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An Ocean Blueprint for the 21st Century - California Ocean ...

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<strong>An</strong>imal Feeding OperationsMany animal feeding operations (<strong>for</strong> example, <strong>for</strong> beef cattle, hogs, or poultry) are locatedin coastal areas or in upstream areas that flow into coastal waters; <strong>the</strong>se businesses havebecome major contributors to coastal water pollution. Along <strong>the</strong> East Coast, many feedingoperations are concentrated in <strong>the</strong> coastal plain, which is home to an economically importantand ecologically sensitive network of wetlands, rivers, estuaries, and coastline.In <strong>the</strong> United States, <strong>the</strong>re are approximately 238,000 confined animal feeding operations,which produce an estimated 500 million tons of manure every year—more than 3times <strong>the</strong> amount of sewage produced by humans. 8 The animal manure generates dischargesof solids and liquid effluent to groundwater and surface waters. Ammonia ando<strong>the</strong>r gases also volatilize from manure in storage facilities or on fields, resulting in atmospherictransport and deposition of pollutants. Pollutants originating at animal feedingoperations include nutrients, ammonia, pathogens, hydrogen sulfide, methane, hormones,pesticides, and antibiotics.Although some discharges from animal feeding operations resemble dispersed nonpointsources of pollution, <strong>the</strong> larger concentrated animal feeding operations (CAFOs) aredefined and regulated as point sources under <strong>the</strong> NPDES program of <strong>the</strong> Clean Water Act.EPA issued new effluent guidelines and permitting regulations <strong>for</strong> CAFOs in December2002. Under <strong>the</strong>se new regulations, all CAFOs (about 18,500 nationwide) will be requiredto obtain NPDES permits from EPA or a state by 2006. These regulations are expected togreatly reduce <strong>the</strong> amount of nutrients and sediment entering coastal waters. 9,10 States thathave appropriate legal authority may impose requirements in addition to those in <strong>the</strong> EPACAFO regulations, such as regulating operations that are not large enough to be regulatedunder <strong>the</strong> EPA regulations, requiring increased monitoring and reporting, and requiringanimal processors to be co-permittees along with <strong>the</strong>ir contractors who raise <strong>the</strong> animals.Recommendation 14–3The U.S. Environmental Protection Agency (EPA) and <strong>the</strong> U.S. Department of Agriculture(USDA) should support research on <strong>the</strong> removal of nutrients from animal wastes that maypollute water bodies and on <strong>the</strong> impact of pharmaceuticals and o<strong>the</strong>r contaminants on waterquality. EPA and USDA should also develop improved best management practices that retainnutrients and pathogens from animal waste on agricultural lands. Where necessary to meetwater quality standards, states should issue regulatory controls on concentrated animal feedingoperations in addition to those required by EPA.Improving <strong>the</strong> Control of Point SourcesTo control point source pollution effectively, <strong>the</strong> nation will need to maintain a long-termcommitment to investments in infrastructure, improve <strong>the</strong> en<strong>for</strong>cement of water pollutionstandards, and promote market-based incentives and o<strong>the</strong>r innovative approaches.The Need <strong>for</strong> Long-term Infrastructure InvestmentsThe gap between existing and needed funding <strong>for</strong> wastewater and drinking waterimprovements is large, and serious adverse human health and environmental effects arelikely if <strong>the</strong> challenges presented by an aging public infrastructure are not addressed.Capital spending <strong>for</strong> public wastewater treatment infrastructure is currently about $13billion per year, and annual operations and maintenance costs are around $17 billion.EPA estimates that, over <strong>the</strong> next twenty years, <strong>the</strong> total additional investment needed <strong>for</strong>wastewater treatment infrastructure could exceed $270 billion, and <strong>for</strong> drinking waterinfrastructure could reach almost $265 billion. Sewer system overflows will be particularlycostly to correct. 11 These costs <strong>for</strong> infrastructure improvements are in addition to <strong>the</strong>C HAPTER 14: ADDRESSING C OASTAL WATER P OLLUTION211

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