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AgdaPkt 2004-10-25
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AgdaPkt 2004-10-25
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7/16/2012 4:23:00 PM
Creation date
10/21/2004 1:19:57 PM
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CC Index
CC Index - Document Type
Agenda Packet
Date
10/25/2004
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C:ryptosporidium (part 2 of 2) Page 7 of 11 <br /> �.6-2q <br /> study in Kenya will soon be finalized. Initial results have been ambiguous since <br /> low oocyst dpses induced disease in some primates while higher doses failed to <br /> produce any iliness in other primates (maybe due to acquired immunity). A <br /> human feeding study in Texas evaluating the infedivity of various <br /> Cryprosporidium oocyst doses found 20 percent of the subjects were infected at <br /> the lowest dose (30 oocysts). A joint University of California at Davis and <br /> University of California at San Francisco study will evaluate the infective oocyst <br /> dose for immunocompromised primates to provide information on the minimum <br /> infective dose for immunocompromised populations. <br /> ■ Re/ative Exposure - It is unclear how much of the cryptosporidiosis risk can be <br /> attributed to drinking water. Work is vitally needed that distinguishes the water <br /> contribution to cryptosporidiosis from other sources. This will enable better risk <br /> management and more efficient resource allocation. <br /> ■ Communication of Uncertaintv - Issues associated with detection, species <br /> differentiation, viability, infectivity, host susceptibility, compel the uncertainty <br /> associated with cryptosporidiosis risk in drinking water. Better methods are <br /> needed for quantitatively characterizing this uncertainty and communicating it in a <br /> manner that is comprehensible to the public and aids them in making their own <br /> personal risk management decisions. <br /> ■ Chemica/ Inactivation - Further work needs to be done to evaluate the impacts of <br /> chlorine on environmentally-stressed oocysts which may be more susceptible to <br /> chlorine inactivation than fresh oocysts. The impact of sequencing disinfectants <br /> (e.g., chlorine followed by chloramine) needs to be evaluated further so as to <br /> refine the available alternatives for the SFPUC with regards to disinfection by- <br /> products. <br /> ■ Filtration - While some preliminary work has been conducted on the removal of <br /> Cryptosporidium in water treatment processes, more is needed on the influence of <br /> filter media and filtration rates. An assessment of the importance of increased <br /> parasite loading during the backwash water operations such as recycling, and flow <br /> , rate changes needs to be made. Work on Cryptosporidium removal is being <br /> completed under the auspices of AWWARF and by the British Drinking Water <br /> Inspectorate. <br /> Current Action Plan <br /> The SFPUC action plan is focused on providing information that will aid in the <br /> assessment and control of the risks associated with Cryptosporidium. <br /> ■ Monitorina - SFPUC will continue its monitoring program for its major sources and <br /> start to monitor treated water samples in addition to the existing distribution <br /> system locations. The sample volumes have been increased to lower the detection <br /> limits. <br /> ■ Treatment Process Evaluation - The two SFPUC filtration plants already conform to <br /> the recommendations of the Badenoch report and the Surface Water Treatment <br /> Rule. Nevertheless, an evaluation of operating practices (e.g., increasing plant <br /> http://sfwater.org/printContent.cfin/C_ID/445/ 10/19/2004 <br /> r _ .r. <br />
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