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COMPLIANCE INFO_2020
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2200 - Hazardous Waste Program
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PR0541637
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COMPLIANCE INFO_2020
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Entry Properties
Last modified
11/4/2020 10:19:34 AM
Creation date
9/1/2020 3:48:36 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2200 - Hazardous Waste Program
File Section
COMPLIANCE INFO
FileName_PostFix
2020
RECORD_ID
PR0541637
PE
2226
FACILITY_ID
FA0009758
FACILITY_NAME
SFPUC Tesla Treatment Facility
STREET_NUMBER
9000
Direction
W
STREET_NAME
VERNALIS
STREET_TYPE
Rd
City
Tracy
Zip
95377
CURRENT_STATUS
01
SITE_LOCATION
9000 W Vernalis Rd
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\dsedra
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EHD - Public
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SFPUC June 10, 2020 Page 11 <br /> • After each UV lamp break, the concrete floor is scrubbed and debris is removed to ensure <br /> that any mercury residue is removed to the maximum extent practicable. Any mercury- <br /> contaminated materials are packaged, labeled waste, and stored in the facility's hazardous <br /> waste locker for subsequent off-site disposal. <br /> Monitoring <br /> Monitoring recommendations described here are meant to optimize staff time and the quality of <br /> the data staff collect during and following a UV lamp break. <br /> Downstream Water Monitoring <br /> Water samples should be collected at the Alameda facility downstream over the period that water <br /> leaving the Tesla Facility during a UV lamp break passes (consisting of 5 samples: during the <br /> expected arrival time+/- 10 minutes and 20 minutes). The expected arrival time can be estimated <br /> as: <br /> Time delay(hrs) = 1711/Flowrate(million gallons per day, or MGD) <br /> Based on the typical range of flowrates (range of 140-290 MGD; average of 220 MGD), the <br /> travel time will be 6-12 hours. Results should be compared to the Safe Drinking Water Act's <br /> primary Maximum Contaminant Level of 2 pg/L for inorganic mercury [40 CFR 141.62(b)], <br /> although the instantaneous peak based on turbulent dispersion should be less than 0.6 ug/L. <br /> Ambient Air Measurements <br /> Worker should deploy the Jerome mercury vapor analyzer following each spill event to assess <br /> the level of elemental mercury vapor in the UV Building. The unit's detection limit of 0.5 ug/m3 <br /> is well below the OSHA limit of 25 ug/m3 and the SOP action levels of 3-10 ug/m3. The unit <br /> should be deployed to confirm that ambient air mercury concentrations are below industrial <br /> thresholds in the SOP. The Jerome analyzer should continue to be recalibrated annually. <br /> Visual Monitoring <br /> While cleaning UV lamp covers and the UV Building floor following a UV lamp break, workers <br /> should look closely for evidence of mercury droplets adsorbed to surfaces, taking notes on, and <br /> photographs of any identified mercury droplets, as described in the SOP. During maintenance of <br /> the pipeline downstream of the UV Building, workers should look closely for evidence of <br /> mercury on the pipeline walls and low points. <br /> Water Samples <br /> Water"grab" samples should be collected and analyzed for total mercury following each UV <br /> lamp break at the following locations, labeled consistently with these names: <br /> • Reactor drain (the drainage water from the closed-off reactor section) <br /> • Trench (standing water in the grated floor trench,upstream of the 4-inch weir) <br /> • Pond inlet(discharges from the below-grade culvert into Grit Pond#1 <br />
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