水热预处理强化牛粪厌氧消化及其机理

为解决禽畜废物在厌氧条件下产甲烷性差的问题,采用水热法预处理+中温厌氧消化改良法考察了水热法预处理强化牛粪厌氧消化性能的效果,并进一步通过分析预处理前后牛粪化学组分、元素组成和化学结构变化以探究其强化机制.结果表明:一定强度的水热预处理能提高牛粪的厌氧产甲烷性能,过高的预处理强度(R₀)反而抑制了产甲烷率.在水热预处理温度为70℃、时间为4 320 min时(R₀为3.27),牛粪获得最大甲烷产量(以VS计)176.36 mL/g,比未预处理组(145.76 mL/g)提高了21.00%,乙酸浓度提高了65.69%,木质素去除率达到11.50%,可知有机组分的降解和木质素的移除是牛粪厌氧产甲烷性能提高的主要原因.元素分析发现,预处理后牛粪O/C〔w(O)/w(C)〕得到提高,表示糖类化合物增多;同时红外光谱分析结果显示,R₀过大时,木质素中芳环骨架的CC作用会增强,类木质素物质增多,导致牛粪产甲烷性能降低.研究显示,水热预处理能够有效增强畜禽废物的降解能力,促进牛粪产甲烷性能的提升.      

不同改良物质添加对滨海盐碱地土壤重金属及酶活性的影响

改良物质添加在改善土壤理化性质的同时也可能会导致土壤重金属累积.实验设置了对照（CK）、有机肥（OM）、聚丙烯酰胺+有机肥（PAM+OM）、秸秆覆盖+有机肥（SM+OM）、秸秆深埋+有机肥（BS+OM）和生物菌肥+有机肥（BM+OM）共6个处理方式,研究不同改良物质添加对滨海盐碱地土壤重金属和土壤酶活性的影响,以及二者之间的关系.结果表明,与CK处理相比,不同处理下土壤Cr、Cu、Ni和Pb含量呈现上升趋势,其中SM+OM和PAM+OM处理分别对Cr和Cu含量的影响最为显著,而BM+OM处理对Ni和Pb含量影响最为显著.与CK处理相比,改良物质添加后土壤蔗糖酶和脲酶活性显著上升,其中BM+OM处理效果最好;碱性磷酸酶活性呈现上升趋势,但上升程度较小;过氧化氢酶活性无显著变化.冗余分析表明前两轴累积可解释酶活性变异特征的70.3%,单一重金属对土壤酶活性影响的重要性大小依次为：Ni>Cu>Cr>Pb.     

咪唑烟酸在土壤中的微生物降解及其代谢物分析

通过分析咪唑烟酸在4种典型土壤中灭菌和非灭菌条件下的降解动力学差异,初步探讨了土壤中的微生物对其降解的贡献率。结果表明,咪唑烟酸在非灭菌条件下的半衰期为29～44d,在灭菌条件下的半衰期为81～134d,在非灭菌条件下的降解速率比灭菌条件下提高1 3～3 4倍。在小粉土中微生物降解的理论半衰期约为48d,为灭菌条件下的近3倍,充分说明了土壤中的微生物在咪唑烟酸的降解中起着非常重要的作用。运用LC-ESI-MS检测到4种微生物降解产物,它们的分子量分别为219,222,201和149,并由此推断了咪唑烟酸在土壤中降解转化的主要途径为:首先被微生物转化成更为稳定的氨盐产物,然后再进一步脱甲基、羧基和异丙基及咪唑啉酮环的开裂和重排等。      

Estimating the combined toxicity of flufenacet and imazaquin to sorghum with pore water herbicide concentration

Combined toxicity of herbicides to non-target crops is usually resulted from their successive application. The present study was conducted to assess the combined toxicity of flufenacet (FLU) and imazaquin (IMA) to sorghum with their concentration in soil pore water. The concentrations that inhibited growth by 50% (IC50) of FLU and IMA individually and their combination estimated from the herbicide concentrations in soil pore water notably differed from those based on the amended concentrations, due to the decline in bioavailability resulting from adsorption of the herbicides onto soil. According to the amended concentrations, the combined effect of FLU and IMA in soil on sorghum growth was identified as additive action. Based on the concentration in soil pore water, however, it was determined to be antagonism, which was identical to that observed in a test using culture solution. The results revealed that pore water herbicide concentration might be an effective tool to assess the combined toxicity of herbicides in soil to rotational crops.     

尿素糠醛缩合物缓释化肥的研究

为了提高尿素的利用率,改善土壤的耕作质量,笔者按尿素与糠醛的摩尔比(U/F)控制反应计量,得到尿素糠醛缩合物缓释化肥。加成反应缓冲试剂为Na2B4O7-H3BO3,pH值8~9,反应温度控制在45~55℃,消去反应缓冲试剂为CH3COOH-CH3COONH4,pH值4.5~5,反应温度控制在60℃。测试结果表明,当U/F应介于(1.3~1.5):1时,得到产物的AI值均高于60%,产物在水中的溶出率和在土壤中的溶出率低于普通化肥。该低分子尿素糠醛缩合物是一种缓释化肥,不仅可以显著提高氮素的利用率,而且可以通过调整U/F值与植物生长周期相匹配。该缩合物还具有改善土壤,防止沙化,提高植物根部在土壤中的扎根能力。     

膨润土对鸡粪序批式厌氧消化特性的影响

为考察外源添加物——膨润土对鸡粪厌氧消化特性的影响,在中温〔(35±1)℃〕条件下,采用L₈(23)正交试验设计,考察了膨润土添加量(w,以干基计,下同)、鸡粪VS(挥发性固体)添加量、厌氧消化污泥接种量对鸡粪厌氧消化过程中产气、pH、氨氮形态、EC(电导率)等的影响. 结果表明:添加1.5%和3.0%的膨润土均能显著提高鸡粪VS产CH₄量,并且在高鸡粪添加量情况下达到极显著水平(P<0.01);当膨润土添加量为3.0%、厌氧消化污泥接种量为20%时,VS累积产CH₄量达到301.92 mL/g,比对照组(160.76 mL/g)提高了87.80%;当鸡粪VS添加量相同时,添加1.5%和3.0%的膨润土均能极显著地降低消化料液的ρ(TAN)(TAN为总氨氮)(P<0.01),并且可以减少鸡粪厌氧消化过程中ρ(FAN)(FAN为游离氨)的剧烈变化;添加膨润土还能极显著地降低鸡粪厌氧消化料液的EC. 研究显示,添加膨润土有利于缓解鸡粪厌氧消化过程中氨氮抑制,提高系统稳定性,并可显著改善厌氧消化整体性能.      

Sustainable land management practices as providers of several ecosystem services under rainfed Mediterranean agroecosystems

Little is known about the multiple impacts of sustainable land management practices on soil and water conservation, carbon sequestration, mitigation of global change and crop yield productivity in semiarid Mediterranean agroecosystems. We hypothesized that a shift from intensive tillage to more conservative tillage management practices (reduced tillage optionally combined with green manure) leads to an improvement in soil structure and quality and will reduce soil erosion and enhance carbon sequestration in semiarid Mediterranean rainfed agroecosystems. To test the hypothesis, we assessed the effects of different tillage treatments (conventional (CT), reduced (RT), reduced tillage combined with green manure (RTG), and no tillage (NT)) on soil structure and soil water content, runoff and erosion control, soil carbon dioxide (CO₂) emissions, crop yield and carbon sequestration in two semiarid agroecosystems with organic rainfed almond (Prunus dulcis Mill) in the Murcia Region (southeast Spain). It was found that reduction and suppression of tillage under almonds led to an increase in soil water content in both agroecosystems. Crop yields ranged from 775 to 1,766 kg ha^?1 between tillage treatments, but we did not find a clear relation between soil water content and crop yield. RT and RTG treatments showed lower soil erosion rates and higher crop yields of almonds than under CT treatment. Overall, higher soil organic carbon contents and aggregate stability were observed under RTG treatment than under RT or CT treatment. It is concluded that conversion from CT to RTG is suitable to increase carbon inputs without enhancing soil CO₂ emissions in semiarid Mediterranean agroecosystems.     

连续施用鸡粪对菜心产量和重金属含量的影响

由于养殖业普遍使用微量元素添加剂,导致禽畜粪中重金属残留过高现象广泛存在.根据养殖场鸡粪含氮量计算其用量（N 0～450 kg·hm^-2）,进行连续4茬菜心施用鸡粪田间实验,探讨对菜心产量及重金属含量的影响.结果表明,第1、3茬所有施用鸡粪处理菜心产量比单施无机肥处理降低,第2茬则提高,第4茬鸡粪与无机肥配施处理提高了菜心产量.不同茬别菜心产量差别较大,第2茬显著高于其它茬别.从不同处理4茬菜心重金属平均含量来看,施用鸡粪可提高As、Zn含量,降低Cr、Cd含量,对Pb含量无明显影响,配施鸡粪提高Cu含量.除第2茬因产量稀释作用影响外,不同茬别所有处理菜心As、Pb、Cr、Cu、Zn平均含量随施用茬数增加而提高,Cd平均含量则下降.建议在无公害或绿色食品生产中避免一次性大量施用或连续施用养殖场禽畜粪.     

水溶性有机物在土壤剖面中的分馏及对Cu迁移的作用

通过室内土柱试验研究了DOM在土壤剖面中的“分馏”作用,DOM在纵向运移过程中的穿透行为及对污染的红壤和潮土中重金属Cu溶出效果的影响.结果表明,绿肥和猪粪DOM经过土柱后极性都有所降低,在潮土上的降低幅度较大,分别为11.4%和10.72%;DOM能够明显地增加污染土壤中Cu的溶出,且这种作用效果与DOM及土壤的性质有关,绿肥DOM的作用效果比猪粪DOM的强,整个淋洗过程中潮土上Cu的平均溶出量是红壤上的4.37倍(绿肥DOM)和3.03倍(猪粪DOM);由于微生物对DOM的分解作用,降低了DOM对土壤中Cu的溶出效果.     

Soil quality response to long-term nutrient and crop management on a semi-arid Inceptisol

The soil quality concept provides a tool to help quantify the combined biological, chemical and physical response of soil to crop management practices. Our objective was to quantify effects of 10 fertilizer and farm yard manure (FYM) treatments applied for 31 years to a rotation that included maize (Zea mays), pearl millet (Pennisetum americanum), wheat (Triticum aestivum) and cowpea (Vigna unguiculata) on an Inceptisol at the Indian Agricultural Research Institute in New Delhi, India. A soil quality index (SQI) based on six soil functions (i.e. the soil's ability to: accommodate water entry, facilitate water movement and storage, resist surface degradation, resist biochemical degradation, supply plant nutrients and sustain crop productivity) was derived for each treatment using bulk density, water retention, pH, electrical conductivity (EC), plant-available nutrients, soil organic matter (SOM), microbial biomass, soil enzymes and crop yield. SQI ratings ranged from 0.552 (unfertilized control) to 0.838 for the combined NPK fertilizer plus manure treatment. Comparisons among treatments indicated that SQI increases associated with the combined (NPK + manure) treatment were distributed as follows: N (7.1% increase), P (7.8%), K (14.4%), Zn (4.8%) and manure (15%). The control (−11.4%) and N alone (−5.1%) resulted in degradation compared to a reference soil (no fertilizer/manure, no crop), and NP alone or sub-optimal rates of NPK were on the verge of degradation. Hand weeding and sulphur application had no measurable effect on SQI. High K fixing capacity was a limiting factor for these soils, even when FYM was applied. The lower SQI rating associated with N or NP-only treatments suggests that two of the most common fertilizer management practices in India may not be sustainable. The SQI was calculated without the weighting factors too, which revealed that the weighting factors did not affect the relative ranks of individual treatments.     

稻田土壤β-1, 4-葡萄糖苷酶活性对温度变化的响应特征

温度是土壤酶活性的关键非生物影响因子,调控着土壤物质周转过程.为了探究温度变化对稻田土壤有机质周转及其关键胞外酶活性的影响,设计室内培养试验,分别在5、15、25和35℃下测定亚热带稻田土壤BG（β-1,4-葡萄糖苷酶）活性,探究温度对土壤胞外酶活性及其与碳氮转化过程的影响特征.结果表明:稻田土壤中w（DOC）（DOC为可利用态碳）、w（NH₄+-N）和w（MBC）（MBC为微生物生物量碳）在5~25℃下随着培养时间的增加而降低.在第15天时BG活性达到306.57~437.75 nmol/（g·h）,并随温度的增加表现为先增后减,在第3、75天时,25℃下BG活性为184.46~207.60 nmol/（g·h）.土壤酶活性的Q₁₀（温度敏感性）在15℃升至25℃时表现出正响应（Q₁₀=1.5）,而在5~15℃和25~35℃时Q₁₀ < 1,表现为消除效应.土壤酶活性的变化是多因素共同影响的结果,温度作为关键影响因子,升温显著改变了土壤中w（DOC）、w（NH₄+-N）、w（MBC）、w（MBN）（MBN为微生物生物量氮）,进而影响土壤BG活性;土壤中w（MBC）对BG活性具有直接的显著负影响作用.研究显示,对参与稻田土壤碳转化BG酶活性的温度敏感性及其与土壤关键理化因子之间的耦合关系进行量化,有助于深入开展水稻土碳循环及其调控机制研究.      

生物堆修复城市多环芳烃污染土壤的调控研究

土壤多环芳烃(PAHs)污染已成为一种严重的全球性城市环境问题。以通风时间、绿肥、无机营养剂和疏松剂含量为调控因素,利用现场规模的正交试验进行了生物堆修复城市多环芳烃污染土壤的调控研究。结果表明,所有生物堆处理对土壤PAHs的去除均有一定促进作用,75 d时平均降解率为30.63%~80.41%,且深层土壤降解率比表层土壤高8.55%;运行期间各调控因素对不同深度土壤PAHs降解的影响程度和作用规律各不相同,其中通风时间始终是主导因素,且通风时间越长,降解效果越好;生物堆的最佳运行条件总体上为通风时间3 h、绿肥3.5%、营养剂0.2%、疏松剂18%(表层土壤)或14%(深层土壤)。因此,利用生物堆修复城市PAHs污染土壤是有效的,且增加通风时间是提高其修复效率的优先调控方式。     

堆肥化处理TNT红水污染土壤

DNTS[二硝基甲苯磺酸盐,主要包括2,4-DNT-3-SO₃-(2,4-二硝基甲苯-3-磺酸盐)和2,4-DNT-5-SO₃-(2,4-二硝基甲苯-5-磺酸盐]是TNT (2,4,6-三硝基甲苯)红水污染土壤中主要污染物质,为研究堆肥化对土壤中DNTS的降解效果,采用有机废物堆肥方法,探讨堆肥化对TNT红水污染土壤中DNTS降解的可行性,以及温度、含水率和pH变化对降解效果的影响.结果表明,有机废物堆肥能处理TNT红水污染土壤,在堆肥60 d内,5个堆肥体系(猪粪+木屑、猪粪+麦壳、污泥+木屑、污泥+麦壳和马粪+木屑)对2,4-DNT-3-SO₃-的降解率为65.5%~88.4%,对2,4-DNT-5-SO₃-的降解率为60.9%~100%.在第4天各堆肥体系的高温阶段(29.7~53.6℃),5个堆肥化体系中2,4-DNT-3-SO₃-总量的49.5%~67.3%被降解,说明各堆体的中温-高温阶段对有机物的降解起重要作用.堆体含水率随堆肥时间的延长呈下降趋势,在堆肥第8天,外源补水至体系含水率为50%,猪粪+麦壳体系对2,4-DNT-3-SO₃-的降解率从70.2%增至88.4%,说明适当的外源补水可提高2,4-DNT-3-SO₃-的降解率.5个堆肥体系中pH均呈初期上升、后期下降并趋于稳定的趋势,但在整个堆肥过程中,堆体pH始终保持在7.3~8.3之间.研究显示,5个堆肥体系中猪粪+麦壳体系对DNTS的降解率最高,分别为88.4%和100%.      

Effects of long-term amendment of organic manure and nitrogen fertilizer on nitrous oxide emission in a sandy loam soil

To understand the effects of long-term amendment of organic manure and N fertilizer on N2O emission in the North China Plain, a laboratory incubation at different temperatures and soil moistures were carried out using soils treated with organic manure （OM）, half organic manure plus half fertilizer N （HOM）, fertilizer NPK （NPK）, fertilizer NP （NP）, fertilizer NK （NK）, fertilizer PK （NK） and control （CK） since 1989. Cumulative N2O emission in OM soil during the 17 d incubation period was slightly higher than in NPK soil under optimum nitrification conditions （25℃ and 60% water-filled pore space, WFPS）, but more than twice under the optimum denitrification conditions （35℃ and 90% WFPS）. N2O produced by denitrification was 2.1-2.3 times greater than that by nitrification in OM and HOM soils, but only 1.5 times greater in NPK and NP soils. These results implied that the long-term amendment of organic manure could significantly increase the N2O emission via denitrification in OM soil as compared to NPK soil. This is quite different from field measurement between OM soil and NPK soil. Substantial inhibition of the formation of anaerobic environment for denitrification in field might result in no marked difference in N2O emission between OM and NPK soils. This is due in part to more rapid oxygen diffusion in coarse textured soils than consumption by aerobic microbes until WFPS was 75% and to low easily decomposed organic C of organic manure. This finding suggested that addition of organic manure in the tested sandy loam might be a good management option since it seldom caused a burst of N2O emission but sequestered atmospheric C and maintained efficiently applied N in soil.     

烟梗生物炭持久性自由基反应活性的比较

本研究选用不同热解温度（300,500和700℃）制备的烟梗生物炭,与有机污染物对硝基苯酚（PNP）进行吸附降解反应,探究反应前后烟梗生物炭上持久性自由基（EPFRs）信号强度与其降解有机污染物活性的关系.结果显示：生物炭中EPFRs信号强度随热解温度的升高而从6.155×10⁴升高至1.343×10⁵后降低至5.458×10⁴,而PNP的液相降解率则表现为随热解温度的升高先保持为31%左右不变后下降至14.64%,表明生物炭的EPFRs信号强度与活性并不成正比.300℃热解制备的生物炭中以氧为中心的自由基可以将电子转移给水中的氧分子生成活性氧并促进PNP的降解.而500与700℃热解制备的生物炭中碳为中心的自由基与污染物进行降解反应后生成了新的自由基并被稳定于生物炭表面,导致其自由基信号增强降解活性却大幅下降.     

一株发酵纤维素产丁酸菌及其代谢动力学特性

为开发降解纤维素产丁酸菌的种子资源,从牛粪、猪粪堆肥、玉米地土壤和腐木混合物的富集样品中分离得到一株厌氧降解纤维素产丁酸菌.该菌株细胞呈杆状,长7.1~9.1μm,直径1.2μm左右,经鉴定为丁酸梭菌(Clostridium butyricum),命名为C. Butyricum DCB.在35℃条件下,菌株DCB在纤维二糖液体培养基中的最大比生长速率为0.6536h^-1,世代时间为1.06h,纤维二糖降解速率为0.1g/(L·h),丁酸生成速率为0.06g/(L·h).该菌株利用纤维素发酵产丁酸的转化率高达0.23g/g,具有良好的开发前景.     

Pre-harvest Viral Contamination of Crops Originating from Fecal Matter

Pre-harvest contamination of fresh produce and fruits is a possible route for viral transmission which should not be ignored. The contamination originates from viruses shed in human or animal fecal materials which eventually reach crops through many steps and hurdles, including spread of viruses into the agricultural environment through leakage of septic tanks/pipes or runoff from animal lagoons, virus survival during biosolids and manure treatment, virus survival and transport in soil and subsequent contamination of irrigation water, and virus transmission to crops through irrigation water, etc. Initially, large quantities of virus particles may be released from infected humans or animals, and then in the environment viruses are gradually inactivated under various natural conditions (e.g., temperature, water activity, microbial activities, etc.) and only a tiny portion of viruses may reach crops and cause the contamination. However, the fact that the infectious dose of some foodborne viruses is as low as 10–100 particles makes the pre-harvest contamination still a threat to human health. In the USA, the Environmental Protection Agency (USEPA) and United States Department of Agriculture (USDA) regulations and guidances on proper treatment and usage of manure and biosolids for agricultural purpose may largely reduce the release of viruses to the environment; however, pre-harvest viral contamination due to fecal matter is not completely avoidable. This review focuses on the current knowledge of pre-harvest viral contamination and describes the complex transmission process regarding the presence and survival of virus in soil and fecal material, the effect of different biosolids/manure treatment on virus inactivation, the transmission of virus from soil to water, the contamination of crops by irrigation water and survival of virus on crops.     

Heavy metal contamination of soils and crops from auto traffic,sewage sludge,pig manure and chemical fertilizer

The present paper describes heavy metal contamination of soils and crops resulting from auto traffic, sewage sludge, pig manure and chemical fertilizers, in three separate experiments.The first experiment revealed that although the ADDT (average annual daily traffic) value of the Agricultural Area was lower, higher concentrations of Cu, Cd, Zn, Pb and Mn were obtained in soil when compared with the Commercial-Residential Area. Contaminations of trace metals from various source, e.g., chemical fertilizer, animal manure, night soil and pesticides of the nearby agricultural land were suspected.The second experiment compared the effects of adding a commercial fertilizer and digested sludge which contain substantial amounts of various trace metals to a sandy loam for growing Chinese radish. The results indicated that repeated applications of the fertilizer elevated the contents of various trace metals in the roots of Chinese radish. The phenomenon was further aggravated when digested sludge was also incorporated.The third experiment compared the contents of trace metals in the root and leaf tissues of tree seedlings (Acacia confusa) added with a single dose of the trace metalenriched fertilizer, and different portions of pig manure compost. It was revealed that the fertilizer-treated tree seedlings had a higher content of trace metals in the tissues than those amended with manure compost. Although the metal contents of soil increased as more manure compost was added, the contents in plant tissues did not increase correspondingly.     

生物炭复合菌剂促进堆肥腐熟及氮磷保留

为减少堆肥的氮素损失并提升磷素有效性,通过堆肥试验研究了添加生物炭复合菌剂对猪粪堆肥腐熟度及氮磷保留的影响.结果表明,在42d堆肥中,对照（CK）、生物炭（B）、菌剂（M）和生物炭菌剂（BM）4个处理组均达到了畜禽粪便无害化卫生要求标准.BM处理组的NH₃和N₂O释放累积量为2.36和0.93g,显著低于CK（8.01和1.31g）,且总氮含量达23.78g/kg,显著高于CK（18.36g/kg）.堆肥结束时,CK、B、M和BM处理的TP含量分别为16.41,17.16, 18.51及19.16g/kg,且BM组OP含量增加77.60%,显著高于CK（50.66%）.堆肥后,磷素有效性增加,并以M和BM的变化趋势最为显著,各处理的缓效磷和有效磷所占比例加合顺序为：BM（42.94%） > M（39.80%） > B（37.29%） > CK（31.51%）.研究表明,生物炭复合菌剂在促进堆肥腐熟和氮磷保留中具有良好的效果.     

畜禽粪便有机肥中重金属在土壤剖面中积累迁移特征及生物有效性差异

通过田间小区试验,定量化研究连续4 a施用不同量猪粪、鸡粪有机肥后不同重金属在土壤剖面中迁移积累特征及生物有效性差异,为科学确定农田土壤重金属的环境容量提供依据.结果表明,连续4 a施用猪粪显著增加了耕层土壤中Cu、Cd的含量,与对照比增幅分别是43.8%~118.6%和28.2%~44.9%.施用鸡粪显著增加耕层土壤Cu、Zn、Cd、Cr、As、Pb含量,增幅分别为29.7%~48.5%,239%~456%,19.9%~80.8%,40.4%~163%,11.8%~22.0%和80.3%~95.0%.猪粪带入的Cu、Zn在耕层土壤中的积累率分别为76.4%~119%和14.2%~20.4%,鸡粪带入Cu、Zn在耕层土壤中的积累率分别为72.1%~88.7%和63.9%~78.9%.施用高量的猪粪、鸡粪Cu、Zn存在明显向土壤深层迁移现象,连续4 a施用60 t·hm^-2的猪粪,Cu迁移到了15~30 cm土层.连续4 a施用60 t·hm^-2鸡粪,Zn迁移到了30~60 cm土层.但连续4 a施用不同量猪粪和鸡粪,土壤剖面中耕层以下土层中Cd、Cr、As、Pb含量均没有显著增加.连续4 a施用鸡粪显著降低小麦籽粒中Cu、Cd含量,显著增加了小麦籽粒中Zn、Cr含量和小麦秸秆中Zn含量,连续4 a施用猪粪显著降低了小麦籽粒中Zn含量,60 t·hm^-2猪粪显著增加了小麦子粒中As含量,猪粪处理还显著增加了秸秆中Cu、As含量.4 a小麦收获累计对有机肥带入重金属的携出率小于6%.小麦籽粒对Cu、Zn的累计携出量高于秸秆,对Cd、Cr、As、Pb携出量低于秸秆,有机肥用量越高,小麦收获对有机肥带入重金属的携出率越低.确定农田土壤重金属环境容量时应考虑不同有机肥中重金属在土壤剖面中积累特征和向下迁移量.