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ARCHIVED REPORTS UIC PERMIT APP
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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
Fields
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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ATTACHMENT K:INJECTION PROCEDURES <br /> Injection Pressures <br /> STIG-1 <br /> The injection initially indicated that the STIG-1 well injection rate of 100 gpm would require <br /> an injection pressure of approximately 210 psi and the maximum injection rate of 200 gpm <br /> would have an injection pressure of about 325 psi. Figure K-1 shows the relationship <br /> between injection pressure and injection rate for the operating data collected since 2000. This <br /> shows that overall,injection rates and pressures are consistent and do not show a direct <br /> relationship. Figure K-4 shows the historic injection pressure and measured well head <br /> pressures at the STIG-1 well. No overall increase in wellhead pressure has been seen over <br /> the operating period of the well. <br /> Experiences elsewhere suggest that those initial surface pressures will have to be increased <br /> gradually with time,in order to continue the fluids disposal at a constant flow rate. Then, <br /> after having performed appropriate downhole stimulation treatments (see Attachment J), <br /> the surface pressures can be returned to near-initial conditions. These same pressures are <br /> expected to be found on the new injection well. <br /> However,the operating permit does not allow the surface pressure be allowed to exceed <br /> 975 psi,which historic data show it has not. This is the recommended surface pressure <br /> limitation proposed after an extensive analysis was performed to determine the pressure <br /> required to initiate fracturing of the confining layer above the injection zone. For a detailed <br /> description of that analysis,refer to Section 10 of the Mesquite Report provided in <br /> Appendix 9 of this Application. <br /> LEC-1 and LEC-2 <br /> Pressure increases at the LEC-1 well (and LEC-2 well,if installed) are predicted to not <br /> exceed 800 psi over the 30 year life of the well (Figure K-5) <br /> Waste Streams <br /> The sources of the wastewater to be injected in each well are discussed below. The water <br /> quality of the injected wastewater was presented in Attachment H. <br /> STIG-1 <br /> Brine reject from the ultrafiltration units,brine from the reverse osmosis units, and <br /> blowdown from the cooling towers collectively comprise about 98 percent of the treated <br /> wastewaters that are injected. The other 2 percent of the liquid wastes intended for injection <br /> consist of both continuous and intermittent blowdowns from the Heat Recovery Boilers. <br /> No other waste streams are injected.Filtrate from the chamber filter press and multimedia <br /> filters are collected and routed back to the feedwater storage tank. Periodic effluent from <br /> cleaning the reverse osmosis membrane systems and de minimis losses collected in the <br /> Neutralization and Chemical Drain System are sent to the White Slough WPCF for <br /> treatment. Storm water, service water, and condensate and other liquids in the plant drains <br /> are collected separately,passed through an oil-water separator, and pumped to the White <br /> SAC/371322/082390003(ATTACHMENT-K.DOC) K-3 <br />
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