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ARCHIVED REPORTS UIC PERMIT APP
Environmental Health - Public
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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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STIG PROJECT -- EVALUATION OF WATER FOR INJECTION -- 28 March 1994 18 <br /> times would be shorter for the same input/discharge rates. For example, a stable level of 5000 <br /> gallons with throughput of 406 g/m has t1/2 = 0.14 hours (8.5 min). <br /> 7. Sharp increases in temperature and decreases in concentration are not initially well mixed <br /> throughout the tank. Volume of boiler blowdown will be nominally 1/10 to 1/20th the volume <br /> in the tank. <br /> 8. For a maximum half-time of 2.4 hours with 8 hours between surges, a given surge effect is <br /> reduced to about (1/2)8/2.4= 0.10 of the initial (average) impulse. This is a maximum residual <br /> because a maximum half-time (2.4 hrs) was used in the estimate. <br /> 9. Separation factors vary with differences in input concentrations and with the volume ratio <br /> of permeate to waste.Also,different ions and molecules have their individual separation factors <br /> for any specific environment.These may be largely considered as secondary,minor factors that <br /> merely alter the details about the main effects. By considering the present system to be limited <br /> to the vicinity of nominal conditions, secondary effects will be negligible. Applicaton of these <br /> results to remote conditions risks inaccuracies, depending on true magnitudes of the secondary <br /> effects, which are not investigated. <br /> 10.For the range of operation of the ultrafilter(100 to 200 gpm discharge with 520 to 620 gpm <br /> input), concentration multipliers range from 1.4/.93 to 1.2/.91, where the numerator refers to <br /> the ratio of waste/input concentrations and the denominator refers to ratio of product/input <br /> concentrations. The numerically lower pair corresponds to larger relative (volumetric) waste <br /> rates. A mid-range pair, 1.3/.92, will be used for the nominal conditions modelled in this <br /> review. <br /> 11. Based on data for silica obtained during testing described by Al Beninati, 1994, Results of <br /> Ionics Test run on TX8665:Letter report to Northern California Power Agency,8 March.[Attn: <br /> Scott Eddy]. <br /> 12. A crude concentration factor (cf) for the RO is given by the ratio of input/waste volume <br /> rates,diminished by the portion(y)of dissolved component that follows permeate. For nominal <br /> rates and y=10%, cftrue = (1-0.10)420/130 = 2.91. Given that the RO input is depleted from <br /> the initial liquid concentration by the ultrafilter factor, 0.92, the effective RO mutiplier is <br /> 2.91(0.92) = 2.68. <br /> 13. Sludges removed from the cooling tower originate variously as depositions from the fluid <br /> and particulates scavenged from the atmosphere. Added chemicals partly aim to prevent <br /> deposition of water-borne components and these are more or less successful. <br /> 14. The boiler surge water contains silica at a concentration predicted to be less than 8 mg/kg. <br /> This is a result of evapo-concentration in the boiler operating on finite,residual concentrations <br /> of silica which pass through the RO and demineralizer units. Based on silica concentration in <br /> the original liquid, the internal multiplier for the boiler amounts to <8/59.5 -- 0.13. Since the <br /> boiler surge discharge enters the accumulated volume in the tank, is effect is diminished <br /> compared to what a steady-state contribution would be. In note 7, the average surge effect was <br /> indicated to be a maximum of only 5 to 10 percent of what a steady-state inflow would yield, <br /> and that dissipates between surges. Using a mid-range of 7 percent, the internal multiplier of <br /> the boiler yields a value of 0.07(.13) = 0.0094 in the waste receiver tank. <br /> DON MICHELS ASSOCIATES - Missoula,Montana USA <br />
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