6种类型有机肥的矿化特性研究

采用室内培养法，研究了西北地区日光温室栽培生产中常用的6种有机肥的碳、氮矿化特性。结果表明，不同有机肥碳、氮的矿化量和矿化率(矿化量占总有机碳或氮的比例)的动态变化存在明显差异，碳素矿化率在25.7%～56.3%，变异系数达44.8%；氮素平均矿化率为16.6%～36.3%，变异系数达 29.48%。不同类型有机肥相比，鸡粪的平均碳、氮矿化累积量及矿化率显著高于羊粪和牛粪，羊粪次之，牛粪最小。     

日光温室栽培下不同种类有机肥氮素矿化特性研究

采用田间原位培养试验,研究了日光温室栽培季节不同种类有机肥（鸡粪、猪粪及牛粪各2个）的氮素矿化特性。结果表明: 培养期间（180 d）供试的6个不同有机肥氮矿化率差异较大,在1.1%～19.09%之间,平均7.5%;不同种类有机肥相比,鸡粪的平均氮矿化量及矿化率最高,其次为牛粪及猪粪,这与鸡粪C/N比相对较高有关。各培养阶段有机肥的氮矿化量与相应阶段的土壤积温间的相关性未达显著水平,但随着春季土壤温度增加,这一阶段有机肥氮素的矿化量呈增加的趋势;培养期间有机肥的氮素累积矿化量与日光温室土壤的积温呈显著的线性关系,说明土壤温度是影响有机肥氮矿化量的重要因素。     

不同有机肥对采煤塌陷区土壤氮素矿化动态特征研究

为揭示不同有机肥对煤矿复垦土壤氮素矿化特性的影响,以山西省孝义市水峪煤矿采煤塌陷复垦土壤为研究对象,采用室内好气培养法,研究在40%含水量和30℃培养条件下,施用3种有机肥(鸡粪、猪粪、牛粪)后在0~161天的氮素矿化动态特征,以明确不同有机肥对该矿区复垦土壤氮素矿化特征,从而预估不同有机肥的供氮特性,为合理施用有机肥进行低产农田的培肥改造提供科学依据。结果表明:(1)各处理0~14天铵态氮含量均随培养时间的延长迅速下降,与培养时间呈极显著负相关关系(P<0.01),14~161天土壤铵态氮含量维持在较低水平,培养结束时,各处理铵态氮含量均低于1.31mg/kg。(2)各处理土壤硝态氮含量、累积量及矿质氮累积量变化均呈近似的“S”形曲线递增,表现为0~56天缓慢增加,56~84天迅速增加,84天至培养结束(161天)其含量基本不变。培养结束时不同处理间硝态氮含量、累积量及矿质氮累积量整体上均表现为鸡粪>猪粪>牛粪>空白,且鸡粪较猪粪和牛粪处理间存在显著差异,猪粪和牛粪较空白处理间存在显著差异(P<0.05)。(3)不同施肥处理出现氮素净矿化的时间点不同,其中鸡粪处理在第14天时最早出现净矿化现象,而猪粪和牛粪在培养28天后才出现明显的氮素净矿化。(4)不同施肥处理在培养的不同阶段硝态氮和矿质氮累积速率不同,但整体趋势一致,表现为培养0~84天各处理土壤累积矿化波动较大,56~84天达到峰值,培养84~161天各处理矿化速率平稳下降。总体来看,有机肥的施入能有效促进煤矿复垦土壤氮素矿化,从而提高土壤氮素有效性。其中,施鸡粪较猪粪和牛粪对提高矿区复垦土壤有效氮效果更好。4种处理的氮素矿化效果总体表现为鸡粪>猪粪>牛粪>空白。     

长期施肥对水稻土碳氮矿化与团聚体稳定性的影响

水稻土有机碳、氮矿化过程对水稻土质量和作物养分吸收具有重要的作用,但是它们对施肥措施的响应及其与土壤结构之间的关系尚不清楚。本研究基于红壤性水稻土长期施肥定位试验,分析了不施肥(CK)、施用常量化肥(NPK)、2倍化肥(NPK2)和常量化肥配施有机肥(NPKOM)等处理下水稻土碳氮矿化特征,并研究了其与土壤团聚体稳定性的关系。结果表明NPKOM处理显著提高了土壤有机碳和全氮含量(P0.05),而单施化肥处理(NPK2和NPK)则同CK处理没有显著差异。土壤有机碳矿化速率、累积矿化量和矿化率均为NPKOMNPK2NPKCK处理,其中NPKOM处理显著高于其他处理(P0.05),而后3个处理间没有显著差异。土壤氮矿化速率、累积矿化量和矿化率同土壤碳矿化的规律一致,NPKOM、NPK2和NPK处理累积矿化氮量较CK处理分别提高110.0%、29.4%和8.8%,矿化率分别提高110.8%、25.6%和13.0%。单施化肥处理(NPK和NPK2)的平均质量直径(MWD)分别降低了17.1%和15.5%,而NPKOM处理则增加了19.4%。相关分析表明,土壤碳氮矿化主要取决于土壤有机碳氮含量,而与土壤团聚体水稳定性无直接关系。在今后研究中,应重点分析土壤孔隙结构与有机碳氮周转的关系。     

猪粪与牛粪有机肥对水稻产量、养分吸收利用和 土壤肥力的影响

采用连续5年田间定位试验,研究了等量单独施用猪粪或牛粪有机肥以及有机肥与化学肥料配施对水稻产量、氮磷钾养分吸收累积及利用效率、土壤养分含量及其与产量等关系的影响。结果表明:猪粪有机肥施用(7.5t/hm~2+常量化肥、15 t/hm~2+1/2常量化肥和30 t/hm~2+无化肥)时水稻产量、干物质累积、氮磷累积及生理利用效率与常量化肥处理相比无显著差异;牛粪有机肥与化肥减量配施和单独施用时,尽管氮、磷和钾生理利用效率有所提高,但水稻产量、地上部氮、磷和钾累积量均有不同程度下降,且以单独施用时尤为明显。等量猪粪有机肥对土壤全氮、碱解氮、有效磷和速效钾含量以及pH的提升程度大于牛粪有机肥,有机质含量无明显差异;与猪粪有机肥相比,牛粪有机肥施用时土壤养分各指标与水稻产量、干物质累积量、氮磷钾累积量以及利用效率间的相关性更为明显,其中与产量、干物质累积量和氮磷钾累积量极显著负相关,与氮磷钾生理利用效率显著正相关。因此,等量猪粪有机肥和牛粪有机肥的肥效存在较大差异,在实际生产中应根据不同源有机肥特性进行调节施用。     

猪粪与牛粪有机肥对水稻产量、养分利用和土壤肥力的影响

采用连续5年田间定位试验,研究了等量单独施用猪粪或牛粪有机肥以及有机肥与化学肥料配施对水稻产量、氮磷钾养分吸收累积及利用效率、土壤养分含量及其与产量等关系的影响。结果表明:猪粪有机肥施用(7.5t/hm~2+常量化肥、15 t/hm~2+1/2常量化肥和30 t/hm~2+无化肥)时水稻产量、干物质累积、氮磷累积及生理利用效率与常量化肥处理相比无显著差异;牛粪有机肥与化肥减量配施和单独施用时,尽管氮、磷和钾生理利用效率有所提高,但水稻产量、地上部氮、磷和钾累积量均有不同程度下降,且以单独施用时尤为明显。等量猪粪有机肥对土壤全氮、碱解氮、有效磷和速效钾含量以及pH的提升程度大于牛粪有机肥,有机质含量无明显差异;与猪粪有机肥相比,牛粪有机肥施用时土壤养分各指标与水稻产量、干物质累积量、氮磷钾累积量以及利用效率间的相关性更为明显,其中与产量、干物质累积量和氮磷钾累积量极显著负相关,与氮磷钾生理利用效率显著正相关。因此,等量猪粪有机肥和牛粪有机肥的肥效存在较大差异,在实际生产中应根据不同源有机肥特性进行调节施用。     

有机肥与化肥不同比例配施下水稻土铵态氮释放特征

采用淹水密闭培养-间歇淋洗法,研究了有机肥(猪粪和牛粪)与化肥(尿素)氮以不同比例配施后对水稻土铵态氮释放特征的影响。结果表明:与单施100%尿素处理相比,培养到28 d,配施有机肥处理(除80%尿素氮配施20%牛粪氮、70%尿素氮配施30%牛粪氮和50%尿素氮配施30%牛粪氮处理)显著降低土壤铵态氮的累积释放量,且随有机肥配施比例的增加降幅增大,降低幅度为5.78%~41.20%(P0.05);培养28~90 d,配施有机肥处理(50%尿素氮配施30%牛粪氮处理除外)的土壤铵态氮释放量显著提高;至培养90 d,50%尿素氮配施50%猪粪氮和80%尿素氮配施20%牛粪氮处理的土壤铵态氮累积释放量显著高于单施100%尿素处理,提高幅度分别为4.81%和9.32%(P0.05)。培养结束时,氮素减施20%(单施80%尿素氮、50%尿素氮配施30%猪粪氮和50%尿素氮配施30%牛粪氮)处理的土壤铵态氮累积释放量与单施100%尿素处理无显著差异。本研究表明,50%尿素氮配施30%猪粪氮既可以降低土壤铵态氮前期释放速率,又可以增加水稻土持续稳定的供氮能力,对减少氮肥损失维持作物生产具有重要意义。     

长期施肥条件下水稻土有机氮组分及矿化特性研究

为探明长期定位试验条件下不同施肥处理和地下水位对水稻土有机氮组分及其矿化特性的影响,采用Keeney和Bremer酸解法对土壤有机氮进行分组研究,并利用改进后的Warning淹水培养-间歇淋洗法研究水稻土有机氮矿化特性。结果表明,不同处理土壤酸解氮占全氮的61.2%～64.4%,其中酸解未知氮,氨基酸态氮,氨态氮和氨基糖态氮分别占全氮26.9%～34.0%,13.0%～18.0%,12.6%～14.3%和2.3%～4.7%。恒温淹水培养106d后,以酸解未知氮降幅最大,且酸解未知氮与土壤氮矿化势之间有显著的正相关关系(r=0.865*),表明酸解未知氮是土壤可矿化态氮的主要贡献者。有机肥处理土壤矿化氮累积量及氮矿化势显著高于化肥处理,表明长期施用有机肥是提高土壤供氮潜力的有效手段。此外,低水位土壤矿化氮累积量及氮矿化势略高于高水位土壤。     

添加牛粪对长期不同施肥潮土有机碳矿化的影响及激发效应

为了探讨长期不同施肥潮土有机碳矿化对添加牛粪的响应特征及添加牛粪对长期不同施肥潮土有机碳矿化的激发效应,以始建于1986年的长期定位试验为平台,通过室内恒温培养的方法研究添加等氮量牛粪后长期不同施肥(不施肥,CK;常量有机肥,SMA;常量化肥,SMF;常量有机无机配施,1/2(SMA+SMF))潮土有机碳矿化、土壤有机碳及活性碳库组分(微生物量碳、可溶性有机碳、颗粒有机碳和易氧化有机碳)含量的变化特征。结果表明:无论添加牛粪与否,长期不同施肥潮土有机碳矿化过程均符合一级动力学方程,而牛粪的添加显著增加了长期不施肥、长期单施化肥和长期有机无机配施土壤的有机碳矿化速率常数,增长幅度分别为21.74%、35.00%和45.00%;添加牛粪提高了长期不同施肥潮土有机碳、微生物量碳、颗粒有机碳和易氧化有机碳含量,却显著降低了可溶性有机碳含量;牛粪对长期不施肥、长期施用常量有机肥、常量化肥和常量有机无机配施潮土有机碳矿化的正激发效应分别达到了48.56%、3.60%、48.43%和3.92%,且对长期不施肥及长期施用常量化肥潮土的激发效应显著高于对长期施用常量有机肥及长期有机无机配施土壤;冗余分析显示添加牛粪对长期不同施肥土壤有机碳矿化的激发效应与土壤活性组分碳氮比呈正相关,与土壤养分含量呈负相关。该研究不仅为合理施用有机肥和实现农田生态系统的可持续发展提供理论依据,还有利于实现农业资源再利用及其效益最大化。     

不同中药渣组合好氧堆肥产物对土壤碳矿化特性的影响

为研究不同配方中药渣废弃物好氧堆肥产品品质差异及其对土壤碳素矿化的影响，设置了好氧堆肥和有机肥还田两个试验。通过工厂化条垛式好氧堆肥试验，研究了中药渣废弃物3种组合，在相同碳氮比、不同木质纤维素含量下对好氧堆肥产品品质的影响；采用土壤呼吸瓶进行室内恒温恒湿培养模拟土壤施肥效应，研究了3种有机肥施用对不同肥力土壤有机碳分解动态的影响。试验结果显示：中药渣物料的初始木质纤维素含量显著影响堆肥产品的碳氮养分转化和腐殖质组分。与初始低木质纤维素含量处理(T1)相比，高木质纤维素含量处理(T3)堆肥有机碳降解难，堆肥产品中全碳含量提高5.7%，全氮含量降低18.4%，但有利于腐殖质形成，尤其是显著增加胡敏酸组分20.9%。3种中药渣堆肥产品等碳量输入对不同肥力土壤的碳素矿化效果差异显著，高肥力土壤CO₂-C的释放速率和累积释放量均高于低肥力土壤，但有机碳的累积矿化率却低于低肥力土壤，并且高肥力土壤中添加T1堆肥产品累积矿化率显著高于添加T3堆肥产品。两个肥力土壤中有机肥中胡敏酸组分与土壤碳素矿化率之间呈显著负相关关系。因此，为提高有机肥的土壤固碳效应，可适当提高有机肥中胡敏...     

不同有机肥与化肥配施对氮素利用率和土壤肥力的影响

【目的】不同类型畜禽粪便有机肥在成分和性质上存在明显差异，本文研究了华北地区主要有机肥与化肥以不同比例配施后，对作物氮素吸收利用及土壤养分的影响，以期为本地区有机肥的科学利用提供理论依据和数据支撑。【方法】在华北平原冬小麦–夏玉米种植区进行田间试验。以推荐养分施用量 (每季作物N 225 kg/hm2) 为基础，设置了1个常规单施化肥处理 (CF)，12个鸡粪、猪粪和牛粪氮分别与化肥氮配比处理 (有机肥氮素占比25%、50%、75%、100%)，化肥及3种有机肥的加倍单施处理，同时设1个不施肥处理为对照，共18个处理。分析了作物的氮素吸收量、氮素利用效率，测定了0—20、20—40 cm土层土壤氮、磷、钾含量。【结果】常规施肥量下，单施鸡粪、猪粪、牛粪处理的氮素收获指数 (NHI) 均与化肥处理相当，平均为79.06%；单施牛粪处理的氮素生理利用率 (NPE) 为64.42 kg/kg，显著高于化肥处理；而单施鸡粪、猪粪处理的NPE与化肥处理相当，平均为55.14 kg/kg。与常规施肥量相比，加倍施用鸡粪、猪粪和化肥处理的显著降低NHI值和NPE值，而加倍牛粪处理的NHI与NPE值没有降低。牛粪、鸡粪、猪粪与化肥配施的处理间NHI与NPE值均未表现出显著性差异，且与单施化肥的处理相当。常规施氮量下，单施猪粪、鸡粪处理的氮素偏生产力 (PFP) 和回收率 (NRE) 接近，均值为分别39.67 kg/kg和41.85%，达到了单施化肥处理的水平，而牛粪处理的氮素PFP以及NRE仅为29.08 kg/kg和15.6%，显著低于化肥、鸡粪和猪粪处理。与常规施氮量相比，加倍施用牛粪、鸡粪、猪粪和化肥处理的氮素的PFP值平均降低了49.1%，氮肥NRE值平均降低了23.2%。牛粪、鸡粪、猪粪与化肥各配施比例处理的氮素PFP和NRE值均达到了单施化肥的水平。与单施化肥相比，单施有机肥以及有机无机配施没有明显提高土壤全氮含量，但显著提高有效磷和速效钾含量，单施鸡粪、猪粪处理土壤表层有效磷含量分别是单施化肥处理的5.82和7.06倍。【结论】推荐施肥量下，鸡粪或猪粪单独施用或配施少量化肥氮，牛粪配施75%左右的化肥氮可实现与化肥相当的氮素利用效率，同时提升土壤肥力。在实际生产中应根据有机肥特性调节有机肥与化肥配施比例，实现有机肥的科学利用。     

Biochemical composition and kinetics of C and N mineralization of animal wastes: a typological approach

Forty-seven different animal wastes were characterized using chemical and organic matter fractionation methods (water extraction and Van Soest method) and 224-day incubation studies to assess their decomposition in soil. Simple correlation and multiple factor analysis were performed to establish relationships between the composition of these wastes and C and N mineralization. Carbon and N contents ranged from 101 to 469 mg C kg⁻¹ dry matter (d.m.) and from 4 to 39 mg N kg⁻¹ d.m. Soluble C and N represented less than 9% of organic C and 1.5% of total N at 20°C, respectively. The C fractions soluble at 100°C or in neutral detergent were larger and represented 14 and 32% of the organic C, respectively. The hemicellulose-like (HEM) and cellulose-like (CEL) fractions contained about 16.5 and 6% of the organic N, respectively. The C distribution in the lignin-like (LIG) and CEL fractions was comparable, but the former contained more N. Carbon mineralization varied from 5 to 62% of the organic C added during the 224-day incubation; 70% of the wastes induced net N mineralization at the end of incubation (from 3 to 51% of organic N). Other wastes induced net soil inorganic N immobilization, from −1 to −31% of the organic N added. Most highly significant correlations were established between the C mineralization and the C present in the water-soluble fraction at 20°C, and the HEM and LIG fractions. Relationships between N mineralization and biochemical characteristics were weak, except with the soluble Van Soest fraction, and highly significant correlations were observed between N mineralization rates calculated at 224 days of incubation and the organic N content or C/N ratio of wastes. Finally, an objective hierarchical classification based on composition criteria and C and N mineralization led to the definition of six different classes of wastes. It permitted differentiation between four composted wastes and intrinsically different wastes (i.e., cattle manures, pig manures, and poultry manures) which could not be objectively regrouped. It also placed some very different types of waste (solid phase from pig slurry separation, pig manures, and composted pig mixtures) in the same class.     

不同类型有机肥与化肥配施对小麦品质的影响

【目的】 综合分析不同类型有机肥与化肥配施对小麦籽粒、面粉、面团品质指标的影响，为提升小麦品质提供有机肥科学施用基础。 【方法】 以鸡粪、猪粪和牛粪为供试有机肥料，冬小麦品种济麦22为供试作物进行了田间试验。在施N 225 kg/hm2前提下，设单施化肥（尿素）、鸡粪、猪粪、牛粪处理，及三种有机肥各自分别以25%、50%和75%配合75%、50%、25%的化肥处理，以及化肥、鸡粪、猪粪、牛粪施肥料量加倍处理，共18个处理。小麦收获后，分析了3个籽粒品质指标、5个面粉品质指标、7个面团品质指标，运用多元统计分析方法评价了三种有机肥的不同利用方式和用量对小麦品质的影响。 【结果】 施N 225 kg/hm2条件下，单施鸡粪、猪粪对小麦各品质指标的提升作用与单施化肥处理相当，明显优于牛粪；与单施牛粪处理相比，单施鸡粪、猪粪、化肥处理的平均面团形成时间延长了50.85%，平均粉质指数提高了25.75%，平均湿面筋含量提升了19.71%，平均沉淀值提升了18.17%，平均粗蛋白含量提升了14.37%，面团拉伸比降低了36.84%。增加肥料用量一倍对小麦品质指标的提升作用不显著。常量处理中，25%有机肥+75%化肥最有利于籽粒蛋白含量的提高。将15个品质指标分为3个主成分组，以湿面筋为代表的第一主成分方差贡献率占到60.2%，代表了大部分的数据信息。根据各施肥处理对品质指标影响的相似性，将18种施肥方式聚为四类:1)不施肥；2)单施常量、加倍牛粪处理；3)常量鸡粪、猪粪、化肥单施及常量配施处理；4)加倍化肥、加倍鸡粪和加倍猪粪处理，从1）至4）小麦多数品质指标呈现依次升高的趋势。 【结论】 以常规施氮量(225 kg/hm2)为前提，鸡粪、猪粪配施少量或者不配施化肥，牛粪配施75%化肥都可以显著提升小麦品质，单施牛粪提升小麦品质作用不显著。因此，在有机肥源充足的条件下，在总施氮量不增加的前提下，鸡粪、猪粪氮的施用比例可提高至75%，牛粪的实用比例控制在25%，以获得优质的小麦籽粒品质。     

Predicting nitrogen availability and losses following application of organic manures to arable land: MANNER

Abstract. A decision support system to predict the plant availability of nitrogen (N) following organic manure applications to land has been developed, drawing together the latest UK research information on factors affecting manure N availability and losses. The ADAS MAN ure N itrogen E valuation R outine (MANNER) accounts for manure N analysis, ammonia volatilization, nitrate leaching and mineralization of manure organic N. Only a few easily available inputs are required to predict the amount of N volatilized or leached, and the fertilizer N value for the next crop grown. Predictions from MANNER have been evaluated by comparison with independently collected data from a range of experimental studies where pig, cattle and poultry manures were applied to arable crops. Good agreement was found ( r ² 60–79%, P <0.001), confirming that MANNER can provide a reliable estimate of the fertilizer N value of farm manures spread to arable land under a range of conditions.     

畜禽有机肥氮、磷在红壤中的矿化特征研究

选用腐熟的猪粪、鸡粪和第四纪红土发育的典型红壤为试验材料,通过室内培养试验,研究了土壤中矿质氮(NO-3-N和NH4+-N)及Olsen-p的动态变化.结果表明,有机肥中氮和磷的矿化具有不同特征.氮在红壤中的矿化阶段为:前4周缓慢释放,矿化速率为N 0.29～0.46mg/(kg·d);4～10周快速释放,矿化速率为N...     

Mineralization of Three Organic Manures Used as Nitrogen Source in a Soil Incubated under Laboratory Conditions

Abstract

The rate and timing of manure application when used as nitrogen (N) fertilizer depend on N‐releasing capacity (mineralization) of manures. A soil incubation study was undertaken to establish relative potential rates of mineralization of three organic manures to estimate the value of manure as N fertilizer. Surface soil samples of 0–15 cm were collected and amended with cattle manure (CM), sheep manure (SM), and poultry manure (PM) at a rate equivalent to 200 mg N kg^?1 soil. Soil without any amendment was used as a check (control). Nitrogen‐release potential of organic manures was determined by measuring changes in total mineral N [ammonium‐N+nitrate‐N (NH₄ ⁺–N+NO₃ ^?–N)], NH₄ ⁺–N, and accumulation of NO₃ ^?–N periodically over 120 days. Results indicated that the control soil (without any amendment) released a maximum of 33 mg N kg^?1soil at day 90, a fourfold increase (significant) over initial concentration, indicating that soil had substantial potential for mineralization. Soil with CM, SM, and PM released a maximum of 50, 40, and 52 mg N kg^?1 soil, respectively. Addition of organic manures (i.e., CM, SM, and PM) increased net N released by 42, 25, and 43% over the control (average). No significant differences were observed among manures. Net mineralization of organic N was observed for all manures, and the net rates varied between 0.01 and 0.74 mg N kg^?1 soil day^?1. Net N released, as percent of organic N added, was 9, 10, and 8% for CM, SM, and PM. Four phases of mineralization were observed; initial rapid release phase in 10–20 days followed by slow phase in 30–40 days, a maximum mineralization in 55–90 days, and finally a declined phase in 120 days. Accumulation of NO₃ ^?–N was 13.2, 10.6, and 14.6 mg kg^?1 soil relative to 7.4 mg NO₃ ^?–N kg^?1 in the control soil, indicating that manures accumulated NO₃ ^?–N almost double than the control. The proportion of total mineral N to NO₃ ^?–N revealed that a total of 44–61% of mineral N is converted into NO₃ ^?–N, indicating that nitrifiers were unable to completely oxidize the available NH₄ ⁺. The net rates of mineralization were highest during the initial 10–20 days, showing that application of manures 1–2 months before sowing generally practiced in the field may cause a substantial loss of mineralized N. The rates of mineralization and nitrification in the present study indicated that release of inorganic N from the organic pool of manures was very low; therefore, manures have a low N fertilizer effect in our conditions.     

Mineralization and denitrification in upland, nearly saturated and flooded subtropical soil II. Effect of organic manures varying in N content and C:N ratio

 Nitrogen and carbon mineralization of cattle manure (N=6 g kg^–1; C:N=35), pressmud (N=17.4 g kg^–1; C:N=22), green manure (N=26.8 g kg^–1; C:N=14) and poultry manure (N=19.5 g kg^–1; C:N=12) and their influence on gaseous N losses via denitrification (using the acetylene inhibition technique) in a semiarid subtropical soil (Typic Ustochrepts) were investigated in a growth chamber simulating upland, nearly saturated, and flooded conditions. Mineralization of N started quickly in all manures, except pressmud where immobilization of soil mineral N was observed for an initial 4 days. Accumulation of mineral N in upland soil plus denitrified N revealed that mineralization of cattle manure-, pressmud-, poultry manure- and green manure-N over 16 days was 12, 20, 29 and 44%, respectively, and was inversely related to C:N ratio (R ²=0.703, P=0.05) and directly to N content of organic manure (R ²=0.964, P=0.01). Manure-C mineralized over 16 days ranged from 6% to 50% in different manures added to soil under different moisture regimes and was, in general, inversely related to initial C:N ratio of manure (R ²=0.690, P=0.05). Cumulative denitrification losses over 16 days in control soils (without manure) under upland, nearly saturated, and flooded conditions were 5, 23, and 24 mg N kg^–1, respectively. Incorporation of manures enhanced denitrification losses by 60-82% in upland, 52–163% in nearly saturated, and 26–107% in flooded soil conditions over a 16-day period, demonstrating that mineralized N and C from added manures could result in 2- to 3-fold higher rate of denitrification. Cumulative denitrification losses were maximal with green manure, followed by poultry manure, pressmud and cattle manure showing an increase in denitrification with increasing N content and decreasing C:N ratio of manure. Manure-amended nearly saturated soils supported 14–35% greater denitrification than flooded soils due to greater mineralization and supply of C.     

京郊畜禽粪污氮磷含量特征及影响因素分析

中国规模化养殖废弃物中养分资源数量可观,但缺乏循环利用技术,处置不当易引发环境污染问题。该文通过问卷调研和粪污样品检测,对京郊典型养殖场粪便和废水中的总氮、总磷含量特点进行分析,同时追踪典型规模化猪场废水中总氮、总磷含量变化的影响因素及其季节性变化特征。结果表明:所调研的养殖场中,猪粪、牛粪的总氮质量分数平均值分别为29.1,17.8 g/kg,总磷质量分数平均值分别为15.1,6.8 g/kg,猪粪便的总氮、总磷含量变异程度大于牛粪;猪场和牛场中废水总氮、总磷质量分数的平均值分别为892,540和82.4,53.3 mg/L,猪场废水总氮、总磷含量变异程度明显大于牛场。规模化猪场粪便总氮、总磷含量受到饲料配方的影响较大;受饲料和圈舍用水量的影响,现行饲养工艺及粪污处理方式下粪便对废水中总氮、总磷含量的影响较小;万头以上的规模化猪场废水中总氮、总磷含量存在季节性差异,且随着废水存储时间的推移其无机磷比例增加。这些变化特征可对畜禽粪便和养殖废水的资源化再利用提供了有用的参考。