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SR0082168
Environmental Health - Public
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SR0082168
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Entry Properties
Last modified
12/4/2024 1:32:50 PM
Creation date
9/1/2020 4:03:44 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4200 – Liquid Waste Program
RECORD_ID
SR0082168
PE
4201 - LIQUID WASTE PLAN CHECK
STREET_NUMBER
228
Direction
W
STREET_NAME
KLO
City
LATHROP
Zip
95330
APN
19124018
CURRENT_STATUS
Active, billable
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
228 W KLO LATHROP 95330
Tags
EHD - Public
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Nitrification occurrence can be confirmed by monitoring for nitrite or nitrate. Wilczak et al <br />(1996) suggest that an accurate nitrogen balance and specific biological monitoring for <br />ammonia -oxidizing bacteria and nitrite -oxidizing bacteria are the best ways to determine whether <br />nitrification is occurring. <br />4.0 Summary <br />Nitrification is a microbial process by which reduced nitrogen compounds (primarily ammonia) <br />are sequentially oxidized to nitrite and nitrate. Ammonia is present in drinking water through <br />either naturally -occurring processes or through ammonia addition during secondary disinfection <br />to form chloramines. Chloramine use is expected to increase in the near future as a result of more <br />stringent disinfection by-product (DBP) maximum contaminant levels (MCLs) associated with <br />the Stage I and Stage II Disinfectant/Disinfection By -Product Rule (D/DBP Rule). There are <br />several symptoms of nitrification that can impact distribution system water quality. Of the water <br />quality issues identified in the literature and summarized in Table 1, only the formation of nitrite <br />and nitrate within the distribution system poses a potential direct public health threat, and is not <br />addressed through current provisions of the Safe Drinking Water Act. The findings of this paper <br />suggest that a nitrite or nitrate MCL violation with the distribution system is unlikely, unless <br />treated water nitrite and nitrate levels are near their respective MCLs. Additional research may <br />be warranted to determine if nitrification episodes can cause direct violations of the Lead and <br />Copper Rule. The causes of nitrification and prevention and mitigation approaches have been <br />thoroughly documented within the literature. <br />5.0 Secondary Considerations <br />5.1 Increased Disinfection By -Products during Mitigation <br />Nitrification mitigation techniques such as break-point chlorination or temporarily switching <br />from chloramines to free chlorine can result in increased levels of disinfection by-products. <br />Disinfection by-products are regulated under the Stage 1 Disinfectants and Disinfection By - <br />Product Rule. Under the Disinfectants and Disinfection By -Product Rule compliance monitoring <br />samples are be collected under routine operating conditions. Thus, disinfection by-product <br />samples collected during a nitrification mitigation episode are not typically included in MCL <br />compliance calculations. It would also be possible to exceed a Maximum Residual Disinfectant <br />Level (MRDL) under the Disinfection By -Product Rule during a nitrification mitigation episode. <br />However, the USEPA specifically allows short-term exceedence of MRDLs to control <br />microbiological contamination problems. <br />5.2 Source Water Nitrification <br />Under certain circumstances nitrification can have a beneficial impact on drinking water quality. <br />This would be true in the controlled conditions at a water treatment plant. Rittmann and <br />Snoeyink (1984) reported that nitrification of ammonia -containing groundwater resulted in <br />"biologically stable" water that did not permit bacterial growth in the distribution system. Kurtz - <br />Crooks et al. (1986) showed that the chlorine demand of ammonia -laden groundwater was <br />.Prepared by AWWA with assistance from Economic and Engineering Services, Inc. 13 <br />
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