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ARCHIVED REPORTS UIC PERMIT APP
Environmental Health - Public
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THORNTON
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2900 - Site Mitigation Program
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PR0528038
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ARCHIVED REPORTS UIC PERMIT APP
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Last modified
9/26/2019 9:59:35 AM
Creation date
9/26/2019 9:22:35 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
UIC PERMIT APP
RECORD_ID
PR0528038
PE
2950
FACILITY_ID
FA0018998
FACILITY_NAME
NCPA LODI ENERGY CENTER
STREET_NUMBER
12751
Direction
N
STREET_NAME
THORNTON
STREET_TYPE
RD
City
LODI
Zip
95242
APN
05513016
CURRENT_STATUS
01
SITE_LOCATION
12751 N THORNTON RD
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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STIG PROJECT -- EVALUATION OF WATER FOR INJECTION -- 28 March 1994 8 <br /> Waste Receivor Tank <br /> Waste streams from the ultrafilter, cooling tower, RO unit, and boiler are collected in the <br /> waste receivor tank (60,000 gallon capacity). This tank provides a place to mix the several waste <br /> streams,providing a more predictable and uniform injectate.It also provides a damping effect for <br /> surges due to boiler blowdown. As a reservoir, it helps accomodate changes in rate of waste water <br /> disposal. <br /> Effects related to surging and mixing depend on the time that incoming parcels of liquid <br /> actually spend in the tank. For any one parcel, passage out of the tank may be described as a <br /> logarithmic dissipation. At nominal conditions, the working volume of the tank (<60,000 gal.) <br /> provides a residence time of about an hour or more. More precisely, a nominal half-time for <br /> clearance of an initial liquid parcel from the tank will vary depending on fill level and inflow <br /> rateb. Half-times on the order of one hour may be expected6. <br /> Relatively steady conditions of input to the tank are punctuated by blowdowns from the <br /> boiler, two or three times per day, when the rate changes suddenly from 3 gpm to 250 gpm, and <br /> back. Combining the surges into the steady boiler blowdown yields about 8 gpm,as an average for <br /> longer time intervals. Insertion of boiler blowdown imparts a nominal, momentary average <br /> concentration decrease of 5 to 10 percent, relative to the mixture composition prior to the boiler <br /> addition. Nominal average temperature effect will be a rise of 6° to 12°F, depending on current <br /> fill level7. <br /> Over time, surge effects from the boiler addition will both mix across the tank contents <br /> and dissipate due to discharge from the tank, the latter in accordance with current conditions <br /> which define residence half-life. Depending on conditions, this would permit a maximum of five <br /> to ten percent of the original (average) impact to be still present when the subsequent surge <br /> occurs$. <br /> Prior to boiler-induced surges, water composition in the tank could be within ±1 percent <br /> (relative)of a computed average based on composition and inflow rates of the three major,steady <br /> waste streams. Deviations from that, induced by boiler discharges, will not be large, and larger <br /> deviations will necessarily be associated with shorter lifetimes and smaller affected volumes. <br /> Effects of boiler alkalinity on the tank mixture will yield less than a 0.02 pH unit increase <br /> on the average fluid. This is less than the precision(±0.1 pH unit)used when estimating pH in the <br /> fluid mixtures. Transients near the point of insertion of the boiler discharge will be stronger than <br /> elsewhere, and cannot be defined sufficiently for precise modelling. Effects several times the <br /> average could still be regarded as negligible. <br /> Boiler discharges would have detectable effects in the waste receiver tank and transients <br /> there may have locally important effects. But, those effects may be expected not to propagate to <br /> the injection well in any important way. Thus, review of mineral deposition potential for fluid <br /> discharges from the receiver tank could be represented usefully by mixture compositions based on <br /> blending the three main waste stream compositions in proportion to their flow rates. It is <br /> recognized that dilutions of ten percent and temperature increases of 12°F are plausible, but <br /> quickly transient. Those transients should be recognized as being of the same relative magnitude <br /> as variations in the input water composition and temperature on which this assessment is based <br /> (Table 1). <br /> DON MICHELS ASSOCIATES -Missoula,Montana USA <br />
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