微生物菌剂对油枯堆肥过程中理化性质的影响研究

以油枯为基本原料,采用好氧堆肥方式进行堆肥试验,研究了添加4种不同微生物菌剂的条件下,油枯-稻壳-甘蔗渣堆肥体系中pH、C/N、水溶性NO3--N、水溶性NH4＋-N中的动态变化规律及菌剂对高温堆肥腐熟进程的影响。结果表明,添加菌剂能有效缩短堆肥到达高温的时间,延长高温分解阶段,加快物料水溶性NH4＋-N和C/N降低,pH和水溶性NO3--N含量升高,加快了油枯堆肥腐熟化进程。添加VT菌剂的堆肥处理相比其他在堆肥15d后最先进入高温分解阶段,高温持续时间为10d,提早5d腐熟,水溶性NO3--N含量从71.41mg.kg-1增加到887.4mg.kg-1,C/N的降低有效促进了NH4＋-N向NO3--N的转化,加快了油枯堆肥化进程,有助于提高堆肥腐熟化程度,说明添加VT菌剂的堆肥腐熟效果相对显著。     

餐厨垃圾与菌糠混合好氧堆肥效果

分别使用玉米秸秆与菌糠作为餐厨垃圾的堆肥调理剂,进行堆肥1次发酵对比试验,旨在考察菌糠作为餐厨垃圾堆肥调理剂的可行性。通过对2种调理剂与餐厨垃圾堆肥过程中理化性质及腐熟度变化的分析,表明餐厨垃圾好氧堆肥时,菌糠是一种优于玉米秸秆的良好调理剂,餐厨垃圾与菌糠混合堆肥时升温速度快、高温期持续时间长,含水率与有机质分别下降19.6%和20.2%。同时,其混合堆料在堆肥过程中散发臭气较少,1次堆肥处理后发芽指数较高（55.6%）,基本实现腐熟。     

不同调理剂对牛粪好氧堆肥的影响

养殖业的发展造成了周边环境的严重污染。好氧堆肥技术是处理固体有机废弃物的一种有效方法。该文利用自制发酵箱进行了牛粪与不同调理剂-玉米芯、玉米秸秆和稻草的混合好氧堆肥试验。试验结果表明，当堆肥底料的初始碳氮比为27：1，初始含水率为65%时，玉米芯、玉米秸杆和稻草均可作为调理剂与牛粪进行好氧堆肥，且可达到无害化要求。而采用粒径大、多孔、疏松的玉米芯作为调理剂，有利于通风供氧，堆体升温和降温均较快，高温持续时间长，堆料腐熟快，有利于加快堆肥的进程。     

不同调理剂对牛粪好氧堆肥的影响

养殖业的发展造成了周边环境的严重污染。好氧堆肥技术是处理固体有机废弃物的一种有效方法。该文利用自制发酵箱进行了牛粪与不同调理剂一玉米芯、玉米秸秆和稻草的混合好氧堆肥试验。试验结果表明,当堆肥底料的初始碳氮比为27:1,初始含水率为65％时,玉米芯、玉米秸杆和稻草均可作为调理剂与牛粪进行好氧堆肥,且可达到无害化要求。而采用粒径大、多孔、疏松的玉米芯作为调理剂,有利于通风供氧,堆体升温和降温均较快,高温持续时间长,堆料腐熟快,有利于加快堆肥的进程。     

条垛堆肥 -蚯蚓堆肥联合处理对堆肥产品性状的影响

蚯蚓粪逐渐成为一种优质的有机肥,然而蚯蚓处理对有机肥属性影响的机制和过程并不清楚。本文选用Rw发酵菌对牛粪和蘑菇渣先进行高温好氧堆肥预处理,然后接种蚯蚓,监测了蚯蚓处理前后堆肥中关键质量属性的变化。结果表明:联合堆肥温度、NH4+-N含量、NH4+-N/NO3--N、T值、pH值、EC值、种子发芽指数均符合堆肥腐熟要求。联合堆肥显著提高了全磷含量、NO3--N含量(P0.05),增幅分别达到16.8%、1 286.1%;显著降低了有机质含量、全钾含量、pH值、EC值(P0.05),分别降低35.9%、77.4%、12.6%、56.1%;但未显著降低NH4+-N含量、全氮含量;显著提高了堆肥的品质,如T值从0.64降低到0.58,种子发芽指数从82.6%提高到90.6%(P0.05)。     

尿素作为补充氮源对西番莲果渣高温堆肥进程的影响

利用西番莲废果渣为基本原料进行堆肥试验,研究了添加尿素及2种微生物菌剂（榕风与福贝）在西番莲果渣堆肥过程中温度、C/N比、总氮（T-N）、水溶性NH4＋-N和水溶性NO3--N的动态变化规律。结果表明,加入一定比例的尿素能够增加高温堆肥中〉50℃的高温持续时间、减少最后达到环境温度所需时间;加快堆肥NH4＋-N的下降,促进堆肥化腐熟后期NO3--N的累积,增加腐熟后全氮的含量,加快堆肥化进程。在添加尿素的基础上,添加微生物菌剂,显著加快果渣堆肥中C/N比的下降速度,促进堆肥腐熟进程的作用效果更明显,但两种微生物菌剂之间对堆肥化的促进作用效果无显著差异。     

含水率对羊粪堆肥腐熟度及污染气体排放的影响

为了优化羊粪好氧堆肥的工艺条件，研究初始含水率对羊粪堆肥腐熟度及污染气体排放的影响。本文以高湿新鲜羊粪为堆肥原料（含水率为75%），添加玉米秸秆调节初始物料含水率分别为70%、65%、60%和55%，堆肥在60 L密闭发酵罐中共持续35 d。结果表明：75%含水率羊粪堆体单独不能顺利启动升温，且在试验期间释放了大量的甲烷和氧化亚氮等温室气体，在所有处理中产生的总温室效应最大（41.4 g/kg）。玉米秸秆与羊粪联合均能成功启动堆肥过程，且堆肥产品均可以达到无害化卫生要求和腐熟标准。其中初始含水率为65%时，堆体不仅高温期持续时间长，且有机质降解程度高，物料干质量降解率达45%，同时比其他处理可降低4.81%～16.99%的总氮损失和7.56%～48.62%的总温室气体排放量。因此，在羊粪和玉米秸秆联合堆肥时，初始含水率65%左右为最佳条件。     

绿化植物废弃物和污泥的堆肥特性研究

绿化植物废弃物和污泥不同比例的堆肥实验显示其质量比为5∶4时堆肥升温快,高温持续时间最长;全碳和全氮含量在堆肥14 d后都有明显的降低;NO3--N的含量变化不大;NH4+-N的含量降低;堆肥的富里酸(FA)快速降低,胡敏酸(HA)先略有降低,然后快速增加;而种子发芽指数在14 d后均超过了0.8;最终腐殖质化参数(HI)为2.71,腐殖化速率(HR)为14.87%,CFA/CO=10.8;重金属的含量符合相关堆肥标准要求。绿化植物废弃物的高木质素含量决定了C/N、T值(终点C/N)/(初始C/N)、NH4+-N/NO3--N不宜作为其腐熟评价指标,但温度、NO3--N和NH4+-N、腐殖化参数、种子发芽指数可作为绿化植物废弃物和污泥混合堆肥的腐熟评价指标。绿化植物废弃物和污泥混合堆肥效果取决于污泥的添加量,含水量高的污泥用量过多会影响堆肥效果。绿化植物废弃物和污泥综合利用对控制堆肥质量,提高废弃物综合利用,促进城市节能减排有重要意义。     

猪粪比例对烟草废弃物高温堆肥腐熟进程的影响

以烟草废弃物为基本原料进行堆肥试验,研究了不同比例猪粪与烟草废弃物混合堆肥体系中温度、pH、全氮、C/N比、水溶性NH＋4-N和种子发芽指数（GI,germination index）的动态变化规律,探讨了不同猪粪比例对烟草废弃物高温堆肥腐熟进程的影响。结果表明,在烟草废弃物中加入猪粪能缩短进入高温分解阶段的时间,增加高温分解持续时间,增加全氮含量,加快物料NH＋4-N和C/N比降低的速率,加快烟草废弃物堆肥腐熟化进程。添加一定比例猪粪的处理（烟草废弃物∶猪粪=7∶3、烟草废弃物∶猪粪=8∶2和烟草废弃物∶猪粪=9∶1）,分别在堆肥第3、4、5 d进入高温分解阶段（〉50 ℃）,高温持续时间分别为11、10、8 d;而纯烟草废弃物处理,最高温度为43 ℃,未进入高温分解阶段;至堆肥26 d,NH＋4-N含量分别比纯烟草废弃物对照降低47.7%、61.9%和25.6%;GI分别达到81.4%、84.1%和83.7%。     

生物质炭对蔬菜废弃物堆肥化过程氮素转化的影响

为了研究添加生物质炭对蔬菜废弃物堆肥化处理过程中氮素转化特征的影响,分析堆肥过程中氮素的转化及损失规律,用西红柿茎蔓、玉米秸秆和猪粪按一定比例混合后添加不同比例的生物质炭,进行了为期30 d的堆肥发酵试验。结果表明,添加生物质炭能够提高堆体温度,使堆体快速进入高温期,延长高温持续时间,可降低挥发性氨的累积释放量,减少堆肥过程中的氮素损失,从而提高堆肥产品全氮的含量,并可促进堆肥后期NH+4-N向NO-3-N转化,提高非酸水解态氮的含量。添加生物质炭有利于堆肥的腐熟,在堆肥第18 d添加较高比例的生物质炭的处理其NH+4-N/NO-3-N≤0.5,堆肥产品达到腐熟。综合保氮和腐熟效果,蔬菜废弃物在堆肥化过程中以添加10%的生物质炭为最佳。     

Mass and Nutrient Losses During the Composting Of Dairy Manure Amended with Sawdust or Straw

Composting has become an increasingly popular manure management method for dairy farmers. However, the design of composting systems for farmers has been hindered by the limited amount of information on the quantities and volumes of compost produced relative to farm size and manure generated, and the impact of amendments on water, dry matter, volume and nitrogen losses during the composting process. Amendment type can affect the free air space, decomposition rate, temperature, C:N ratio and oxygen levels during composting. Amendments also initially increase the amount of material that must be handled. A better understanding of amendment effects should help farmers optimize, and potentially reduce costs associated with composting. In this study, freestall dairy manure (83% moisture) was amended with either hardwood sawdust or straw and composted for 110-155 days in turned windrows in four replicated trials that began on different dates. Initial C:N ratios of the windrows ranged from 25:1 to 50:1 due to variations in the source and N-content of the manure. Results showed that starting windrow volume for straw amended composts was 2.1 to 2.6 times greater than for sawdust amendment. Straw amended composts had low initial bulk densities with high free air space values of 75-93%. This led to lower temperatures and near ambient interstitial oxygen concentrations during composting. While all sawdust-amended composts self-heated to temperatures >55°C within 10 days, maintained these levels for more than 60 days and met EPA and USDA pathogen reduction guidelines, only two of the four straw amended windrows reached 55°C and none met the guidelines. In addition, sawdust amendment resulted in much lower windrow oxygen concentrations (< 5%) during the first 60 days. Both types of compost were stable after 100 days as indicated by CO₂ evolution rates <0.5 mg CO₂-C/g VS/d. Both types of amendments also led to extensive manure volume and weight reductions even after the weight of the added amendments were considered. However, moisture management proved critical in attaining reductions in manure weight during composting. Straw amendment resulted in greater volume decreases than sawdust amendment due to greater changes in bulk density and free air space. Through composting, farmers can reduce the volume and weights of material to be hauled by 50 to 80% based on equivalent nitrogen values of the stabilized compost as compared to unamended, uncomposted dairy manure. The initial total manure nitrogen lost during composting ranged from 7% to 38%. P and K losses were from 14 to 39% and from 1 to 38%, respectively. There was a significant negative correlation between C:N ratio and nitrogen loss (R₂=0.78) and carbon loss (R₂=0.86) during composting. An initial C:N ratio of greater than 40 is recommended to minimize nitrogen loss during dairy manure composting with sawdust or straw amendments.     

Application rate and composting method affect the immediate and residual manure fertilizer value in a maize–rice–rice–maize cropping sequence on a degraded soil in northern Vietnam

A field experiment was carried out in northern Vietnam to investigate the effects of adding different additives [rice (Oriza sativa L.) straw only, or rice straw with added lime, superphosphate (SSP), urea or a mixture of selected microorganism species] on nitrogen (N) losses and nutrient concentrations in manure composts. The composts and fresh manure were applied to a three-crop per year sequence (maize–rice–rice) on a degraded soil (Plinthic Acrisol/Plinthaquult) to investigate the effects of manure type on crop yield, N uptake and fertilizer value. Total N losses during composting with SSP were 20% of initial total N, while with other additives they were 30–35%. With SSP as a compost additive, 65–85% of the initial ammonium-N (NH₄-N) in the manure remained in the compost compared with 25% for microorganisms and 30% for lime. Nitrogen uptake efficiency (NUE) of fresh manure was lower than that of composted manure when applied to maize (Zea mays L.), but higher when applied to rice (Oriza sativa L.). The NUE of compost with SSP was generally higher than that of compost with straw only and lime. The mineral fertilizer equivalent (MFE) of manure types for maize decreased in the order: manure composted with SSP?>?manure composted with straw only and fresh manure?>?manure composted with lime. For rice, the corresponding order was: fresh manure?>?manure composted with SSP/microorganisms/urea?>?manure composted with lime/with straw alone. The MFE was higher when 5 tons manure ha^?1 were applied than when 10 tons manure ha^?1 were applied throughout the crop sequence. The residual effect of composted manures (determined in a fourth crop, with no manure applied) was generally 50% higher than that of fresh manure after one year of manure and compost application. Thus, addition of SSP during composting improved the field fertilizer value of composted pig manure the most.     

秸秆对猪粪静态兼性堆肥无害化和腐熟度的影响

为促进猪粪静态兼性堆肥产品无害化和腐熟,通过添加玉米秸秆调控堆体物理结构特性和碳氮比,采用传统自然发酵方式进行为期90d的静态兼性堆肥试验,分别设置纯猪粪处理(P)和秸秆调控处理(PC)研究静态兼性堆肥过程腐熟度指标、粪大肠菌群以及微生物群落结构演变特征。结果表明,秸秆调控增加了堆体孔隙率(提高19.41%),促进氧气向堆体内部扩散,增强了好氧微生物对有机质的降解,降低NH₄⁺-N,可溶性有机氮(dissolved total nitrogen, DTN)等植物毒性物质含量,提升了堆肥腐熟度,两组处理堆肥产品种子发芽指数分别为40.84%(P)和114.60%(PC)。静态兼性堆肥经过30～40 d自然发酵后,粪大肠菌群数量达到卫生安全标准,堆体温度、NH₄⁺-N和有机酸含量均会影响粪大肠杆菌的活性。堆体中微生物以厚壁菌门、放线菌门、变形菌门等与木质纤维素降解相关的菌门为优势菌门,堆体自上而下由好氧菌属演替为厌氧菌属,并形成好氧、兼性、厌氧的微生物分层。秸秆调控增加了堆体的好氧区域,促进和提高了猪粪...     

不同C/N下鸡粪麦秸高温堆肥腐熟过程研究

用鸡粪与小麦秸秆为堆肥原料进行高温好氧堆肥试验,研究添加鸡粪对小麦秸秆高温好氧堆肥过程中堆体温度、pH值、碳氮比和养分等理化指标的影响,寻求鸡粪与小麦秸秆高温堆肥的最佳配比,为农作物秸秆快速资源化利用提供科学依据和技术指导。结果表明,鸡粪与小麦秸秆在C/N=25时堆体达到的温度最高,为62℃,达到最高温度所需的时间最短,为2 d。堆肥过程中各处理pH值变化基本一致,都是先上升后下降的过程。堆肥结束时A2处理C/N=14.4,NH4＋-N含量比最高时降低了76.2%,腐殖质比初始增加了50.2%,胡敏酸相对于最低点升高了160%,富里酸与堆肥前相比降低57.1%。堆肥结束时,全氮含量除A1处理有所降低外,其余处理均有所增加。各处理堆肥全磷、全钾、速效磷和速效钾含量在堆肥结束时比堆肥初始均有所增加。综合判断,鸡粪与小麦秸秆C/N=25进行堆肥较为适宜。     

牛粪堆肥化中氮素形态与微生物生理群的动态变化和耦合关系

在强制通风静态垛装置中研究了牛粪堆肥化中氮素形态和微生物生理群的动态变化。在堆制的56d里,根据堆温变化分阶段采集堆肥样品,测定各种氮素组分的含量和氮素微生物生理群的数量。结果表明,堆肥过程中,总氮减少了21．6％;有机氮是堆肥中的主要氮素形态,其含量降低了19．1％;氨基酸态氮和氨态氮的含量分别降低了20．9％和86．4％,在有机氮和总氮中的比例分别降低了2．2％和5．2％;氨基糖态氮和硝态氮含量分别增加了147％和79％,在有机氮和总氮中的比例分别增加了2倍和1．3倍。氨气的挥发占总损失的63％,高温期的释放量占总挥发量的69％。堆肥中氨化细菌数量较高,在高温期大幅度增加,其数量变化与堆肥中氨气和氨态氮含量都呈极显著正相关关系。在堆肥过程中,硝化细菌数量总体较小,在降温期增加幅度较大;反硝化细菌数量逐渐增加,堆制结束时达到堆肥初期的2．45倍;固氮菌数量总体增加1．8倍,其中降温期数量较多。堆肥过程中存在的反硝化作用,是氮素损失的另一个重要原因。     

Maturity indices for composted dairy and pig manures

Bulking agents and bedding materials used on farms for composting manures affect the time required for composts to mature. The effects of these materials on guidelines for the use of composted manures in potting mixes are not fully known. Several chemical and biological compost characteristics were mentioned and a cucumber plant growth greenhouse bioassay was performed on samples removed from windrows during composting of: (i) dairy manure amended with wheat straw; (ii) dairy manure amended with sawdust (mostly Quercus spp.); and (iii) pig manure amended with sawdust and shredded wood (mostly Quercus spp.). Dry weights of cucumber seedlings grown in fertilized and unfertilized potting mixes amended with composts (30%, v/v) having stability values of <1 mg CO₂-C g^-1 dw d⁻¹, did not differ significantly from those in a control peat mix. Only the most mature dairy manure-wheat straw compost samples consistently established sufficient N concentrations in cucumber shoots in unfertilized treatments. For the dairy manure-wheat straw compost, all possible subset regression analyses of compost characteristics versus cucumber plant dry weight revealed that any of several compost characteristics (electrical conductivity-EC, compost age, total N, organic C, C-to-N ratio, ash content, CO₂ respirometry, Solvita CO₂ index and the Solvita^® Compost Maturity Index) predicted growth of cucumber in the unfertilized treatments, and thus maturity. In contrast, at least two characteristics of the dairy manure-sawdust compost were required to predict growth of cucumber in the unfertilized treatments. Effective combinations were EC with compost age and the Solvita^® maturity index with total N. Even five compost characteristics did not satisfactorily predict growth of cucumber in the non-fertilized pig manure-wood compost. Nutrient analysis of cucumber shoots indicated N availability was the principal factor limiting growth in potting mixes amended with the dairy manure-sawdust compost, and even more so in the pig manure-wood compost even though the compost had been stabilized to a high degree (<1 mg CO₂-C g⁻¹ dw d⁻¹). Maturity of the composted manures, which implies a positive initial plant growth response of plants grown without fertilization, could not be predicted by compost characteristics alone unless the bulking agent or bedding type used for the production of the composts was also considered.     

促腐剂在鸡粪堆肥发酵中的应用研究

选用鸡粪和小麦秸秆为原料进行高温好氧堆肥,研究促腐剂在鸡粪堆肥发酵中的应用。结果表明,接种促腐剂可迅速提高堆肥初期的发酵温度,最高温度超过70℃,但发酵后期降温快,高温加快了堆肥的发酵。发酵20d种子发芽指数达到80%以上;发酵30d含氮量比对照高4.3%,含水量降低3个百分点。综合堆温、C/N、种子发芽指数各项腐熟度指标,接种促腐剂可使鸡粪堆肥腐熟时间比对照提前5d以上。接种促腐剂可降低物料对种子发芽指数的影响,显著缩短发酵时间,加快堆肥物料的水分挥发,使堆肥中的无机营养成分含量相对增加,从而提高鸡粪堆肥的质量。     

Passively Aerated Composting of Straw-Rich Pig Manure: Effect of Compost Bed Porosity

Straw-rich manure from organic pig farming systems can be composted in passively aerated systems as the high application of straw results in a compost bed with good structure and porosity. The passively aerated composting process was simulated in one-dimensional reactors of 2 m³ for straw-rich manure with compost bed densities of 1100, 700 and 560 kg m^?3. Temperature profiles over the reactor height were monitored online and ammonia emissions were measured periodically. The composition of the compost bed over the reactor height was determined at the end of the composting process. The composting process strongly depends on the density of the compost bed. At a density of 1100 kg.m^?3, the porosity of the bed is too low to initiate natural convection, and aerobic degradation fails and anaerobic conditions may lead to emissions of methane and odorous compounds. At a density of 560 kg.m^?3, the porosity of the bed is high and the high rate of natural convection will keep the temperature low thereby preventing the removal of pathogens and weeds. Best results were observed at a density of 700 kg.m^?3 for which aerobic degradation and drying were adequate and temperatures were high enough to kill pathogens and weeds. On basis of the Ergun equation, which describes the airflow in porous media with internal heat generation, this corresponds to a compost bed permeability of 7×10^?8 m². It was also shown that it is possible to compost animal manures with a low C/N ratio without significant emissions of ammonia. This can be established by trapping the initial ammonia emissions in a straw filter, which is placed on top of the compost bed. Ammonia absorbed in the straw filter and in the compost bed were removed by nitrification and denitrification. The passively aerated composting system results in a compost bed which is highly heterogeneous with respect to temperature, oxygen level and its composition. It is proposed that in this way a highly diverse microbial community in the compost bed is established which can perform various microbial conversions. The extensive composting system is most promising for on-farm production of an organic fertilizer from straw-rich manure, since the costs of the process and the level of ammonia emissions were low.     

不同覆盖措施对鸡粪堆肥氨挥发的影响

采用箱式抽气法对不同鸡粪堆肥体系中氨气挥发释放速率及其影响因素进行了研究.结果表明,鸡粪堆肥的氨挥发强度在堆置后20d内最大.氨挥发速率最高达到0.28 g/(kg·h),覆盖粘土能有效抑制堆体的氨挥发.覆盖处理中铵态氮有累积的现象,铵态氮浓度最高达到6.68 g/kg,导致其pH值和电导率显著高于不覆盖处理.从全氮含量的变化来看,覆盖秸秆和篷布处理的氮素损失率分别为21-79%和19.78%,是对照处理的73.71%和66.91%,表现出良好的保氮效果.     

低蛋白饲喂技术对猪粪好氧堆肥腐熟度的影响

  【目的】  猪粪由于产生量大、碳氮比低、水分含量高等导致储存处理难度较大，好氧堆肥处理猪粪因原料所提供微生物活动环境较差，导致堆肥效率低下。低蛋白饲喂技术在不影响猪生长发育的同时降低了饲料中的氮投入，可以显著改变猪粪的养分组成。本研究通过多种有机肥腐熟指标判定，分析低蛋白含量日粮饲喂的猪粪通过不同堆肥方式是否可快速有效地达到腐熟，并符合安全施用标准。  【方法】  动物试验选取初始体重为60 kg的去势公猪72头，分高、低蛋白饲喂两个处理，每个处理6次重复，每个重复6头猪。试验饲料均适应喂养7天后，开始收集粪便，收粪期为60天。堆肥试验共设4个处理，分别是高蛋白饲喂静态堆肥 (MH)、低蛋白饲喂静态堆肥 (ML)、高蛋白饲喂好氧堆肥 (CH)、低蛋白饲喂好氧堆肥 (CL)，堆肥周期为14天。监测了堆肥过程中堆体温度和碳、氮含量等指标，并测定堆肥处理的小白菜种子发芽指数 (GI)。  【结果】  以堆肥过程中高温持续时间、堆肥NH₄+-N含量、T值 (堆肥结束C/N与堆肥初始C/N的比值) 和GI (小白菜种子发芽指数) 4项为腐熟判断指标，在14天堆肥周期内，高蛋白饲喂产生的猪粪在静态堆肥情况下 (MH)，高温持续时间为0天，NH₄+-N含量为0.43 g/kg、T值为0.91、GI指数为0，未能达到腐熟标准；高蛋白饲喂产生的猪粪堆肥在好氧堆肥条件下 (CH)，高温持续时间为5天，NH₄+-N含量为0.33 g/kg、T值为0.70、GI指数为0.31，T值和GI值均未能达到腐熟标准；低蛋白饲喂产生的猪粪，在静态堆肥中 (ML) 高温持续时间为0 天，NH₄+-N含量为0.54 g/kg、T值为0.81、GI指数为0.25，均未能达到腐熟标准；而在好氧堆肥 (CL) 中，高温持续时间为6天，NH₄+-N含量0.14 g/kg、T值为0.57、GI指数为0.96，均达到腐熟标准。  【结论】  高蛋白饲养产生的猪粪在静态和好样发酵条件下堆放14天，都不能完全腐熟。低蛋白饲喂产生的猪粪在静态堆放条件下，堆肥14天也不能达到腐熟标准。而低蛋白饲养产生的猪粪在好样条件下，可以在堆放14天时达到腐熟，因为低蛋白饲喂技术使猪粪碳氮比提高了约15%，高温发酵时长延长了40%，极大提高了猪粪短时间内的腐熟程度。因此，在循环农业中，通过上游低蛋白饲喂技术可促进下游猪粪的快速处理和循环利用。