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Information Sheet IS-9 <br /> Reissued Waste Discharge Requirements General Order R5-2013-0122 <br /> Existing Milk Cow Dairies <br /> infiltration of water into underlying soils in manured areas. Furthermore, retention ponds must <br /> be located in, or lined with, soils of at least 10 percent clay and no more than 10 percent gravel. <br /> (Cal. Code. Regs., tit. 27, § 22562(d).) <br /> However, it is Central Valley Water Board staff's understanding that the retention pond standard <br /> was developed based on the assumption that manure solids contained within the wastewater <br /> would effectively reduce the permeability of the soils lining the wastewater ponds. This reduced <br /> permeability would result in a lowering of the pond leaching rate to a level thought to be <br /> protective of groundwater quality. An October 2003 report (the "Task 2 Report") by Brown, <br /> Vence, and Associates (BVA) confirmed that the "...current Title 27 requirements are insufficient <br /> to prevent groundwater contamination from confined animal facilities, particularly in vulnerable <br /> geologic environments." Adverse impacts have been detected in areas where groundwater is <br /> as deep as 120 feet below ground surface, and in some areas underlain by fine-grained <br /> sediments. Factors that appear to affect a clay-lined pond's ability to be protective of <br /> groundwater quality vary significantly from site to site due to native soil conditions, pond <br /> construction, pond age, manure properties, climate, pond operation, pond maintenance and <br /> depth to groundwater. Potential controlling factors appear to include: the inherent structure of <br /> the underlying soil, the moisture content of the unsaturated portion of the aquifer (vadose zone), <br /> the presence or absence of macropores or preferential pathways within the vadose zone <br /> (desiccation cracking, earthworm channels, development of root holes), and the oxidation <br /> reduction conditions present within the vadose zone and within the aquifer itself. <br /> Resolution 68-16(State Anti-Degradation Policy) <br /> The State Anti-Degradation Policy, adopted by the State Water Board in October 1968, limits <br /> the Board's discretion to authorize the degradation of high-quality waters. This policy has been <br /> incorporated into the Board's Basin Plans. High-quality waters are those waters where water <br /> quality is more than sufficient to support beneficial uses designated in the Board's Basin Plan. <br /> Whether or not a water is a high-quality water is established on a constituent-by-constituent <br /> basis, which means that an aquifer can be considered a high-quality water with respect to one <br /> constituent, but not for others. (State Water Board Order WQ 91-10.) <br /> The following provisions of the State Anti-Degradation Policy are directly applicable to the <br /> discharges regulated by the Dairy General Order: <br /> 1. Whenever the existing quality of water is better than the quality established in policies as of the <br /> date on which such policies become effective, such existing high quality will be maintained until it <br /> has been demonstrated to the State that any change will be consistent with maximum benefit to <br /> the people of the State, will not unreasonably affect present and anticipated beneficial use of <br /> such water, and will not result in water quality less than that prescribed in the policies. <br /> 2. Any activity which produces or may produce a waste or increased volume or concentration of <br /> waste and which discharges or proposes to discharge to existing high quality waters will be <br /> required to meet waste discharge requirements which will result in the best practicable treatment <br /> or control of the discharge necessary to assure that (a) a pollution or nuisance will not occur and <br />