有机肥与无机肥配施对菜地土壤N2O排放及其来源的影响

该研究采用同位素自然丰度法,通过室内培养试验研究北京地区菜地有机肥和无机肥配施对土壤释放N2O及同位素位嗜值SP（site preference）的影响,以期获得不同肥料及其配比下土壤N2O的来源及变化规律。结果表明：施用无机肥释放的N2O显著高于有机肥,其累积排放量是有机肥的6.63倍,且无机肥施用比例越高,排放量越大;各肥料组合在施用后7天内均以反硝化作用生成N2O为主,贡献最高达到78.89%,SP为6.97‰,之后硝化作用逐渐增强并成为主要途径,最高占比达76.48%,SP为25.24‰;培养期内施用无机肥可以促进反硝化作用,平均占比52.98%,SP为15.52‰,而有机肥会使硝化作用增强,平均占比71.35%,SP为23.55‰。因此,在北京潮褐土地区菜地土壤施用有机肥对N2O有良好的减排效果,可为蔬菜生产中肥料的合理应用提供科学依据。     

设施和露天栽培下有机菜地土壤氮素矿化和硝化作用的比较研究

矿化作用和硝化作用是土壤氮素转化的主要途径,通过室内培养试验,对设施和露天栽培方式下有机菜地土壤氮素的矿化与硝化作用进行了比较研究。结果表明,除培养第1d外,设施有机菜地土壤氮素矿化量、矿化率在整个培养期间都显著高于露天有机菜地土壤;设施有机菜地土壤硝化量、硝化率在培养前两周内高于露天有机菜地土壤;设施有机菜地土壤矿化与硝化作用总体比露天有机菜地土壤强烈。矿化作用可能与全氮、C/N、微生物活性关系密切,而硝化作用强弱可能与微生物活性有关。无论施肥与否,设施有机菜地土壤N2O排放速率在培养期间总体高于露天有机菜地土壤,前者N2O累积排放量显著高于后者,这可能与土壤C/N有关。     

有机无机肥配施对菜地土壤氮素径流流失的影响

利用田间小区试验,研究了无机肥配施不同用量有机肥对菜地土壤氮素径流流失的影响.结果表明,施肥显著增加菜地土壤氮素径流流失量.单施无机肥处理总氮、硝态氮和铵态氮流失量均最高,分别为4.20,1.22,2.30kg/hm2.配施有机肥可降低不同形态氮流失量,且随有机肥配施量增加而显著降低.配施高量有机肥处理总氮、硝态氮和铵...     

不同菜地土壤硝化与反硝化活性

硝化作用和反硝化作用是氮素气态损失的主要途径,在实验室培养条件下,研究了3种菜地土壤之间硝化反硝化活性的差异,反硝化作用利用乙炔抑制培养法对其进行测定。结果表明,培养33d后红泥土、灰沙土和灰泥土的氮素硝化率均很高,分别为96．1％、88.3％和70．4％,其中红泥土与灰泥土的硝化率差异达到了极显著水平（P〈0．01）,而灰沙土与红泥土、灰泥土之间的差异不显著（P〉0．05）。pH值最高和最低的菜地土壤其硝化率分别表现出最高和最低,值得注意的是,在pI-14．61条件下灰泥土的硝化率可达70．4％。氮肥的施用显著或极显著增加了3种土壤硝化过程的N2O排放量,占施氮量的0．59％-0．70％。3种菜地土壤之间氮肥的反硝化活性表现为灰泥土〉红泥土〉灰沙土,其差异也极显著（P〈0．01）,氮肥的反硝化损失量占施氮量的-0．02％-0．20％。土壤硝化和反硝化氮素损失累积量随时间t的变化均符合修正的Elovich方程：y=bln（t）＋a。     

有机无机肥配施对菠萝蜜种植土壤线虫群落的影响

为探究有机肥施用对菠萝蜜种植土壤线虫群落结构的影响,以马来西亚1号菠萝蜜嫁接苗为试验材料,设置CK(不施肥)、100CF(100%化肥)、30OM(30%有机肥+70%化肥)、50OM(50%有机肥+50%化肥)、70OM(70%有机肥+30%化肥)、100OM(100%有机肥)6个处理,比较不同施肥方式下菠萝蜜幼苗生长及土壤线虫群落的差异。结果表明:与不施肥和纯施化肥相比,有机-无机配施显著促进菠萝蜜幼苗生物量积累,增加土壤pH、有机质含量。其中食微线虫和杂食/捕食线虫的占比随着有机肥用量的增加呈增长趋势,而植食性线虫占比呈下降趋势。增施有机肥能显著提高土壤线虫多样性指数(H′)和均匀度指数(J′),土壤食物网以细菌主导的分解途径占更大比例。β多样性分析结果表明,除50OM和100CF处理构建的线虫群落结构相似外,其他处理的线虫群落结构差异显著。菠萝蜜幼苗地上部干重与土壤食细菌线虫丰度、有机质和pH呈显著正相关,而植食性线虫丰度与土壤pH、有机质、碱解氮含量和食微线虫丰度呈显著负相关。食细菌线虫丰度与土壤有机质和pH呈显著正相关。有机-无机配施能够提高土壤线虫多样性和均匀度,平衡不同...     

长期有机–无机肥配施对农田杂草土壤种子库的影响

为揭示长期有机-无机肥配施处理下农田杂草土壤种子库的特征变化规律,本研究通过田间长期定位施肥模式试验,运用群落生态学方法研究了小麦-大豆轮作制度下大豆种植季7种施肥处理区杂草土壤种子库的结构及其生物多样性特征。结果表明,土壤样品中共检出杂草种子16种,隶属于10科; 土壤种子库总密度分布在15995~106300 grain/m2范围。长期有机-无机肥配施处理区的杂草土壤种子库优势物种组成较为简单,优势种为12种,配施麦秸处理区主要以栗米草为主,配施粪肥处理区主要以水苋菜为主; 土壤种子库的密度显著降低至15995~41900 grain/m2范围; 物种丰富度降低至7.67~9.33范围,并且将物种多样性和均匀度指数维持在休闲与纯化肥处理区之间（1.5~2.0和0.6~0.8）。长期配施麦秸、 粪肥均显著影响土壤杂草土壤种子库的结构特征,且麦秸与粪肥品种间差异的影响大于麦秸施用量差异的影响。因此,本研究认为有机-无机肥配施既有利于作物的优质高产,也可以通过调整有机肥种类以及与施用量来调控杂草土壤种子库,实现经济效益和生态效益的双赢。     

菜地土壤氮素矿化和硝化作用的特征

采用培养试验对南京郊区 6 对菜地土和水稻土的土壤 N 素矿化和硝化作用特征进行了研究。菜地土为相同类型水稻土改种蔬菜约 20 年的土壤。结果表明,培养 28 天期间,6 对供试土壤中有 4 对土壤都是菜地土壤矿化 N 量低于相同类型水稻土,其日矿化速率也低于相应的水稻土,而其他 2 对供试土壤之间无明显差异。大多数菜地土的土壤硝化率低于相应的水稻土。培养28 天时的矿化率和硝化率与土壤 pH、速效 P 呈显著相关。     

不同氮源及秸秆添加对菜地土壤N_2O排放影响

在饱和田间持水量WFPS(water-filled pore space)为75%、温度为25℃的条件下,用室内培养研究设施菜地土壤在不同氮肥种类(硝酸钙CN,碳酸氢铵AB,硫酸铵AS,尿素U,对照CK)和有无秸秆添加情况下N2O的排放特征。培养17天的结果表明,各种肥料类型中,对照和硝态氮肥处理最先出现N2O排放高峰,铵态氮肥处理出现较晚。无论有无秸秆,碳酸氢铵(AB)处理的累积排放量都最高,分别为4.206±0.899和2.159±0.256μg g-1干土,铵态氮肥处理N2O排放量明显高于硝态氮肥。添加秸秆后各处理N2O排放明显增加,比未施秸秆增加1倍多(CN处理除外)。不同处理(CK除外)的N2O累积排放量与时间的关系都可用y=aLn(x)+b表示(P<0.001)。实验还发现,施用氮肥会导致土壤酸化,添加秸秆可改善土壤酸化现象。     

有机无机肥配施对紫色土旱坡地土壤无机磷迁移的影响

为探索长江上游紫色土旱坡地麦玉轮作系统减少农田磷素流失的最佳施肥模式,降低磷对水体富营养化的影响。2011—2015年,以紫色土旱坡地典型农作冬小麦和夏玉米为材料,在西南大学试验农场进行田间定点试验。试验采用随机区组设计,共设置7个田间小区试验,分别为倍量施磷肥(2P)、优化施肥(P)、优化施肥+猪粪有机肥(MP)、优化施肥+秸秆还田(SP)、优化施肥量磷减20%+猪粪有机肥(MDP)、优化施肥量磷减20%+秸秆还田(SDP)、不施磷肥(P0)。测定了各农田土壤基础性质,以及0—20,20—40,40—60cm土层土壤全磷和有效磷含量,并对不同施磷水平以及磷肥减量配施不同有机肥条件下紫色土旱坡地土壤磷素迁移流失进行了原位定点研究。结果表明:不同施肥条件下紫色土旱坡地总磷(TP)和总可溶性磷(TDP)迁移流失量有明显的差异。TP流失量大小依次为2PPMPSPMDPSDPP0。2P处理总磷流失量最高,P处理是SDP和MDP处理的1.5~2倍。TDP流失量大小依次为2PMPPMDPSPSDPP0。坡上除了P0和P处理全磷含量有所减少外,其他各处理全磷含量都呈增加趋势,坡中、坡下的增长幅度要大于坡上,其中坡下处理MP比种植季前增加了0.400g/kg。除了P0处理土壤有效磷含量降低外,其他各个小区处理坡上、坡中、坡下土壤中有效磷含量都呈增加趋势。猪粪有机肥和秸秆还田对土壤中磷素有一定的活化作用,促进了磷素在土壤中的迁移,且猪粪有机肥对土壤磷素活化作用更强。化学磷肥减量并配施有机肥是应对农业面源污染"控源节流"的较好措施。     

有机无机肥配施对玉米-豇豆种植系统土壤N2O排放的影响

在等施氮量条件下,比较有机肥与无机肥施用后旱地玉米-豇豆复种系统土壤硝化与反硝化作用、N_2O排放与作物产量的变化,有助于正确认识肥料施用对N_2O排放的影响,为制定大田合理的丰产减排措施提供理论依据。本研究通过田间试验,利用静态箱技术和BaPS气压过程分离技术研究了不同肥料类型处理(无机肥、有机肥、有机无机肥配施)下玉米-豇豆种植系统土壤N_2O排放、硝化与反硝化作用的变化特征。结果表明:1)相对于单施无机肥或有机肥,有机无机肥配施可显著降低土壤硝化作用速率;在玉米生长季,有机无机肥配施处理平均土壤硝化作用速率分别比化肥和有机肥处理显著降低了28.74%和13.96%,豇豆生长季显著降低了24.66%和13.28%。土壤反硝化作用速率在各施肥处理间差异不显著。2)有机无机肥配施显著降低土壤N_2O排放;在玉米生长季,有机无机肥配施处理分别比无机肥处理和有机肥处理显著降低33.44%和32.29%,在豇豆生长季分别显著降低27.00%和15.14%。3)相关分析表明,土壤N_2O排放与硝化作用速率呈极显著相关,而与反硝化作用速率呈不显著相关。4)有机无机配施处理玉米和豇豆产量最高。因此,有机无机肥配施能有效降低玉米-豇豆系统土壤N_2O排放和提高作物产量,是一项丰产低N_2O排放的施肥技术,但长期有机无机肥配施对土壤N_2O排放和作物产量的影响还需要进一步研究。     

有机无机肥料配合施用对设施菜田土壤N2O排放的影响

采用静态箱气相色谱法研究了有机无机肥料配合施用对设施菜田土壤N2O排放的影响。结果表明: 1）设施芹菜和番茄施基肥后57 d（灌溉后13 d）出现土壤N2O排放通量峰值,追肥后（施肥与灌溉同步）1 d出现土壤N2O排放通量峰值; 芹菜季和番茄季施用基肥后20 d内N2O排放量分别占当季总排放量的40%65%左右,是土壤N2O主要排放期。2）施用基肥后至定植灌水前各处理土壤N2O排放量逐渐降低,灌水后N2O排放通量迅速上升。各处理土壤N2O排放通量与土壤含水量之间呈显著相关,相关系数在0.43~0.72之间。3）土壤N2O排放主要发生在番茄季,番茄生育期各处理土壤N2O总排放量是芹菜生育期的3.1倍; 各处理土壤N2O排放通量与5 cm土层温度之间总体上呈显著相关,相关系数在0.40~0.58之间。4）设施菜田大幅减施化肥的有机无机肥配合施用模式可显著降低土壤N2O排放量和肥料损失率,芹菜季和番茄季土壤N2O排放量较习惯施肥处理分别降低66.3%和85.1%,肥料损失率分别降低45.2%和74.9%。5）等氮量投入时,施用秸秆较施用猪粪可有效降低土壤N2O排放,芹菜季和番茄季分别降低43.4%和74.2%。     

定位化肥牛粪配施对设施蔬菜产量和土壤肥力的影响

采用定位施肥方式,连续多次在同一保护地块化肥减量配施牛粪,通过大棚蔬菜种植试验,设置对照(CK,单施复合肥2250 kg/hm2)、低(L,66.7％CK+有机肥30000 kg/hm2)、中(M,33.3％CK+有机肥4500 kg/hm2)及高(H,单施有机肥60000 kg/hm2)4个不同化肥减量配施有机肥底肥...     

Fulvic acid displaces manure to improve soil in vegetable greenhouse

Acid soil has led to a significant decrease in vegetable yield in high-yield greenhouse vegetable production system. Chicken manure and fulvic acid (FA) application experiment was conducted to evaluate the effects on chemical properties of soil in vegetable greenhouse so as to confirm whether FA could replace chicken manure in acid soil amelioration under the same addition levels of nutrient, when compared to the effect of chemical fertilizers application alone on acid soil improvement. The results showed that the pH of soil added with chicken manure and FA, respectively, increased from the original value of 5.4 to 5.99 and 6.32 at the end of the experiment, while soil pH applied only with chemical fertilizers decreased to 5.43. Correlation analysis indicated that cation exchange capacity (CEC) of soil was positively correlated with soil pH buffering capacity. The peak values of soil CEC and pH buffering capacity occurred in April each year and subsequently tended to decrease in August and December throughout the experiment. Data demonstrated that chicken manure and FA in combination with soil contributed to soil base saturation that increased from 26.5%, 33.8% to 36.7%, 45.9% in chicken manure and FA treated soil during December 2011 to December 2012, respectively; however, chemical fertilizers displayed an adverse effect on soil base saturation that decreased from 17.1% to 5.6% on the same time period. Exchangeable aluminum (Al) concentration showed a weak but significant increase by 5.2% on August 2012 in comparison to April 2012, as chemical fertilizers were added into soil alone. Unlike to chemical fertilizer, chicken manure and FA significantly decreased soil exchangeable Al concentration from the original value of 5.37 cmol kg^?1 to 4.56 and 4.22 cmol kg^?1 at the end of experiment respectively. Compared to total yield treated solely with chemical fertilizers, chemical fertilizers combination with chicken manure or FA resulted in an increase in total yield in 2011 and 2012. Although chicken manure and FA possessed the same trend of improving acidic soil in vegetable greenhouse, a greater contribution was attributed to FA due to its lower mineralization rate of organic matter. Therefore, it was suggested that FA could completely displace chicken manure in improvement in acidic soil in vegetable greenhouse.     

Mitigating nitrous oxide emissions from a maize-cropping black soil in northeast China by a combination of reducing chemical N fertilizer application and applying manure in autumn

Abstract

Nitrous oxide (N₂O) emissions from agricultural soils, mainly caused by chemical nitrogen (N) fertilizer inputs, are major sources of N₂O in Chinese terrestrial ecosystems. Thus, attempts to reduce N₂O emissions from agricultural soils by optimizing N applications are receiving increasing attention. Further, organic fertilizers are being increasingly used in China to improve crop production/quality and prevent or reduce soil degradation. However, organic and chemical fertilizers are often both applied in spring in northeast China, which promotes N₂O emissions and may be sub-optimal. Therefore, we hypothesized that reducing applications of chemical fertilizer N and applying manure in autumn could be an effective strategy for mitigating N₂O emissions from cropped soils in the region. To test this hypothesis, we established a field trial to investigate the effects of different combinations of chemical N fertilizer applications and animal manure in autumn on both N₂O emissions and maize (Zea mays L.) grain yields in northeast China. The treatments, expressed as NxMy (where Nx and My denote the total amounts of chemical fertilizer nitrogen (N) and manure (M) applied in kg N ha^?1 and m³ M ha^?1, respectively), were N₀M₀, N₂₃₀M₀, N₂₇₀M₁₂, N₂₃₀M₁₅, N₃₂₀M₁₈ in 2010 and N₀M₀, N₂₃₀M₀, N₂₀₀M₁₂, N₂₀₀M₁₅, N₂₈₀M₁₈ in 2011. Measurements of the resulting N₂O emissions showed that pulse fluxes occurred after each chemical N fertilizer application, but not after manure inputs in autumn or during soil-thawing periods in the following spring. Emission factors for the chemical fertilizer N were on average 1.07% (1.00?1.10%) and 1.14% (0.49?1.83%) in 2010 and 2011, respectively. Furthermore, by comparing the nine pairs of fertilization treatments, the relative increase in cumulative nitrous oxide-nitrogen (N₂O-N) emissions was found to be proportional to the relative increase in urea application, but independent of the amount of autumn-applied manure. These findings imply that N₂O emissions from fertilized agricultural soils in northeast China could be mitigated by supplying manure in the autumn and reducing the total amount of chemical N fertilizer applied in the following year. Although no significant difference in maize grain yield was found among the fertilization treatments, the grain yield-scaled N₂O emissions for the treatments with a lower chemical N application (e.g., N₂₃₀M₁₅ and N₂₀₀M₁₅ treatments) were significantly lower than those with a higher chemical N application (e.g., N₃₂₀M₁₈ and N₂₈₀M₁₈ treatments). Meanwhile, under the condition of the same application amount of chemical fertilizer N, the grain yield-scaled N₂O emission decreased with the increase of manure application rate. Thus, the results support the hypothesis that combining reductions in chemical N fertilizer and applying manure in autumn could be an effective strategy for mitigating N₂O emissions from N-fertilized soils in northeast China.     

Gaseous and leaching nitrogen losses from no-tillage and conventional tillage systems following surface application of cattle manure

Previous studies have demonstrated inconsistent results on the impact of tillage systems on nitrogen (N) losses from field-applied manure. This study assessed the impact of no-tillage (NT) and conventional tillage (CT) systems on gaseous N losses, N₂O:N₂O + N₂ ratios and NO₃⁻-N leaching following surface application of cattle manure. The study was undertaken during the 2003/2004 and 2004/2005 seasons at two field sites in Nova Scotia namely, Streets Ridge (SR) in Cumberland County and the Bio-environmental Engineering Centre (BEEC) in Truro. Results showed that the NT system had higher (p < 0.05) NH₃ losses than CT. Over the two seasons, manure incorporation in CT reduced NH₃ losses on average by 86% at SR and 78% at BEEC relative to NT. At both sites and during both seasons, denitrification rates and N₂O fluxes in NT were generally higher than in CT plots, presumably due to higher soil water and organic matter content in NT. Over the two seasons, mean denitrification rates at SR were 239 and 119 g N ha⁻¹ d⁻¹, while N₂O fluxes were 120 and 64 g N ha⁻¹ d⁻¹ under NT and CT, respectively. At BEEC mean denitrification rates were 114 and 71 g N ha⁻¹ d⁻¹, while N₂O fluxes were 52 and 27 g N ha⁻¹ d⁻¹ under NT and CT, respectively. Conversely, N₂O:N₂O + N₂ ratios were lower in NT than CT suggesting more complete reduction of N₂O to N₂ under NT. When averaged across all soil depths, NO₃⁻-N was higher (p < 0.05) in CT than NT. Nitrate-N decreased with depth at both sites regardless of tillage. In most cases, NO₃⁻-N was higher under CT than NT at all soil depths. Similarly, flow-weighted average NO₃⁻-N concentrations in drainage water were generally higher under CT. This may be partly attributed to higher denitrification rates under NT. Therefore, NT may be a viable strategy to remove NO₃⁻-N from the soil, and thus, reduce NO₃⁻-N contamination of groundwater. However, it should be noted that while the use of NT reduces NO₃⁻-N leaching it may come with unintended environmental tradeoffs, including increased NH₃ and N₂O emissions.     

区分土壤中硝化与反硝化对N2O产生贡献的方法

土壤是产生N₂O的最主要来源之一。硝化和反硝化反应是产生N₂O的主要机理，由于硝化和反硝化微生物同时存在于土壤中，因而硝化和反硝化作用能同时产生N₂O。N₂O的来源可通过使用选择性抑制剂，杀菌剂以及加入的标记底物确定。通过对生成N₂O反应的每一步分析，主要从抑制反应发生的催化酶和细菌着手，总结了测量区分硝化、反硝化和DNRA反应对N₂O产生的贡献方法。并对¹⁵N标记底物法，乙炔抑制法和环境因子抑制法作了详细介绍。     

沼肥替代化肥对设施蔬菜产量和土壤养分及重金属累积的影响

针对盲目施用沼肥可能带来的土壤环境问题,该研究采用5年8茬的设施番茄-甜椒田间轮作试验,研究不同沼肥和化肥配比对蔬菜产量、设施土壤氮磷养分及重金属累积的影响.结果表明:在等氮钾养分投入下,沼肥和化肥以不同比例配施的各处理没有影响蔬菜产量;氮素盈余和0~180cm土层土壤全氮含量随沼肥施用比例增加没有显著差异;磷素盈余随沼肥施用比例增加显著增加,完全沼肥处理0~30cm土层土壤Olsen-P及CaCl2-P含量分别达到151和8.0mg/kg,高于其他2个处理,且明显超出环境阈值.与完全沼肥处理相比,减量沼肥施用(3/5沼肥处理)明显降低了土壤氮素淋洗风险和磷素累积.与不施肥处理相比,施用沼肥后30~60、60~90、150~180cm土层土壤全Hg含量均低于不施肥处理;除30~60cm土层使用沼肥处理土壤中全As含量显著高于不施肥处理,其他土层各处理间均没有显著差异,而完全沼肥处理全Cr、全Cd、全Pb含量有所下降,且全Pb含量下降最为显著,但均没有出现重金属污染风险.沼肥替代化肥施用可有效实现废弃物中的养分资源循环利用,但增加菜田土壤磷素累积和淋失风险,本研究为设施菜田合理施用沼肥提供技术支持,为实现沼肥资源的循环利用和化肥替代模式提供理论参考.     

有机肥与无机肥在提高土壤肥力中的作用

以在山东禹城试验区持续近20年的定位试验为依据，对长期施用有机肥、无机肥、有机无机结合等不同施肥条件下的土壤养分演变进行了系统总结。结果表明，在同等施肥情况下，有机肥不但在增加土壤有机营养，改善土壤有机质质量等方面具有极其显著的作用，而且随着年限的增长，在增加土壤速效养分方面，有机肥的效果也逐渐超过无机肥。