畜禽粪便堆肥过程中氮素的损失与控制

堆肥是实现畜禽粪便处理及资源化利用的有效途径,然而畜禽粪便堆肥过程中氮素损失较严重,对氮素损失与控制的研究可为有效控制氮素损失提供理论基础和实践参考.本文简述了畜禽粪便堆肥过程中氮素转化及主要损失途径,总结了影响堆肥氮素损失的主要因素(包括堆肥物料初始特性、堆肥环境参数和堆肥工艺条件),并综述了氮素损失控制措施(调节C、N代谢,改变氮素形态,添加NH₃吸附剂和调节通风与控温措施)的研究进展,此外,对未来的研究方向进行了展望.     

一株水生产碱杆菌(Alcaligenes aquatilis)的分离鉴定及其氨氧化效果

【背景】随着畜牧业的高速发展,资源化利用畜禽粪便并减少其所造成的污染是一项艰巨的任务。好氧堆肥作为一种有效利用畜禽粪便污染的途径而成为重点研究方向。【目的】通过筛选具有高效氮转化能力的微生物,用于减少好氧堆肥中氮素损失,从而提高肥力、减少污染。【方法】通过对牛粪中异养硝化细菌的分离鉴定及对氨氧化能力的研究得到氨氧化能力较强的菌株NS-1。在不同工艺参数下培养菌株NS-1,进一步研究其氨氧化能力。【结果】通过形态学鉴定及16S rRNA基因序列鉴定,最终确定菌株NS-1为水生产碱杆菌(Alcaligenes aquatilis)。试验结果表明当碳源为丁二酸钠、C/N为15、温度为35℃、pH 7.0时菌株NS-1的氨氧化能力有大幅度提升。菌株NS-1在32 h内将1 230.694 7 mg/L的氨氮完全去除,去除率达到了100%,去除速率高达38.46 mg/(L·h)。【结论】菌株NS-1优良的氨氧化能力对于减少堆肥过程中的氮素流失有重要意义,可为生产优质生物有机肥提供微生物材料和技术支持。     

环境条件对猪粪好氧堆肥过程的影响

禽畜粪便的大量排放给环境造成了巨大污染,其中猪场粪便和污水是最主要的污染源。为了实现猪粪的无害化、减量化和资源化,好氧堆肥是目前普遍应用和效果良好的实用技术。为了探明堆肥过程的生物学和化学过程,论本文主要从几个影响因素如温度、调理剂、含水率、通风方式、微生物菌剂等对猪粪好氧堆肥技术方面进行了综述。     

畜禽粪便中抗生素抗性基因的分布特征及消减技术研究进展

随着集约化畜禽养殖业的不断发展,兽用抗生素的长期使用导致畜禽粪便抗生素抗性基因污染日益严重,对生态环境和人类健康造成严重危害。如何有效消减畜禽粪便中的抗生素抗性基因成为当前研究热点。本文系统总结了畜禽粪便中抗生素抗性基因的产生途径、分布和影响因素,并阐述了好氧堆肥、厌氧消化及其强化工艺消减畜禽粪便抗生素抗性基因的研究进展,根据现有工艺研究存在的问题展望了今后的重点研究方向,为畜禽粪便中抗生素抗性基因的消减提供理论基础和技术支撑。     

中国农田土壤N2O排放通量分布格局研究

中国作为世界上一个重要农业大国,对全球大气中N2O浓度的影响正在引起人们的普遍关注.该研究采用针对农业土壤痕量气体排放估算建立的、基于N2O的产生、传输和消耗机理的反硝化分解(DNDC)模型,在建立了有关中国气候、农业土壤和农业生产的分县数据库基础上,估计了我国各县农业土壤N2O的排放通量,发现我国农田土壤N2O排放通量有较明显的地区差异,西北地区较低,东南地区较高.还发现无论温度升高,还是施肥量变化,对我国农田土壤N2O排放通量的影响,都存在区域差异,表现为东南地区的变化幅度较西北地区大,这可能与我国气候的干湿变化有较密切的关系.     

添加过磷酸钙对蔬菜废弃物堆肥中氨气及温室气体排放的影响

为研究过磷酸钙不同添加量对蔬菜废弃物堆肥过程中氨气和温室气体排放的影响,以生菜的废弃菜叶和玉米秸秆为原料,以过磷酸钙肥料为添加剂,进行了27 d的曝气供氧堆肥,对堆肥过程中的氨挥发和温室气体排放(N2O、CH4和CO2)进行了监测.试验共设6个处理,除CK处理(不添加过磷酸钙)外,其余处理依次根据混合物料初始总氮物质量的5%、10%、15%、20%和25%的比例添加过磷酸钙.结果表明:添加过磷酸钙对减少堆肥过程中的氨挥发和温室气体排放均有明显效果,氨挥发总量较CK减少了4.0%~16.7%,总温室气体CO2排放当量减少了10.2%~20.8%.堆肥过程中排放的NH3对温室效应的贡献相对较大,各处理NH3的CO2排放当量为59.90~81.58 kg·t-1,占4种气体总CO2排放当量的69%~77%.蔬菜废弃物堆肥过程中适量添加过磷酸钙是减少氨挥发和温室气体排放并提高堆肥品质的有效措施.     

微生物在有机固废堆肥中的作用与应用

好氧堆肥是实现有机固体废弃物资源化利用的主流处理方式。堆肥腐熟是一个由微生物主导的生理生化过程,堆料通过微生物发酵实现矿质化、腐殖化和无害化,转变成腐熟的有机肥。传统的好氧堆肥存在发酵周期长、养分损失、恶臭及温室气体排放等不足。在堆肥过程中添加微生物是弥补传统好氧堆肥缺陷、提高堆肥品质和功效的有效方法。近年来,国内外在好氧堆肥过程中主要微生物类群与其演替规律、外源添加微生物的作用与功能等方面取得了较大进展。本文简述好氧堆肥基本过程与主要影响因素,以及这个过程中主要微生物类群与其演替规律,重点介绍有关微生物添加剂在好氧堆肥中的应用及其作用方面的研究进展。同时,我们对目前微生物添加剂在应用中存在的问题进行分析并对解决途径进行探讨。     

垃圾填埋场N_2O排放通量及测定方法研究进展

氧化亚氮(N2O)是第三大温室气体和最主要的臭氧层破坏气体.填埋是目前城市生活垃圾处理处置的主要方式,而垃圾填埋场是N2O的排放源之一.实验室研究和现场测定均表明,生活垃圾填埋场可以有高的N2O释放通量,但不同填埋场测定数据差异很大.目前,对生活垃圾填埋场N2O排放量的原位准确测定以及排放机理和重要性的认识仍有很多不足.本文概述了生活垃圾填埋场N2O排放研究现状,从垃圾堆体和覆土层两部分探讨了传统厌氧卫生填埋场的N2O产生和排放机理,并就此对新型脱氮型生物反应器填埋场做了相应探讨.最后,就静态箱法、涡度相关法等N2O通量测定方法在填埋场的适用性进行了讨论,并展望了填埋场N2O排放的研究方向.     

浮床植物净化生活污水中N、P的效果及N2O的排放

在温室内采用浮床无土栽培技术,研究了黑麦草(Lolium mutliflorum)、水芹(Oenanthe javanica)和香根草(Vetiveria Zizanioides)3种植物对生活污水中N、P的去除效果及净化过程中N2O的排放特征。结果表明,浮床植物系统对生活污水的TN、NH4 -N和TP具有良好的净化效果。同对照系统相比,浮床黑麦草、水芹和香根草系统对TN的平均去除率分别提高了26.2%,22.9%,4.1%;对NH4 -N的去除率分别提高了31.4%,14.5%,3.0%;对TP去除率分别提高了33.1%,54.2%,15.5%。净化周期内,浮床各系统的TN、NH4 -N和TP浓度随着污水停留时间的延长直线下降,而NO3-N浓度却因系统内硝化强度大于反硝化强度而产生了累积;植物的存在明显的促进了浮床系统的N2O排放,浮床黑麦草、水芹、香根草和对照系统N2O的平均排放通量分别为174.44μg/(m2.h),82.19μg/(m2.h),112.49μg/(m2.h)和44.81μg/(m2.h)。浮床系统N2O排放通量的日变化呈现出夜间下降而白天增加的规律,与温度的昼夜变化规律基本相同,表明温度的升降直接影响了N2O的生成及排放。     

好氧反硝化微生物学机理与应用研究进展

近年来,关于好氧反硝化过程的研究主要集中在三个方面:分别是好氧反硝化菌株的分离和脱氮性能表征,好氧反硝化微生物的应用潜力分析,以及好氧反硝化过程的机理研究。好氧反硝化菌株分布范围广泛,可从多种环境中分离得到,种属以Pseudomonas sp.、Alcaligenes sp.和Paracoccus sp.为主。好氧反硝化菌株及菌群在实验室条件下表现出优良的耐冷、耐盐特性,并具有可降解毒性有机物及N_2O减排的潜力。关于好氧反硝化过程的机理研究表明,虽然硝酸盐作为电子受体的竞争力比氧气弱,但反硝化作为辅助电子传递途径,可提高产能效率,防止NAD(P)H的过量积累。因此,硝酸盐可与氧气同时参与微生物的新陈代谢,即发生好氧反硝化现象。未来除了继续分离更新更好的好氧反硝化菌株外,应加强对好氧反硝化机理及实际生物强化方面的研究。     

Patterns and quantities of NH(3), N(2)O and CH(4) emissions during swine manure composting without forced aeration--effect of compost pile scale

To evaluate the NH(3), N(2)O, and CH(4) emissions from composting of livestock waste without forced aeration in turned piles, and to investigate the possible relationship between the scale of the compost pile and gas emission rates, we conducted swine manure composting experiments in parallel on small- and large-scale compost piles. Continuous measurements of gas emissions during composting were carried out using a chamber system, and detailed gas emission patterns were obtained. The total amount of each gas emission was computed from the amount of ventilation and gas concentration. NH(3) emission was observed in the early period of composting when the material was at a high temperature. Sharp peaks in CH(4) emission occurred immediately after swine manure was piled up, although a high emissions level continued after the first turning only in the large-scale pile. N(2)O emissions started around the middle stage of the composting period when NH(3) emissions and the temperature of the compost material began to decline. The emission rates of each gas in the small and large piles were 112.8 and 127.4 g NH(3)-N/kg T-N, 37.2 and 46.5 g N(2)O-N/kg T-N, and 1.0 and 1.9 g CH(4)/kg OM, respectively. It was found that changing the piling scale of the compost material was a major factor in gas emission rates.     

Prevention and control of losses of gaseous nitrogen compounds in livestock operations: a review

Nitrogen (N) losses from livestock houses and manure storage facilities contribute greatly to the total loss of N from livestock farms. Volatilisation of ammonia (NH3) is the major process responsible for the loss of N in husbandry systems with slurry (where average dry matter content varies between 3 and 13%). Concerning this volatilisation of NH3, the process parameters of pH and air temperature are crucial. During a period of approximately 10 years, systematic measurements of NH3 losses originating from a large variety of different livestock houses were made. One of the problems with NH3 emissions is the large variation in the measured data due to the season, the production of the animals, the manure treatment, type of livestock house, and the manure storage. Generally speaking, prevention and control of NH3 emission can be done by control of N content in the manure, moisture content, pH, and temperature. In houses for growing pigs, a combination of simple housing measures can be taken to greatly reduce NH3 emissions. In houses for laying hens, the control of the manure drying process determines the emission of NH3. Monteny has built an NH3 production model with separate modules for the emission of the manure storage under the dairy house and the floor in the house. Manure spreading is also a major source of NH3 emission and is dependent on slurry composition, environmental conditions, and farm management. The effects of these factors have been employed in a model. Losses via NO, N2O, and N2 are important in husbandry systems with solid manure and straw. The number of experimental data is, however, very limited. As N2O is an intermediate product of complex biochemical processes of nitrification and denitrification, optimal conditions are the key issues in N2O reduction strategies. We may expect that in the near future the emission of greenhouse gases will get the same attention from policy makers as NH3. Sustainable livestock production has to combine low emissions of gaseous N compounds with acceptable odour emissions, low emissions of greenhouse gases, and acceptable standards of animal welfare. For the entrepreneur, the strategy must be built on the regulations, the special conditions of his farm, and what is reasonably achievable.     

堆肥化处理对畜禽粪便中四环素类抗生素及抗性基因控制的研究进展

随着四环素类抗生素在畜禽养殖中的广泛应用,畜禽粪便已成为四环素类抗生素和抗性基因的重要富集位点,其未经处理直接施用具有潜在的生态环境和人类健康风险。堆肥化处理可有效消减畜禽粪便中的四环素类抗生素,并且对抗性基因的扩散和传播具有一定的控制效果。本综述比较了不同的堆肥化工艺对粪肥中四环素类抗生素消减的效果,并重点讨论了其微生物降解机理,总结了堆肥化处理对粪肥中四环素抗性基因消减的研究进展,进一步讨论了堆肥化处理过程中抗性基因变化的微生态机理与控制策略,最后提出了采用热水解等预处理工艺去除抗生素压力和采用厌氧堆肥化工艺增强抗性基因控制的技术建议,以及从动态的角度采用高通量的检测技术来解析抗性基因消减机制的研究策略建议。     

Effect of turning regime and seasonal weather conditions on nitrogen and phosphorus losses during aerobic composting of cattle manure

Cattle manure from stock bedded on straw was aerobically composted under ambient conditions, turning with either a tractor-mounted front-end loader or a rear discharge manure spreader. Three composting experiments, each of approximately four months duration, were conducted to investigate the effect of turning regime and seasonal weather conditions on nitrogen and phosphorus losses during aerobic composting of cattle manure. Manure stacks of 12-15 m(3) initial volume were constructed in separate 5 x 5 m concrete compartments. Experiment 1 (January-April 1999) compared manure heaps turned once (T1) or three times (T3) using a front-end loader with an unturned static (S) control manure stack. Experiment 2 (June-September 1999) compared the same treatments as Experiment 1. Experiment 3 (September-December 1999) compared T1 and T3 turning regimes using a front end loader with turning by a rear-discharge spreader (TR1 and TR1T2) for more effective aeration of the manure. Turning took place at 6 weeks for the one turn treatments, and after 2, 6 and 10 weeks for the three turn treatments. Leachate losses were dominated by NH(4)-N during the first three weeks of composting, after which time NH4-N and NO3-N concentrations in leachates were approximately the same, in the range 0-20 mg N l(-1). The concentrations of both NH4-N and NO3-N in leachate were higher after turning. Molybdate-reactive P concentrations in leachate tended not to be significantly influenced by turning regime. Gaseous losses of NH3 and N2O rose quickly during the initial phases of composting, peaking at 152 g N t(-1) d(-1) for the T3 treatment. Mean NH3 emission rate (25-252 g N t(-1) d(-1)) for the first two weeks of Experiment 2 conducted during the period June-September were an order of magnitude greater (1-10 g N t(-1) d(-1)) than Experiment 3, conducted during the colder, wetter autumn period (September-December). Nitrous oxide emission rates ranged between 1-14 g N t(-1) d(-1) and showed little influence of turning regime. Total N and P concentrations in turned (T) and static (S) manure were elevated at the end of all experiments, due to loss of dry matter. Mean total N losses were 30.4% (T1) and 36.8% (T3) and total P losses 28.2% (T1) and 27.4% (T3).     

Chrysomya megacephala larvae feeding favourably influences manure microbiome,heavy metal stability and greenhouse gas emissions

Chrysomya megacephala is a saprophagous fly whose larvae can compost manure and yield biomass and bio‐fertilizer simultaneously. However, there are concerns for the safety of the composting system, that is risk of diseases spread by way of manure pathogens, residue of harmful metals and emission of greenhouse gases. Microbiota analysis and heavy metal speciation by European Communities Bureau of Reference were evaluated in raw, C. megacephala‐composted and natural stacked swine manure to survey pathogenic bacterial changes and mobility of lead and cadmium in manure after C. megacephala feeding; the emission rate of CH₄ and N₂O from manure during C. megacephala composting and natural stacking was also measured. C. megacephala composting altered manure microbiota, reduced the risk of pathogenic bacteria and maintained the stability, and microbiota changes might be associated with heavy metal fractions, especially in Pseudomonas and Prevotella. In addition, C. megacephala‐composting significantly reduced the emission rate of CH₄ and N₂O in comparing with natural stacking situation and the first two days should be the crucial period for CH₄ and N₂O emission measurement for manure treatment by C. megacephala. Moreover, OTU26 and Betaproteobacteria were changed after C. megacephala composting which might play a role in emission of CH₄ and N₂O, respectively.     

垃圾填埋场氧化亚氮排放控制研究进展

填埋是国内外城市生活垃圾处理的一种主要方式.垃圾填埋场是温室气体氧化亚氮(N2O)和甲烷(CH4)的重要排放源.作为一种高效痕量的温室气体,N2O具有极高的潜在增温效应,其每分子潜在的增温作用是二氧化碳(CO2)的296倍.而且N2O能在大气中长期稳定存在,对臭氧层具有较强的破坏作用.本文针对垃圾填埋场N2O排放的控制研究,概述了垃圾填埋处理过程中主要排放源的N2O排放及其影响因素,提出了现阶段适应我国垃圾填埋场N2O排放控制的一系列措施,并展望了垃圾填埋场温室气体N2O排放控制理论和技术的研究方向.     

Allantoin-N concentration changes and analysis of the influencing factors on its changes during different manure composting

Allantoin is one of important nitrogenous compounds in manure. In this study, the simulation experiment of aerobic composting was adopted to explore concentration changes, degradation and relevant influencing factors of allantoin-N during six manure composting. The result showed that the allantoin-N concentration was markedly different among different manures. The various livestock and poultry excreted 1.92-11.14gkg(-1) allantoin-N which accounted for 9.98-32.27% of the total excreted nitrogen. The changing trend of the allantoin-N concentration firstly increased (for 0-14 days), then decreased (for 14-70 days) during different manure composting, and the allantoin-N concentration after composting was lower than the initial allantoin-N concentration in all manure composting. During allantoin degradation for 14-70 days of composting, the half-life of allantoin-N was 57.76 days in broiler manure, 46.21 days in layer-hen manure, 27.73 days in hog manure, 25.67 days in sow manure, 38.51 days in young pig manure and 15.75 days in dairy manure, and the sequence in the half-life was chicken manure>pig manure>dairy manure. Allantoin degradation conformed to first-order kinetics. Through the correlation analysis, hippuric acid, hydrolyzable nitrogen, amino acid-nitrogen, HUN fraction, NO(3)(-)-N and total hydrolyzable nitrogen could be closely related to allantoin-N transforming during composting. Humification could be the main influencing factor for reducing allantoin-N concentration during composting.     

Microbiology of nitrogen cycle in animal manure compost

Composting is the major technology in the treatment of animal manure and is a source of nitrous oxide, a greenhouse gas. Although the microbiological processes of both nitrification and denitrification are involved in composting, the key players in these pathways have not been well identified. Recent molecular microbiological methodologies have revealed the presence of dominant Bacillus species in the degradation of organic material or betaproteobacterial ammonia‐oxidizing bacteria on nitrification on the surface, and have also revealed the mechanism of nitrous oxide emission in this complicated process to some extent. Some bacteria, archaea or fungi still would be considered potential key players, and the contribution of some pathways, such as nitrifier denitrification or heterotrophic nitrification, might be involved in composting. This review article discusses these potential microbial players in nitrification–denitrification within the composting pile and highlights the relevant unknowns through recent activities that focus on the nitrogen cycle within the animal manure composting process.     

过量施肥对设施菜田土壤菌群结构及N2O产生的影响

【背景】N_2O是一种很强的温室气体,其温室效应强度大约是CO_2的265倍。土壤氮肥施加量是影响N_2O排放的重要因素,而厌氧条件下微生物反硝化则是N_2O产生的重要途径。【目的】研究过量施肥条件下蔬菜大棚土壤菌群结构变化及其对N_2O气体排放的影响。【方法】利用自动化培养与实时气体检测系统(Robot)监测土壤厌氧培养过程中N_2O和N_2排放通量,比较过量施肥和减氮施肥模式下土壤N_2O排放模式的差异。通过Illumina二代测序平台对这2种不同施肥处理的土壤微生物群落进行高通量测序,研究不同施肥量对土壤菌群组成的影响。【结果】过量施肥土壤中硝酸盐的含量大约是减氮施肥土壤的2倍,通过添加硝酸盐使2种土壤的硝酸盐含量均为60 mg/kg或为200 mg/kg时,过量施肥土壤在厌氧培养前期N_2O气体的产生量及产生速度都明显高于减氮施肥土壤。另外,过量施肥导致土壤菌群结构发生显著改变,并且降低了土壤微生物的多样性。相对于减氮施肥,过量施肥方式富集了Rhodanobacter属的微生物。PICRUSt预测结果显示,传统施肥没有显著改变反硝化功能基因相对丰度。【结论】长期过量氮肥施用显著增加了土壤N_2O的排放,可能原因是施肥改变了包括氮转化相关微生物在内的土壤菌群组成,从而影响了土壤N_2O气体的形成与还原过程。