Williams C M, Barker J C, Sims J T
Animal and Poultry Waste Management Center, North Carolina State University, Raleigh 27695-7608, USA.
Rev Environ Contam Toxicol. 1999;162:105-57. doi: 10.1007/978-1-4612-1528-8_3.
Waste by-products such as excreta or bedding material that are generated by the worldwide annual production of more than 40 million metric tons (t) of poultry meat and 600 billion eggs are generally land applied as the final step of a producer's waste management strategy. Under proper land application conditions, the nutrients and organisms in poultry wastes pose little environmental threat. Environmental contamination occurs when land application of poultry wastes is in excess of crop utilization potential, or is done under poor management conditions causing nutrient loss from environmental factors such as soil erosion or surface runoff during rainfall. Environmental parameters of concern are N, P, and certain metals (Cu and Zn in particular), as well as pathogenic microorganisms that may be contained in poultry waste. The biochemical cycle of N is very dynamic, and N contained in poultry waste may either be removed by crop harvest, leave the animal production facility, waste treatment lagoon, or application field as a gas (NH3, NO, NO2, N2O, or N2), or, due to its mobility in soil, be transported in organic or inorganic N forms in the liquid state via surface runoff or leaching into groundwater. Elevated concentrations of NO3-N in groundwater used for human consumption is a health risk to infants that are susceptible to methemoglobinemia. An environmental impact resulting from elevated NO3-N is eutrophication of surface waters. Ammonia loss from poultry waste is an environmental concern because of volatilized wet and dry deposits of NH3 into nitrogen-sensitive ecosystems. Phosphorus in poultry wastes may contribute to environmental degradation by accelerating the process of eutrophication. Unlike N, P is very immobile in soil and must first be transported to a surface water environment to have an environmental impact. It is generally accepted, however, that this nutrient affects receiving waters via transport in eroding soil as sediment-bound P or in surface runoff as soluble inorganic or organic P. Numerous studies have reported that excess P contained in land-applied manures may contribute to eutrophication. Soils containing P concentrations that greatly exceed the agronomic potential of crops may require years or even decades to return to levels that are crop limiting for this nutrient. Environmental concerns include the capacity of such soils to adsorb new P and the amount of P loss from these soils from erosion, runoff, drainage, or leaching to groundwater. Although much information is available regarding the loss of P from agricultural fields from erosion and runoff, less information is available regarding P losses from fields receiving poultry wastes. However, studies have shown that there are many challenges to controlling P losses from fields receiving manures. In addition, subsurface transport of P resulting from repeated application of poultry manure onto soils that are artificially drained is an environmental concern where drainage waters enter or interact with water bodies sensitive to eutrophication. Trace elements such as As, Co, Cu, Fe, Mn, Se, and Zn are often added in excess to poultry feed to increase the animal's rate of weight gain, feed efficiency, and egg production and to prevent diseases. Because most of the excess trace elements are not absorbed by the bird, the concentration of elements excreted in the manure will reflect dietary overformulation. Because trace elements are generally required in very small quantities for crop growth and, like P, are immobile in most soil types, their concentrations will increase with repeated land application of poultry wastes. Of particular concern are accumulations of Cu and Zn in certain soil types utilized for certain crops. Copper and Zn toxicity for some crops have been documented in some areas receiving repeated land-applied poultry wastes. A potential environmental concern relative to poultry litter and trace elements in receiving soils involves the transpor
全球每年生产超过4000万吨禽肉和6000亿枚鸡蛋所产生的排泄物或垫料等废弃物副产品,通常作为生产者废弃物管理策略的最后一步用于土地施用。在适当的土地施用条件下,禽粪中的养分和微生物对环境几乎没有威胁。当禽粪的土地施用超过作物利用潜力,或者在管理不善的条件下进行,导致在降雨期间因土壤侵蚀或地表径流等环境因素造成养分流失时,就会发生环境污染。值得关注的环境参数包括氮、磷和某些金属(特别是铜和锌),以及禽粪中可能含有的致病微生物。氮的生化循环非常活跃,禽粪中的氮可能通过作物收获被去除,以气体形式(氨、一氧化氮、二氧化氮、一氧化二氮或氮气)离开动物生产设施、废物处理泻湖或施用田地,或者由于其在土壤中的流动性,以有机或无机氮形式通过地表径流或淋溶进入地下水。用于人类消费的地下水中硝酸盐氮浓度升高对易患高铁血红蛋白血症的婴儿来说存在健康风险。硝酸盐氮浓度升高导致的环境影响是地表水富营养化。禽粪中的氨损失是一个环境问题,因为氨以干湿沉降形式挥发到对氮敏感的生态系统中。禽粪中的磷可能通过加速富营养化过程导致环境退化。与氮不同,磷在土壤中移动性很差,必须首先输送到地表水环境中才会产生环境影响。然而,一般认为这种养分通过侵蚀土壤中与沉积物结合的磷或地表径流中可溶性无机或有机磷的形式输送,从而影响受纳水体。许多研究报告称,土地施用的粪肥中过量的磷可能导致富营养化。含磷浓度大大超过作物农艺潜力的土壤可能需要数年甚至数十年才能恢复到该养分对作物有限制作用的水平。环境问题包括此类土壤吸附新磷的能力以及这些土壤因侵蚀、径流、排水或淋溶到地下水而造成的磷损失量。尽管有很多关于农田因侵蚀和径流造成磷损失的信息,但关于接收禽粪的田地中磷损失的信息较少。然而,研究表明,控制接收粪肥田地中的磷损失存在许多挑战。此外,在人工排水的土壤上反复施用禽粪导致的磷的地下输送也是一个环境问题,因为排水会进入对富营养化敏感的水体或与之相互作用。诸如砷、钴、铜、铁、锰、硒和锌等微量元素经常被过量添加到禽饲料中,以提高动物的体重增加速度、饲料效率和产蛋量,并预防疾病。由于大部分过量的微量元素未被禽类吸收,粪便中排出的元素浓度将反映日粮的过度配方。由于作物生长一般只需极少量的微量元素,而且与磷一样,在大多数土壤类型中移动性很差,随着禽粪在土地上的反复施用,它们的浓度会增加。特别令人担忧的是,在某些用于特定作物的土壤类型中铜和锌的积累。在一些反复施用禽粪的地区,已经记录了铜和锌对某些作物的毒性。与禽舍垫料和接收土壤中的微量元素相关的一个潜在环境问题涉及运输