基于生命周期视角的种养一体化奶牛场环境经济效益评估

准确评估种养一体化奶牛场的经济性能与环境绩效,是相关支持政策制定的基础,也是促进奶业低碳生产的关键.本文基于生命周期视角,对非种养一体化奶牛场（non-IPBS）和种养一体化奶牛场（IPBS）养殖过程中的温室气体排放、能源消耗、水消耗、土地占用等环境成本和经济效益进行评估.结果表明,non-IPBS生产1t标准牛奶（FPCM）的净收益为1427元,而IPBS的实际净收益提高7%,如果青贮玉米自给率从当前的32%提升到100%,则实际净收益将提高19%,同时,该净收益的提高率取决于耕地流转费用,临界点为14695元/hm²;相比non-IPBS,IPBS生产1tFPCM的温室气体排放、能源消耗、水消耗、土地占用分别减少6%、6%、5%、7%,如果青贮玉米自给率提升到100%,则相应减少16%、16%、11%、14%.IPBS在降低青贮玉米种植的化肥施用、解决养殖场粪便污染等方面优势明显,在提升养殖经济效益、降低温室气体排放等方面具有巨大潜力,值得推广.     

Life cycle assessment of milk production — a comparison of conventional and organic farming

An LCA was performed on organic and conventional milk production at the farm level in Sweden. In the study, special focus was aimed at substance flows in concentrate feed production and nutrient flows on the farms. The different feeding strategies in the two forms of production, influence several impact categories. The import of feed by conventional dairy farms often leads to a substantial input of phosphorus and nitrogen. Organic milk production is a way to reduce pesticide use and mineral surplus in agriculture but this production form also requires substantially more farmland than conventional production. For Swedish conditions, however, a large use of grassland for grazing ruminants is regarded positively since this type of arable land use promotes the domestic environmental goals of biodiversity and aesthetic values.     

牛粪便资源化利用的研究进展

随着规模化养牛业的迅猛发展,由牛粪便带来的环境污染问题日益严重,主要涉及恶臭气体的污染、氮磷污染、药物、添加剂污染、有害病原微生物污染以及重金属元素污染等。牛粪便资源化利用主要遵循生态效益、积极效益和社会效益最大限度统一平衡的原则,努力实现物质最大化利用。文章综述了牛粪对环境污染的现状以及国内外利用牛粪便的主要资源化技术途径,包括能源化、肥料化、饲料化、食用菌栽培和蚯蚓生物分解处理等,分析探讨了各个资源化技术的优缺点,认识到单一技术存在的局限性,如粪便饲料化,可能存在中毒等安全隐患,高温好氧堆肥技术则主要针对固粪的处理。因而提出了多种牛粪便资源化技术有效结合,以发挥最大的经济和环境效益,实现资源的综合循环利用,同时对各个技术统筹结合的发展方向进行了展望。     

Modelling greenhouse gas emissions from European conventional and organic dairy farms

Agriculture is an important contributor to global emissions of greenhouse gases (GHG), in particular for methane (CH₄) and nitrous oxide (N₂O). Emissions from farms with a stock of ruminant animals are particularly high due to CH₄ emissions from enteric fermentation and manure handling, and due to the intensive nitrogen (N) cycle on such farms leading to direct and indirect N₂O emissions. The whole-farm model, FarmGHG, was designed to quantify the flows of carbon (C) and nitrogen (N) on dairy farms. The aim of the model was to allow quantification of effects of management practices and mitigation options on GHG emissions. The model provides assessments of emissions from both the production unit and the pre-chains. However, the model does not quantify changes in soil C storage.Model dairy farms were defined within five European agro-ecological zones for both organic and conventional systems. The model farms were all defined to have the same utilised agricultural area (50 ha). Cows on conventional and organic model farms were defined to achieve the same milk yield, so the basic difference between conventional and organic farms was expressed in the livestock density. The organic farms were defined to be 100% self-sufficient with respect to feed. The conventional farms, on the other hand, import concentrates as supplementary feed and their livestock density was defined to be 75% higher than the organic farm density. Regional differences between farms were expressed in the milk yield, the crop rotations, and the cow housing system and manure management method most common to each region.The model results showed that the emissions at farm level could be related to either the farm N surplus or the farm N efficiency. The farm N surplus appeared to be a good proxy for GHG emissions per unit of land area. The GHG emissions increased from 3.0 Mg CO₂-eq ha⁻¹ year⁻¹ at a N surplus of 56 kg N ha⁻¹ year⁻¹ to 15.9 Mg CO₂-eq ha⁻¹ year⁻¹ at a N surplus of 319 kg N ha⁻¹ year⁻¹. The farm N surplus can relatively easily be determined on practical farms from the farm records of imports and exports and the composition of the crop rotation. The GHG emissions per product unit (milk or metabolic energy) were quite closely related to the farm N efficiency, and a doubling of the N efficiency from 12.5 to 25% reduced the emissions per product unit by ca. 50%. The farm N efficiency may therefore be used as a proxy for comparing the efficiencies of farms with respect to supplying products with a low GHG emission.     

规模化养殖的中国荷斯坦奶牛产污系数模型的确定

以近期中国荷斯坦奶牛产污系数试验资料为基础,分析饲料摄入量及成分与排出粪污污染物之间的关系,建立了奶牛产污系数模型并进行了验证.结果表明:育成牛排粪量可用采食量、摄入氮、摄入磷和摄入铜4因子预测,其模型拟合度高于产奶牛;育成牛排氮量可用采食量、摄入氮两因子预测,产奶牛的排氮量可用摄入氮预测;产奶牛和育成牛的排磷量均可用摄入磷预测.该模型由于包括了不同季节、不同样本、不同奶牛养殖场等影响因素,使结果具有广泛的适用性,可用于分析中国荷斯坦奶牛养殖对环境的污染及粪污农田的消纳利用.     

硝化抑制剂对我国蔬菜生产产量、氮肥利用率和氧化亚氮减排效应的影响:Meta分析

我国蔬菜生产系统由于长期过量施肥导致氮肥利用率低和环境问题严重,氮肥配施硝化抑制剂是降低活性氮损失、增加蔬菜产量和提高氮肥利用率的有效策略,然而缺乏系统研究.基于数据整合分析的方法,系统分析了氮肥配施硝化抑制剂［双氰胺（DCD）、3,4-二甲基吡唑磷酸盐（DMPP）和2-氯-6-三氯甲基吡啶（NP）］对我国蔬菜生产的产量、植株氮吸收、氮肥利用率和氧化亚氮减排效应的影响,进一步揭示不同田间管理措施对其效果的影响.结果表明,氮肥配施硝化抑制剂能够显著提高蔬菜产量（9.2%）、植株氮吸收（10.4%）和氮肥利用效率（11.2%）,同时减少氧化亚氮排放（28.4%）.不同硝化抑制剂类型中,NP对增产效应和氧化亚氮减排效应的影响幅度最高,分别为16.1%和32.0%,其次是DMPP和DCD.硝化抑制剂在不同氮肥用量中能提高蔬菜产量（6.7%~14.7%）和减少氧化亚氮排放（14.6%~36.8%）.在中性和碱性菜地土壤中,硝化抑制剂的增产效应和氧化亚氮减排效应的影响幅度较酸性土大.硝化抑制剂在露地栽培、根菜类和叶菜类的条件下对产量的增加和氧化亚氮的减排效果较好.主成分分析表明,土壤总氮含量和土壤pH是影响硝化抑制剂对蔬菜产量形成和驱动氧化亚氮排放的主要因素.综上,硝化抑制剂是实现蔬菜系统提质增效、节肥减排的重要举措.同时,农户应根据土壤和田间管理措施选择适宜硝化抑制剂类型,以最大限度提高其有效性.     

典型畜禽粪污中雌激素排放特征

为探究畜禽粪污中雌激素的排放水平和分布特征,采用固相萃取-高效液相色谱串联质谱（SPE-HPLC-MS/MS）分析方法,对上海市典型畜禽养殖类型（猪、奶牛、鸡）排放粪污样品中雌激素含量进行测定.结果表明:猪场粪便、沼渣肥、还田土壤、尿液和沼液样品中5种雌激素（E1,雌酮;E2,雌二醇;E3,雌三醇;EE2,炔雌醇;DES,己烯雌酚）总量分别为94.5 ng/g、35.1 ng/g、0.1 ng/g和8 882.2 ng/L、4 388.6 ng/L,其中E1是排泄物中最主要的雌激素;奶牛场粪便、堆肥、还田土壤、尿液、污水进水及出水样品中雌激素总量分别为84.6 ng/g、16.2 ng/g、0.1 ng/g和2 636.7 ng/L、2 605.6 ng/L、615.7 ng/L,其中E1和E2含量最高;鸡场粪便和堆肥样品中雌激素总量分别为60.9和17.5 ng/g.研究显示,猪场、奶牛场和鸡场排泄物中均含有一定数量的天然和人工合成雌激素,雌激素含量水平总体表现为粪便高于有机肥、尿液高于污水;通过畜禽粪污向环境中排放的雌激素总量表现为猪场>奶牛场>鸡场;厌氧发酵对猪场污水中雌激素具有一定的去除效果,而污水厌氧-好氧净化处理和固体粪高温好氧堆肥对奶牛场排泄物中雌激素具有较高的去除效果.      

Changes in heavy metal contents in animal feeds and manures in an intensive animal production region of China

The 360 feed and manure samples were collected from 150 animal farms in Jiangsu Province, China and analyzed for heavy metals. Concentrations of Zn and Cu in animal feeds were 15.9-2041.8 and undetected-392.1 mg/kg respectively, while Hg, As, Pb, Cd, and Cr in all feeds were below 10 mg/kg. Concentrations of Cu, Zn, and Cr in animal manures were 8.4-1726, 39.5-11379, and 1.0-1602 mg/kg respectively, while As, Cd, Hg, and Pb were 〈 10 mg/kg. The concentration of Cu, Zn, As and Cr in animal feed and manure were positively correlated （p 〈 0.001）, but the Cd, Hg, and Pb were not statistically correlated between the feed and the manure. Concentrations of Cu and Zn were highest in pig feed and manure, followed by poultry and dairy feeds and manures. During 1990- 2008, Cu, Zn, As, Cr, Cd contents increased by 771%, 410%, 420%, 220%, and 63% in pig manure, 212%, 95%, 200%, 791%, and -63% in dairy manure, and 181%, 197%, 1500%, 261, and 196% in poultry manure. Most of the increases occurred from 2002 to 2008, which reflects the extensive use of feed additives after 2002. In contrast, Pb and Hg in manures continuously decreased from 1990 to 2008. The results suggest that the heavy metal contents in animal manure have been greatly increased over 18 years and the contribution of manures to soil should be considered.     

江苏省案例地区牲畜养殖养分循环与环境效应

运用案例区域调查法和养分物质分析法,对江苏牲畜养殖场饲料、牲畜排泄物、土壤、地表及地下水体养分状况进行了调查、分析对牲畜规模养殖中的养分循环与管理及其环境效应进行了评价.研究表明,牲畜养殖中液体粪水的排放和露天堆放固体粪便的淋失易造成环境问题.地表水体之间的水力联系和地表径流是造成牲畜养殖废弃物环境问题的主要途径.虽然采取固体粪便与液体粪水相分离的方法在一定程度上减少了对环境的影响,但液体粪水仍是污染环境的主要来源.本文还对液体粪水的处理与利用、牲畜排泄物的利用与养分管理提出了建议.     

NUTGRANJA 2.0: a simple mass balance model to explore the effects of different management strategies on nitrogen and greenhouse gases losses and soil phosphorus changes in dairy farms

Farm nutrient management has been identified as one of the most important factors determining the economic and environmental performance of dairy cattle (Bos taurus) farming systems. Given the environmental problems associated with dairy farms, such as emissions of greenhouse gases (GHG), and the complex interaction between farm management, environment and genetics, there is a need to develop robust tools which enable scientists and policy makers to study all these interactions. This paper describes the development of a simple model called NUTGRANJA 2.0 to evaluate GHG emissions and nitrogen (N) and phosphorus (P) losses from dairy farms. NUTGRANJA 2.0 is an empirical mass-balance model developed in order to simulate the main transfers and flows of N and P through the different stages of the dairy farm management. A model sensitivity test was carried out to explore some of the sensitivities of the model in relation to the simulation of GHG and N emissions. This test indicated that both management (e.g. milk yield per cow, annual fertiliser N rate) and site-specific factors (e.g. % clover (Trifolium) in the sward, soil type, and % land slope) had a large effect on most of the model state variables studied (e.g. GHG and N losses).     

Phosphorus loss from different farming systems estimated from soil surface phosphorus balance

The phosphorus load originating from crop production and animal husbandry is a major contributor to the eutrophication of lakes, rivers and coastal waters. The P losses to surface waters may, however, differ drastically due to the diversity of agricultural production systems practised under contrasting environmental conditions. To assess the most problematic types of agriculture, we need information on the P load from different alternative farming practices. Such information cannot, however, be obtained solely from field runoff experiments, as the number of treatment combinations required to account for all relevant farming systems and environmental conditions far exceeds our research capabilities. To facilitate the comparison of P loads, we therefore need reasonably simple models. A key factor controlling the P load from agriculture is the past and present use of nutrients in fertilizers and manure in relation to a crop's uptake, i.e. the soil-surface balance of P. Here, we present a simple empirical model that relates the P surplus (or deficit) in a farm to the edge-of-field losses of algal-available P. Based on long-term fertilizer trials, the model first estimates the change in soil-test P of top soil with the aid of the soil-surface balance of P. Soil-test P is then used to approximate the concentration of dissolved reactive P in surface runoff and drainage flow, as adjusted for different P application types. The loss of particulate P is obtained from typical erosion rates. The model can be applied in life-cycle analyses and in assessing future developments. We illustrate use of the model by calculating the loss of algal-available P from conventional and organic crop and dairy farms located on clay and fine sand soils.     

太湖流域稻田不同氮肥管理模式下的氮素平衡特征及环境效应评价

研究了不同氮肥管理模式下的稻田氮素平衡特征和环境效应.在太湖主要入湖河流直湖港下游开展了农户常规施肥处理、缓控释肥处理、有机无机肥配施处理、按需施肥处理以及化肥减量优化处理5种氮肥管理模式的田间小区试验,实测了稻季的径流和淋洗氮损失,估算了氨挥发和N₂O等气体损失,分析了不同氮肥处理下的环境排放量和氮素平衡特征.与农户常规施肥处理相比,其他处理在减少氮肥总投入量20%～40%的情况下产量与农户对照基本持平,氮肥利用率提高了14.5%～44%.不同氮肥管理模式下,缓控释肥处理和按需施肥处理的氮环境排放量最低,比农户施肥处理分别降低了52.8%和45.4%.在等氮量投入下,有机无机配施处理比纯化肥处理减少了环境氮排放量.农户施肥处理存在着明显的氮盈余,增加了麦季氮流失的风险,按需施肥处理略微出现氮亏缺,在一定程度上减少了麦季氮流失风险.新型缓控释肥处理和按需施肥处理能在不降低产量和效益的情况下,提高氮肥利用率,减少环境排放量,是值得在太湖流域推广的经济环保氮肥管理模式.     

Review of greenhouse gas emissions from crop production systems and fertilizer management effects

Fertilizer nitrogen (N) use is expanding globally to satisfy food, fiber, and fuel demands of a growing world population. Fertilizer consumers are being asked to improve N use efficiency through better management in their fields, to protect water resources and to minimize greenhouse gas (GHG) emissions, while sustaining soil resources and providing a healthy economy. A review of the available science on the effects of N source, rate, timing, and placement, in combination with other cropping and tillage practices, on GHG emissions was conducted. Implementation of intensive crop management practices, using principles of ecological intensification to enhance efficient and effective nutrient uptake while achieving high yields, was identified as a principal way to achieve reductions in GHG emissions while meeting production demands. Many studies identified through the review involved measurements of GHG emissions over several weeks to a few months, which greatly limit the ability to accurately determine system-level management effects on net global warming potential. The current science indicates: (1) appropriate fertilizer N use helps increase biomass production necessary to help restore and maintain soil organic carbon (SOC) levels; (2) best management practices (BMPs) for fertilizer N play a large role in minimizing residual soil nitrate, which helps lower the risk of increased nitrous oxide (N₂O) emissions; (3) tillage practices that reduce soil disturbance and maintain crop residue on the soil surface can increase SOC levels, but usually only if crop productivity is maintained or increased; (4) differences among fertilizer N sources in N₂O emissions depend on site- and weather-specific conditions; and (5) intensive crop management systems do not necessarily increase GHG emissions per unit of crop or food production; they can help spare natural areas from conversion to cropland and allow conversion of selected lands to forests for GHG mitigation, while supplying the world's need for food, fiber, and biofuel. Transfer of the information to fertilizer dealers, crop advisers, farmers, and agricultural and environmental authorities should lead to increased implementation of fertilizer BMPs, and help to reduce confusion over the role of fertilizer N on cropping system emissions of GHGs. Gaps in scientific understanding were identified and will require the collaborative attention of agronomists, soil scientists, ecologists, and environmental authorities in serving the immediate and long-term interests of the human population.     

种植绿肥对作物产量和细菌群落稳定性的影响

为深入研究青海高原地区长期种植绿肥,减施化肥条件下小麦/油菜产量及土壤理化性状及微生物群落的变化,通过2011年建立的定位试验,设GF0（毛苕子作为绿肥,不施用化肥）、GF60（毛叶苕子配施60%化肥）、GF70（毛叶苕子配施70%化肥）、GF80（毛叶苕子配施80%化肥）、GF90（毛叶苕子配施90%化肥）、GF100（毛叶苕子配施100%化肥）、F0（休耕并且不施化肥）、F100（休耕并且施用100%化肥）共8个处理,利用高通量测序等技术,研究了种植利用绿肥减施化肥条件下小麦和油菜的产量、土壤性质和微生物群落结构的变化特征.结果表明,在保证小麦、油菜不减产的基础上,种植绿肥后茬作物减施化肥达到30%左右.绿肥配施减量化肥对土壤肥力有显著的提升作用,特别是土壤有机碳和全氮含量有明显的提高,分别提高1.34%~7.46%、2.16%~7.48%.化肥与绿肥配施增强了土壤微生物群落多样性,其中酸杆菌门和变形菌门是本研究土壤中的优势菌群.共生网络分析表明,绿肥处理提高了细菌群落的稳定性和抗干扰能力,同时绿肥应用增加了细菌群落中的关键物种.本研究表明,不同土壤微生物丰度受种植模式、施肥量影响很大,长期种植绿肥、减施化肥提高了土壤微生物丰度和多样性,增强微生物群落的稳定性.种植绿肥条件下化肥减肥量30%左右保证作物稳产可为当地的施肥管理提供参考.     

Greenhouse gas mitigation with scarce land: The potential contribution of increased nitrogen input

Agricultural lands have been identified to mitigate greenhouse gas (GHG) emissions primarily by production of energy crops and substituting fossil energy resources and through carbon sequestration in soils. Increased fertilizer input resulting in increased yields may reduce the area needed for crop production. The surplus area could be used for energy production without affecting the land use necessary for food and feed production. We built a model to investigate the effect of changing nitrogen (N) fertilizer rates on cropping area required for a given amount of crops. We found that an increase in nitrogen fertilizer supply is only justified if GHG mitigation with additional land is higher than 9–15 t carbon dioxide equivalents per hectare (CO₂-eq._./ha). The mitigation potential of bioenergy production from energy crops is most often not in this range. Hence, from a GHG abatement point of view land should rather be used to produce crops at moderate fertilizer rate than to produce energy crops. This may change if farmers are forced to reduce their N input due to taxes or governmental regulations as it is the case in Denmark. However, with a fertilizer rate 10 % below the economical optimum a reduction of N input is still more effective than the production of bioenergy unless mitigation effect of the bioenergy production exceeds 7 t carbon dioxide (CO₂)-eq._./ha. An intensification of land use in terms of N supply to provide more land for bioenergy production can only in exceptional cases be justified to mitigate GHG emissions with bioenergy under current frame conditions in Germany and Denmark.     

有机肥与无机肥配施对潮土N2O排放的影响

华北平原是我国重要的粮食主产区,由于土壤有机质含量低,增加氮肥用量并不能导致玉米产量持续增加.有机肥和无机肥配施被广泛认为是同时实现粮食增产和提高土壤有机质的双赢措施,但是有机肥和无机肥配施对华北平原农田N₂O排放的影响尚不明确.本研究在华北平原潮土区,通过测定不同种类有机肥与无机肥配施后农田N₂O排放通量和作物产量,旨在揭示不同种类有机肥及其用量对潮土N₂O排放和作物产量的影响效应.田间试验共设置8个处理,分别为不施肥(CK)、化肥氮(NPK)、 40%牛粪氮+60%化肥氮(CM)、 40%鸡粪氮+60%化肥氮(FC)、 40%猪粪氮+60%化肥氮(FP)、 20%牛粪氮+80%化肥氮(1/2CM)、 20%鸡粪氮+80%化肥氮(1/2FC)和20%猪粪氮+80%化肥氮(1/2FP).整个玉米季N₂O排放通量均与土壤WFPS显著正相关(P<0.05).除NPK处理外,玉米季N₂O排放量与土壤可溶性有机碳(DOC)平均含量存在显著的线性关系.玉米季CK处理N_2<...     

基于MEA情景的长江流域氮平衡及溶解态无机氮通量:流域-河口/海湾氮综合管理

以长江流域氮循环为研究对象,基于千年生态系统评估框架下的4种情景,预测了2050年长江流域的氮循环在不同驱动因子作用下的未来变化趋势,并提出长江流域生态系统的优化管理的建议.研究结果表明,在1970—2010年期间,长江流域氮输入量增加了5倍,长江向河口输出的溶解态无机氮(DIN)通量增加了8倍,流域土壤中的氮已经达到饱和并且氮过剩量持续增加,流域对氮的截留率下降,水体输送的DIN通量增加,区域氮循环失衡问题日益严重.在千年生态系统评估框架下,预测在2050年,在采取积极措施的预测情境下,河流向河口和近海输送的溶解态无机氮通量将会比2000年有所下降,而在消极应对的预测情境下,河流向河口和近海输送的溶解态无机氮通量将会继续增加,从而加剧河口和近海地区水体的污染程度.非点源氮输入将是长江溶解态无机氮输出通量的主要来源,其中以化肥氮输入为主,其次为禽畜粪便氮输入,贡献率最低的是点源污水氮输入.情景预测及源解析研究表明,2050年长江流域-河口/海湾氮污染控制的重点在于减少长江下游-太湖流域、沅江-湘江-洞庭湖流域、赣江-鄱阳湖流域及岷江流域的化肥及畜禽粪便排放,2050年要实现长江水系水质全面达标,长江流域的氮输入量需要削减29%,其中长江下游-太湖流域削减40%,汉江流域削减43%,沅江-湘江-洞庭湖流域削减31%.从子流域尺度制定氮污染管理策略更适用于流域-河口/海湾系统框架下的综合管理.     

Life Cycle Assessment of fossil energy use and greenhouse gas emissions in Chinese pear production

A Life Cycle Assessment (LCA) was performed to analyze environmental consequences of different pear production chains in terms of fossil energy use and greenhouse gas (GHG) emission in China. The assessment identified hotspots that contributed significantly to the environmental impacts of pear production from the cradle to the point of sale. The results showed that GHG emissions and fossil energy use varied in the different production chains because the environmental performance does not associate with the farming systems (i.e. organic vs. conventional), but is co-determined by farm topography and thus machinery use, by market demands to seasonality of products and thus the need for storage, and by local farming practices including manure management. The LCA could be used as a tool to guide selections of agricultural inputs with the aim of reducing environmental impacts. The results of the LCA analysis indicate that a list of choices are available to reduce energy use and GHG emission in the pear production chain, namely substitution of the traditional storage systems by an efficiently controlled atmosphere storage system, using manure for biogas production, conversion from the conventional farming to organic farming, and reduction of mechanical cultivation.     

广东省人为源氨排放清单及减排潜力研究

根据各类氨排放源活动水平数据,采用排放因子法,建立了2010年广东省人为源氨排放清单,在分析其排放特征的基础上探讨了氨的减排潜力.结果表明:2010年广东省人为源氨排放量为582.9 kt,畜禽和氮肥施用是排放贡献最大的人为源,分别占总排放量的44.2%和40.4%;茂名、湛江和肇庆依次是排放量最大的3个城市,共占广东省总排放量33.0%;在畜禽源中,肉猪排放量最大,占畜禽源排放总量44.4%,其次是肉鸡、母猪和黄牛,分别占16.0%、15.2%和6.5%;畜禽在畜舍、储存管理、农田施肥和放牧4个养殖阶段的氨排放量不同;控制农业源对NH3的减排起关键性作用,茂名、湛江和肇庆是广东省重点控制的3个城市,肉猪、母猪、肉鸡、黄牛和氮肥施用则为重点控制源,主要控制措施包括低氮饲料喂养、畜舍改造、粪便密封、粪肥注施、延长放牧时间和使用尿素替代物.     

最佳管理措施对非点源污染控制效果的预测——以北京密云县太师屯镇为例

选取北京市密云水库上游太师屯镇为研究区,针对该区农业非点源污染特征,设计了最佳管理措施(BMPs).同时,在非点源污染损失估算的基础上,率先尝试从经济学角度预测8种不同非点源污染措施在控制氮、磷和泥沙流失的效果及所获得的环境效益、经济效益,并将各单项措施的控制效率进行了比较分析.研究结果表明：改变土地利用类型的3种措施中,25°以上荒草坡还林措施效果最好,对总氮、总磷、泥沙流失的控制效果都超过15%,最高可达30%以上,且经济效益最大;25°以上坡耕地还林效果次之,对总氮、总磷、泥沙流失的控制效果都超过5%,最高可达12%;15°~25°坡耕地变果园措施最差,对总氮、总磷、泥沙流失的控制效果一般为4%~8%.坡度为0°~15°坡耕地在土壤侵蚀控制中具有重要地位;坡耕地植物篱和保护性耕作对土壤侵蚀类非点源污染的控制效果相近,削减的污染损失占非点源污染损失总价值的13%,具有明显的环境效益.针对畜禽养殖污染设计的农村户用沼气池,其经济效率在10%左右;测土施肥技术可减少氮素流失、节约大量化肥,且削减的污染损失达到非点源污染损失总价值的19%.作为综合污染控制措施的河岸缓冲带,可以有效地拦截氮、磷和泥沙的流失,对泥沙的控制效果最好,为83%,对氮的控制效果最低,仅为27%;而从经济效益方面比较,缓冲带减少氮素流失所获得的经济效益最大,约为该措施总经济效益的56%,泥沙次之,占28%;植被缓冲带削减非点源污染的总经济效率最高,可达35%,折合经济价值约1.69×106元.