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ARCHIVED REPORTS_XR0003878
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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O
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120 (STATE ROUTE 120)
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17000
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3500 - Local Oversight Program
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PR0545632
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ARCHIVED REPORTS_XR0003878
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Last modified
11/19/2024 3:59:34 PM
Creation date
5/4/2020 12:30:19 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003878
RECORD_ID
PR0545632
PE
3528
FACILITY_ID
FA0005176
FACILITY_NAME
FRANZIA WINERY
STREET_NUMBER
17000
Direction
E
STREET_NAME
STATE ROUTE 120
City
RIPON
Zip
95366
APN
24506030
CURRENT_STATUS
02
SITE_LOCATION
17000 E HWY 120
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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casing volume. Once the well is purged and indicator <br /> parameters have stabilized, a sample will be collected after <br /> the water level approaches 80 percent of its initial <br /> elevation. Where water level recovery is slow, the sample <br />} will be collected after stabilization is achieved and enough <br /> water is present to fill sample containers. <br /> Cross contamination from transferring pumps (or bailers) <br /> ' from well to well will be avoided by utilizing dedicated <br /> equipment. Where this is not feasible, thorough cleani-,g of <br /> equipment will be performed between sampling rounds. <br /> Sampling will proceed from the least contaminated to the <br /> most contaminated well, if information is available before <br /> sample collection, or if it is indicated by field evidence. <br /> 1 Where several types of analysis will be performed for a <br /> given well, individual samples will be collected in the <br /> following order: <br /> 1. Volatile organics <br /> 2. Purgeable organic carbon <br /> 3. Purgeable organic halogens <br /> 4. Total organic carbon <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 be utilized for the common <br /> volatile/sewivolatile to analyses are shown on Table 2. <br /> Groundwater samples will be collected with a teflon bailer <br /> with bottom emptying device. Duplicate samples will be <br /> transferred to vials or containers that meet Regional Board <br /> specifications (Table 1). Groundwater from the bailer will <br /> be transferred to the sample container by allowing the fluid <br /> to flow slowly along the sides of the vessel. All <br /> ' containers will be filled above the top of the opening to <br /> form a positive meniscus. No head space should be present <br /> in the sample container once it is sealed. After the vial is <br /> ' capped it will be inverted to check for air bubbles. If <br /> bubbles are present the sample will be discarded and <br /> replaced. If it is not possible to collect a sample without <br /> head space, the problem will be noted on the field <br /> ' technician' s sampling log. <br /> Immediately following sample collection, samples will be <br /> labeled and stored in an ice chest containing frozen <br /> chemical ice sealed in plastic bags. Sample labels will <br /> contain the following information: date, time, project ID, <br /> sample ID, name of sampler and type of analysis. All <br /> samples will be transported under chain-of-custody protocol <br /> to a state certified laboratory within 24 hours. A sample <br /> container filled in the laboratory with organic free water <br />
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