
PR0527444
PE
2950
FACILITY_ID
FA0018586
FACILITY_NAME
FORMER ROY KNOLL TOWING
STREET_NUMBER
3570
Direction
E
STREET_NAME
MINER
STREET_TYPE
AVE
City
STOCKTON
Zip
95205
APN
14339014
CURRENT_STATUS
01
SITE_LOCATION
3570 E MINER AVE
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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initial elevation. Where water level recovery is slow, the sample will be collected after <br /> stabilization is achieved and enough water is present to fill sample container. <br /> Cross contamination from transferring pumps (or bailers) from well to well will be avoided by <br /> utilizing dedicated equipment. Where this is not feasible, thorough cleaning of equipment will <br /> be performed between sampling rounds. Sampling will proceed from the least contaminated to <br /> the most contaminated well, if information is available before sample collection, or if it is <br /> indicated by evidence. Where several types of analysis will be performed for a given well, <br /> individual samples will be collected in the following order: <br /> 1. Volatile organics <br /> 2. Purgeable organic hydrocarbons <br /> 3. Purgeable organic halogens <br /> 4. Total organic hydrocarbons <br /> 5. Total organic halogens <br /> 6. Extractable organics <br /> 7. Total metals <br /> 8. Dissolved metals <br /> 9. Phenols <br /> 10. Cyanide <br /> The specific analytical methods to be utilized for the common volatile/semivolatile analyses are <br /> shown on Table 2. <br /> Groundwater samples will be collected with a teflon bailer with bottom emptying device. <br /> Duplicate samples will be transferred to vials or containers that meet Regulatory Agency <br /> specifications (Table 1). Groundwater from the bailer will be transferred to the sample container <br /> by allowing the fluid to flow slowly along the sides of the vessel. All containers will be filled <br /> above the top of the opening to form a positive meniscus. No head space should be present in <br /> the sample container once it is sealed. After the vial is capped it will be inverted to chech for <br /> air bubbles. If bubbles are present the sample will be discarded and replaced. If it is not <br /> possible to collect a sample without head space, the problem will be noted on the field <br /> technicians's sampling log. <br /> Immediatedly following sample collection, samples will be labeled and stored in an ice chest <br /> containing frozen chemical ice sealed in plastic bags. Sample labels will contain the following <br /> information: date, time, project ID, sample ID, and name of sampler and type of analysis. All <br /> samples will be transported under chain of custody protocol to a state certified laboratory within <br /> 24 hours. A sample container filled in the laboratory with organic free water and carried <br /> unopened during the sampling trip will also be provided (Trip Blank). A "high-low" <br /> temperature recording thermometer will accompany sample shipments to ensure proper sample <br /> temperature maintenance. <br /> 8 <br />
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