氮肥与有机肥配施协调土壤固定态铵与可溶性氮的研究

【目的】 土壤固定态铵是肥料氮的一个“临时贮藏库”,可逐渐释放以供作物利用,土壤可溶氮则是土壤固定态铵的重要来源,因此研究设施条件下氮肥与有机肥配施对土壤固定态铵和可溶性氮含量的动态变化以及相互关系的影响,对于设施生产中安全高效的施肥管理有着重要意义。 【方法】 以番茄为试材,温室内连续两年进行田间小区试验,设不施肥(CK)、施N量0、187.5、375. 562.5 kg/hm2 (N0、N1、N2、N3)、单施有机肥(M,75000 kg/hm2)以及有机肥与氮肥配施处理(MN0、MN1、MN2、MN3)。分析了土壤固定态铵和可溶性氮(土壤矿质氮和可溶性有机氮)含量动态变化。 【结果】 施肥显著提高了0-30 cm土层土壤固定态铵和可溶性氮的含量(P < 0.01);各施肥处理均以第1穗果膨大期时含量最高。总体来看,不施有机肥条件下,土壤固定态铵和矿质氮、可溶性有机氮的含量均以施N 375.0 kg/hm2处理为最高,而在氮肥与有机肥配施条件下,以施N 375.0 kg/hm2与有机肥75000 kg/hm2配施处理和施N 562.5 kg/hm2与有机肥75000 kg/hm2配施处理的土壤固定态铵和矿质氮、可溶性有机氮含量为最高,但未发现氮肥施用量对土壤固定态铵含量产生显著影响;除收获期20-30 cm土层外,整个生长季内土壤固定态铵和矿质氮含量之间均有显著的正相关关系(P < 0.05),部分土层土壤固定态铵与可溶性有机氮之间也有显著的正相关关系(P < 0.05)。 【结论】 设施番茄栽培条件下,土壤固定态铵和可溶性氮在土壤氮素的固持与释放方面极显著相关,施无机N 375.0 kg/hm2配合有机肥75000 kg/hm2,可较好地提高土壤中的氮的有效性,更好地协调土壤供氮能力。     

基于钾平衡和氮淋失风险的红壤猪粪安全用量

我国红壤区土壤普遍缺钾。通过8 a猪粪施用试验,研究了长期不施肥,长期施低量有机肥钾（59?kg/(hm2·a)）,高量有机肥钾（237?kg/(hm2·a)）,高量有机肥钾+石灰（有机肥钾237?kg/(hm2·a)＋石灰1?000?kg/(hm2·a)）对红壤旱地钾平衡的影响,并结合氮淋失风险制定有机肥钾安全用量。研究表明,红壤旱地长期有机肥施用提高了土壤供钾能力,而不会增加钾淋失。施入土壤的有机肥钾超过69%被作物吸收,但低量有机肥处理导致土壤钾库不断耗竭,而高量有机肥和高量有机肥+石灰处理每年可向土壤补充钾48～57?kg/hm2。针对单作玉米系统,保障作物钾需求和土壤钾库平衡的有机肥施钾量为180?kg/hm2。若考虑有机肥施用的硝酸盐淋失风险,有机肥施钾量不能高于155?kg/hm2,同时需补施25?kg/hm2化肥钾满足作物生长、预防土壤钾库耗竭。     

长期施肥下潮土全氮、碱解氮含量与氮素投入水平关系

通过长期肥料定位试验,对不同施肥处理下潮土全氮和碱解氮含量演变特征及其与氮素投入水平的关系进行研究。结果表明,不施氮肥处理,土壤全氮和碱解氮含量基本保持平衡或者缓慢增加;长期施用化学氮肥处理,土壤全氮和碱解氮含量均有所增加;施用有机肥和秸秆还田处理,土壤全氮和碱解氮含量均显著提高。单施化学氮肥处理每投入氮素1 kg/hm2,土壤全氮含量增加0.017 mg/kg;而氮磷钾化肥配施有机肥和氮磷钾化肥并秸秆还田处理每投入氮素1 kg/hm2,土壤全氮含量分别增加0.049和0.035 mg/kg。施氮磷钾处理每投入氮素1 kg/hm2,土壤碱解氮含量增加0.001 mg/kg;而化肥配施有机肥或玉米秸秆处理每投入氮素1 kg/hm2,土壤碱解氮含量均增加0.004和0.004 mg/kg。总的来说,施用化学氮肥、有机肥配施化肥及秸秆还田处理增加氮素投入量均可以提高土壤全氮及碱解氮含量,且有机肥配施化肥及秸秆还田处理优于单施化肥。综上所述,增施有机肥及秸秆还田对于提升土壤肥力及实现农业可持续发展具有深远意义。     

长期不同施肥措施下黑土作物产量与养分平衡特征

为了明确长期不同施肥措施下黑土作物产量及养分平衡特征,利用开始于1979年的哈尔滨黑土肥力长期定位试验,以小麦-大豆-玉米轮作(3a)为一个周期,选取对照(不施肥,记作CK)、常量氮磷钾化肥配施(小麦施N、P2O5量分别为150、75 kg/hm2,大豆施N、P2O5量分别为75、150 kg/hm2,玉米施N、P2O5量分别为150、75 kg/hm2,K2O共施75 kg/hm2,记作NPK)、常量有机肥(施肥18 600 kg/hm2,记作M)、常量化肥有机肥配施(化肥施量同NPK,有机肥施量同M,记作MNPK)和二倍量氮磷化肥有机肥配施(小麦施N、P2O5量分别为300、150 kg/hm2,大豆施N、P2O5量分别为150、300 kg/hm2,、玉米施N、P2O5量分别为300、150 kg/hm2,有机肥共37 200 kg/hm2,记作M2N2P2)5个处理,研究了不同作物的平均产量、产量年际变化和土壤养分表观平衡。结果表明:1)较CK,长期平衡施用化肥或化肥配施有机肥提高了作物产量,多年平均增产率分别在82.5%~91.6%(小麦)和35.6%~40.9%(玉米)之间。长期不同施肥措施增产效果表现为M2N2P2MNPKNPKM,有机无机肥配施与单施化肥处理间作物产量差异不显著。2)长期不施肥处理小麦和玉米产量随试验年限推移呈下降趋势,降幅分别为13.93和42.61 kg/(hm2·a),大豆则以7.409 kg/(hm2·a)的速率增加。施肥处理小麦、大豆和玉米产量随试验年限的增加呈总体上升的趋势。3)在该试验条件下,长期施用常量化肥处理(NPK)和常量化肥有机肥配施处理(MNPK)土壤氮亏缺量分别为29.7和17.5 kg/hm2,磷盈余量分别为33.4和61.2 kg/hm2。各处理土壤中钾素均表现为亏缺,亏缺量在30.4~73.0 kg/hm2之间。MNPK处理氮、钾供应状况有所改善,较NPK处理分别增加12.2和27.6 kg/hm2。4)作物产量与土壤有机质、碱解氮、有效磷、降雨量、生育期日平均气温呈显著正相关关系(P0.05)。5)在黑土小麦-大豆-玉米典型轮作制度下,基于土壤养分平衡特征提出"稳氮、减磷和增钾"的施肥策略。该研究为评价和建立长期施肥模式、促进粮食持续生产提供依据。     

长期秸秆还田对华北潮土肥力、 氮库组分及作物产量的影响

【目的】近年,华北小麦-玉米轮作系统秸秆全量还田已逐步普及,但秸秆还田下土壤氮库组成的变化并不清楚。本文利用肥料定位试验,研究了长期秸秆还田(32年)对华北潮土肥力、 氮库组分和作物产量的影响。【方法】研究选用河北省衡水旱作试验站长期定位试验的不施肥(对照CK)和等量氮、 磷肥用量下的0kg/hm2(S0)、 2250 kg/hm2(S1)、 4500 kg/hm2(S2)和9000 kg/hm2(S3)秸秆还田处理。于2012年小麦收获后采集各处理020 cm土样,利用新鲜土样测定微生物量氮、 NH+4-N和NO-3-N;风干土壤用常规方法测定氮磷钾全养分、 有机质和pH,用Bremner法测定有机氮(酸解氨基酸态氮、 酸解氨态氮、 氨基糖氮和酸解未知态氮),用Silver-Bremner法测定固定态铵。同时结合长期试验数据, 分析长期秸秆还田下有机质和作物产量的变化。【结果】与试验开始前(1981年)相比,长期施用化肥处理的土壤全磷和有机质显著增加,全氮没有明显变化,而全钾出现降低趋势(-3.2%);秸秆用量的增加提高了全氮、 全磷和有机质,降低了pH值,但对全钾没有影响。酸解氨基酸态氮、 酸解氨态氮和未知态氮为潮土有机氮的主要组分;与CK相比,长期施肥提高了土壤有机氮含量,酸解氨基酸态氮、 酸解氨态氮和氨基糖氮均随秸秆用量的增加而增加,而不同施肥处理对酸解未知态氮和非酸解氮没有明显影响。长期化肥施用提高了微生物量氮和晶格固定态铵,秸秆用量的增加进一步提高了微生物量氮,但降低了固定碳铵。施肥没有明显影响NH+4-N含量,但长期施用化肥提高了NO-3-N含量,且高量秸秆还田对NO-3-N含量的提高具有促进作用。施肥显著提高了作物产量,在施用化肥基础上增施秸秆进一步提高了小麦和玉米产量,且玉米产量随秸秆用量的增加而增加,而高量秸秆还田对小麦产量并没有显著影响。【结论】长期化肥(氮、 磷肥)和秸秆结合施用提高了土壤肥力(主要为氮、 磷), 增加了土壤碳固持,但仅玉米秸秆还田导致了土壤钾消耗,增加钾肥投入维持土壤钾平衡是必要的。长期秸秆还田对酸解氨基酸态氮的贡献高于酸解氨态氮;高量秸秆还田提高了微生物量氮和NO-3-N含量,但降低了固定态铵含量。长期秸秆还田提高了作物产量,而为保证秸秆还田后茬的作物高产,与之配套的还田方法和田间管理是很必要的。     

长期单施有机肥和化肥对土壤养分和小麦产量的影响

【目的】等氮、磷、钾养分投入条件下,探索黄淮海小麦主产区化肥和有机肥施用对小麦的增产效果以及土壤养分的演变规律,为小麦科学施肥及土壤肥力的提升提供依据。【方法】本研究以8年长期定位试验为平台,在冬小麦—夏玉米的传统种植制度下,有机肥和化肥处理均分别设置5个施氮 (N) 量:0、120、240、360、600 kg/hm2,共9个处理。化肥处理的磷、钾用量等同各有机肥处理带入的量。于每年小麦收获期测定小麦产量和土壤养分含量。【结果】在土壤养分方面,土壤有机质、全氮、有效磷、速效钾含量均随有机肥用量的增加而增加,并且呈逐年增长的趋势。化肥在提高土壤有机质及全氮方面与施肥量无明显关系,年际间差异不明显,基本处于同一水平。增施化肥在开始几年能够缓慢提高土壤有效磷和速效钾的养分含量,之后保持稳定。在同一施氮水平下,有机肥处理土壤有机质、全氮、有效磷钾养分含量均显著高于化肥各处理。在作物增产方面,施氮240、360、600 kg/hm2的有机肥处理小麦产量均显著高于施氮120 kg/hm2的有机肥处理,但三个处理之间差异不显著;化肥各处理间均差异不显著。除施N 120 kg/hm2水平下,化肥处理产量显著高于有机肥处理外,其他相同氮水平下化肥处理与有机肥处理无显著差异。【结论】有机肥在培肥土壤方面,效果明显优于化肥,并且有机肥处理随施肥量的增加能够持续提高土壤养分库容量,而化肥对于土壤养分的提升效果不大,始终处于一个相对较为稳定的水平。有机肥和化肥施用均对小麦产量具有显著的提升效果。在N 120 kg/hm2的低氮条件下,化肥对小麦的增产效果优于有机肥,而在高于N 240 kg/hm2的养分条件下,有机肥与化肥增产效果基本一致。另外,当产量提高到一定水平后,增加施肥量无助于作物产量的提高。     

氮肥减施和秸秆还田对土壤固定态铵含量的影响

【目的】固定态铵作为土壤氮素的暂存库,其含量的变化能够影响土壤的保氮供氮功能,而深入探究氮肥减施对土壤固定态铵的影响及其对秸秆还田的响应,可为优化农田氮肥管理提供理论依据。【方法】依托位于中国东北黑土区玉米种植系统连续9年全量玉米秸秆覆盖归还的保护性耕作试验平台,通过设置玉米秸秆不还田(S0)、秸秆还田量33%(S33)和秸秆全量覆盖还田(S100)3个秸秆还田量处理,以及240 kg hm^-2(N240)、190 kg hm^-2(N190)、135kg hm^-2(N135)、0 kg hm^-2(N0)4个氮素施用水平,研究氮素减施3年后土壤固定态铵总量的变化以及不同秸秆还田量对固定态铵的影响。【结果】秸秆不还田时,土壤固定态铵总量随施氮量降低而逐渐下降,且在不施氮肥处理(N0)时显著低于施氮肥处理;在S33N190时土壤-作物系统出现氮素缺乏,并且随施氮量的下降土壤固定态铵降低量与氮素缺乏量之间具有显著的正相关关系。在所有氮肥水平,秸秆还田尤其是全量秸秆还田均有利于缓解固定态铵的释放,但在N135...     

施氮对高肥力稻田氮肥利用率及土壤-水体铵氮损失的影响

研究稻田不同施氮量下的农学效率和环境效应,对水稻高效优质环境保护型生产和合理施肥具有重要意义。在平湖稻区研究了不同施氮下水稻边际利润、最佳经济施肥量以及不同时期氮素利用率、土壤固定态铵、碱解氮及田面水铵氮浓度的动态变化。结果表明,当地水稻最佳经济施肥量为235kg N/hm2;施氮225kg/hm2时当季氮肥利用率仅为31.2%。土壤固定态铵以及碱解氮含量均在水稻生长时期内逐渐下降,但随施氮量的增加而增加。低氮处理促使土壤固定态铵含量有较大增幅,而高氮处理则使土壤碱解氮含量有较大增幅。在水稻不同生长时期的施肥后一个星期内,高于225kg N/hm2处理田面水NH4+-N急剧上升而后急剧下降;而75,150kg N/hm2处理田面水NH4+-N一直低于2mg/L。可见,浙北地区氮肥施用量保持在225kg/hm2为宜,过量施氮(超过225kg/hm2)将超过水稻的正常生长需求,造成土壤固铵量饱和,引起土壤碱解氮含量急剧上升,并导致田面水NH4+-N含量急剧上升。     

长期施肥下潮土速效钾含量与钾素投入水平关系

以郑州潮土肥力与肥料效益长期试验为基础,分析了长期施肥条件下土壤速效钾含量演变特征及其与钾素投入量的关系。结果表明,在不施钾肥条件下,土壤速效钾含量先逐年下降,810年后稳定在60 mg/kg左右; 施用钾肥和有机肥均可以显著提高土壤速效钾含量; 土壤速效钾含量与钾素投入量之间具有显著的正相关关系。单施化肥的NPK处理每投入钾1 kg/hm2,土壤速效钾含量增加0.007 mg/kg; 而化肥配施有机肥或玉米秸秆处理每投入钾1 kg/hm2,土壤速效钾含量分别增加0.025和0.014 mg/kg。从提升土壤钾素供应能力的角度而言,化肥配合施用有机肥或秸秆还田是值得推广的培肥措施。     

外源氮添加对不同种植年限设施菜田土壤固定态铵含量的影响

研究外源氮(N)添加对不同种植年限设施菜田土壤固定态铵含量及最大固铵量的影响。选取4个不同种植年限（0年、2年、13年和21年）的设施菜田土壤,分别设置4个外源氮添加处理,进行为期36天的室内培养,测定不同种植年限和外源氮添加处理下的土壤固定态铵含量,并计算其最大固铵量。4个外源氮添加处理分别是:（1）CK,不添加任何氮肥,为对照;（2）CF,常规施氮,添加尿素态N 374 mg kg?1干土;（3）RCF,减量施氮（减N 46%,添加尿素态N 200 mg kg?1干土）;（4）RCF + OM,减量施氮配施有机氮（添加尿素态N 150 mg kg?1干土并以鸡粪形式添加有机态氮50 mg kg?1干土）。结果显示:随设施蔬菜种植年限的增加,土壤本底固定态铵含量呈逐渐增加的趋势,而最大固铵量却呈下降的趋势。同一种植年限下,各施肥处理在培养过程中的土壤固定态铵含量总体表现为CK < RCF + OM < RCF < CF,说明施肥可增加土壤固定态铵含量,但其增幅大小受施肥量的多少和施肥种类影响,其中CF处理土壤固铵量为最大（98.61 mg kg?1）,显著高于RCF和RCF + OM处理,而RCF处理的土壤固铵量（84.76 mg kg?1）又高于RCF + OM处理（77.34 mg kg?1）。设施菜田增施氮肥可提高土壤固定态铵的含量,且化肥较有机肥的效果更优。     

小麦苗期施入氮肥在土壤不同氮库的分配和去向

应用盆栽试验和15N标记技术研究了小麦苗期施入N肥后土壤不同N库的动态。结果表明 ,施肥后 28d ,作物所吸收的土壤N占总吸N量的 58.1% ,吸收的肥料N占 41.9%。作物对肥料N的利用率达到 55.3% ,N肥在土壤中的残留率为 24.3% ,损失率为 20.4%。施肥后短期以NH4+-4 N存在的肥料N占施N量的 50.5% ,随着硝化作用的进行和作物的吸收 ,土壤中的NH4+-N显著下降。NO3--N在第 7d达到高峰 ,表现为先升高后降低的趋势 ,说明施肥后在 7d以前有强烈的硝化作用发生。施肥后 2d ,以固定态铵存在的肥料N占 33.7% ,至 28d ,仅占施入N量的 2.4% ,说明前期固定的铵在作物生长后期又重新释放出来供作物吸收。在施肥后第 7d ,肥料N以微生物N存在的量占施肥量的 15.2% ;至 28d来自肥料N的微生物N也几乎被耗竭 ,仅占施N量的 2.4%。随作物生长 ,肥料N在各个土壤N库中的数量均显著下降。在其它N库几乎被耗竭的情况下 ,至施肥后 28d主要以有机N的形式残留。在不种作物的条件下 ,土壤N素的矿化量很低 ,作物的吸收作用导致土壤有机N库不断矿化 ,施入N肥后 ,土壤N素的矿化量增加 ,表现为明显的正激发效应     

Effect of biochar and nitrogen fertilizers on maize seedling growth and enzyme activity relating to nitrification

Maximizing nitrogen use efficiency (NUE) involves synchronizing the interplay between nitrogen preferential crops and the nitrogen transformation pathways of soil. Biochar may benefit specific N-preference crops in relatively unsuitable soil environments; however, experimental data are lacking. This study tested eight treatments, consisting of four nitrogen treatments (N0 = control; N1 = NH₄Cl; N2 = NaNO₃; and N3 = 1:1 ratio of NH₄⁺ and NO₃⁻) each with biochar applied at 0% or 2% (w/w). The results show that biochar and/or nitrogen application enhanced maize seedling biomass and NO₃⁻-based fertilizer resulted in higher seedling biomass than NH₄⁺-based fertilizer. With the application of biochar and NH₄⁺-based fertilizer, maize seedling biomass increased and soil NH₄⁺-N content was significantly reduced compared with NH₄Cl sole application. Correlation analysis and redundancy analysis revealed that SOC content and inorganic nitrogen content were the main factors influencing maize growth and N absorption. Biochar with or without nitrogen fertilizer (except N1 treatment) significantly increased β-1,4-glucosidase (BG) activity. Co-application treatments also resulted in higher vector length, an indicator of C limitation—the increment might add to the risk of microbial C limitation. The activity of ammonia monooxygenase (AMO), a key enzyme in nitrification, decreased with the co-application of biochar and nitrogen, suggesting the alteration of nitrogen transformation.     

化肥有机肥配合施用下双季稻田氮素形态变化

为揭示有机无机肥配合施用下稻田氮素的动态及迁移特征,在湘南双季水稻农作区第四纪红土发育的红黄泥稻田上进行了连续6年田间试验。通过比较不施氮肥（PK）、施用有机肥猪粪（M）、化肥（NPK）及有机肥化肥配合（NPKM）,研究稻田表层全氮、无机氮动态变化,不同层次（25—30、55—60、85—90 cm）土壤溶液无机氮动态,耕层土壤无机氮动态等。结果表明,NH4+-N是红壤双季稻田无机氮素存在的主要形态,施用化学肥料处理（NPK）施肥后1～3 d表面水NH4+-N浓度占全氮比例可达0.5～0.9,有机肥处理（M）为0.3左右。不同层次土壤溶液及其土壤氮素浓度呈现一致的特征,即施肥后短期内出现浓度峰值随后迅速下降,且随着往下推移,氮素峰值出现时间延长,表层水全氮及无机氮在施肥后1～2 d出现浓度高峰,耕层土壤及25—30 cm土壤溶液无机氮浓度高峰约在施肥后3～5 d。化肥有机肥配施有利于水稻稳产高产,年产量达12.2 t/hm2,比不施氮肥的对照产量（7.3 t/hm2）增加68%;土壤有机质6年提升18.5%,显著高于化肥。施用有机肥（M）及有机无机肥配合（NPKM）显著降低了稻田表层水全氮及不同层次土壤溶液和耕层土壤NH4+-N峰值浓度,提高水稻产量和培肥土壤,有利于减少当前氮肥过量施用带来的环境负荷。     

有机肥和化肥长期配合施用对土壤及不同粒级供氮特性的影响

通过间隙淋洗培养试验 ,研究水旱轮作下有机肥与化肥长期配合施用后土壤及不同粒级中氮的矿化特性。结果表明 ,经 14年 2 9茬连续施肥后土壤氮素矿化势明显增加 ,不同处理间的顺序为 :猪粪 化肥 (3 10mgkg- 1) >秸秆 化肥 (2 98mgkg- 1) >化肥 (2 76mgkg- 1) >对照 (2 0 4mgkg- 1)。长期施肥对土壤氮素矿化速率常数影响较小 ,反映了在相同土壤条件下有机氮矿化的共性。经 16周连续培养各处理土壤氮素的矿化率均在 17%左右。土壤不同粒级中氮的矿化量和矿化势均为 0～ 2 μm >2～ 10 μm >50～ 10 0 μm >10～ 50 μm ,有机肥与化肥长期配合施用显著增加了 0～ 2和 2～ 10 μm粒级氮的矿化势和矿化量。与盆栽试验结果相比 ,培养过程矿化释放的氮明显高于同期土壤的供氮量 ,表明在使用矿化氮评价土壤供氮能力时必须加以矫正。     

长期施肥对土壤氮矿化的影响

Two field experiments were conducted in Jiashan and Yuhang towns of Zhejiang Province, China, to study the feasibility of predicting N status of rice using canopy spectral reflectance. The canopy spectral reflectance of rice grown with different levels of N inputs was determined at several important growth stages. Statistical analyses showed that as a result of the different levels of N supply, there were significant differences in the N concentrations of canopy leaves at different growth stages. Since spectral reflectance measurements showed that the N status of rice was related to reflectance in the visible and NIR （near-infrared） ranges, observations for rice in 1 nm bandwidths were then converted to bandwidths in the visible and NIR spectral regions with IKONOS （space imaging） bandwidths and vegetation indices being used to predict the N status of rice. The results indicated that canopy reflectance measurements converted to ratio vegetation index （RVI） and normalized difference vegetation index （NDVI） for simulated IKONOS bands provided a better prediction of rice N status than the reflectance measurements in the simulated IKONOS bands themselves. The precision of the developed regression models using RVI and NDVI proved to be very high with R2 ranging from 0.82 to 0.94, and when validated with experimental data from a different site, the results were satisfactory with R2 ranging from 0.55 to 0.70. Thus, the results showed that theoretically it should be possible to monitor N status using remotely sensed data.     

不同培肥措施对采煤塌陷区复垦土壤氮素矿化的影响

为揭示不同培肥措施对采煤塌陷区复垦土壤氮素矿化特征,采用间歇淋洗好气培养法,研究了不施肥(CK)、单施化肥(CF)、单施有机肥(M)、化肥配施有机肥(MCF)和化肥配施生物有机肥(MCFB)5种培肥措施对复垦4年和8年土壤矿质态氮和可溶性有机氮变化及氮素矿化特征的影响。结果表明:间歇淋洗好气培养过程中,复垦8年土壤累积NO_3~-—N产生量较4年增加2.63%~26.83%,NH_4~+—N累积产生量增加12.50%~32.14%,可溶性有机氮(SON)累积产生量在CF和M处理下减少31.59%~62.50%,其他处理增加3.44%~34.69%。同一复垦年限下NO_3~-—N、NH_4~+—N和SON累积产生量均以MCFB最高。从矿化参数来看,5种培肥措施土壤矿化势(N_0)均表现为复垦8年高于复垦4年土壤,增加幅度为MCFB(26.9%)CK(15.9%)CF(15.0%)M(12.7%)MCF(4.8%);CK和CF处理下潜在可矿化有机氮(N_0/N)随复垦年限增加而减少,减少率分别为9.4%和13.8%,其余3种培肥措施N_0/N呈增加趋势,增加率表现为MCF(13.2%)MCFB(7.5%)M(2.8%);MCF处理下矿化率(N_t/N)随复垦年限增加而增加,增加率为13.2%,其余4种培肥措施的矿化率(N_t/N)均表现为复垦8年低于复垦4年土壤,减少幅度为CF(12.1%)CK(9.4%)MCFB(7.5%)M(2.7%)。不同处理间N_0、N_0/N和N_t/N值则均以8年复垦土壤的MCFB处理最高。综合来看,经过连续8年复垦,化肥配施生物有机肥较其他培肥措施更大程度上提高了各项矿化参数值,但随着复垦年限的增加,以化肥配施有机肥处理的N_0、N_0/N的增加幅度最大,以化肥配施生物有机肥处理的N_t/N减少率最低,长期单施化肥有降低潜在可矿化有机氮量(N_0/N)的趋势。     

SOME EFFECTS OF PARTIAL STERILIZATION ON MINERAL NITROGEN IN A LIGHT SOIL

Field plots on loamy sand with and without the soil fumigant ‘D-D’ (dichloropropane-dichloropropene mixture) were sampled at 0–12, 12–24, and 24–64 cm depths during May 1966–8. All plots received 125 kg/ha nitrogen fertilizer early in March each year and were cropped with sugar beet. Fumigation increased the total amount of mineral (NH₄⁺+ NO₃^?) nitrogen to a depth of 64 cm by 67 kg/ha on average, largely by increasing NH₄⁺-nitrogen. In unfumigated plots some mineral nitrogen leached below 12 cm every year but there was at least 125 kg/ha in the surface 64 cm in 1966 and 1968; during the wet spring of 1967 much leached below 64 cm. Sequential sampling in 1968 confirmed that some of the fertilizer nitrogen moved down the profile during spring. Plots partially sterilized either one or two years previously and not again, contained the same quantity of mineral nitrogen as plots that had never been fumigated. Fumigation increased the mineral nitrogen in plots by a similar amount whether or not they had been fumigated previously. Thus, on this soil, partial sterilization with ‘D-D’ seemed to have little residual effect on mineral nitrogen.     

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.     

盆栽和田间条件下土壤15N标记肥料氮的转化

利用¹⁵N在盆栽条件下研究了铵的矿物固定作用对肥料氮在三种土壤中转化的影响.结果表明,红壤性水稻土不固定肥料铵,但在白土和夹沙土中,56-77%的肥料氮被土壤矿物所固定,这些“新固定”的固定态铵的有效性很高,其中90%以上在30-50天内即被水稻所吸收,或者为微生物所利用转变为生物固定态氮.生物固定态氮对当季作物的有效性远较“新固定”的固定态铵的低.田间微区试验的结果还表明,甚至第二、三季作物吸收的残留肥料氮中,20-86%的氮也系来自固定态铵.作者认为,对具有较强固铵能力的土壤来说,只有了解铵的矿物固定作用,才能正确了解肥料氮的其它转化过程.     

Presubmergence and green manure affect the transformations of nitrogen‐15‐labeled urea under lowland soil conditions

The effect of presubmergence and green manuring on various processes involved in [¹⁵N]‐urea transformations were studied in a growth chamber after [¹⁵N]‐urea application to floodwater. Presubmergence for 14 days increased urea hydrolysis rates and floodwater pH, resulting in higher NH₃ volatilization as compared to without presubmergence. Presubmergence also increased nitrification and subsequent denitrification but lower N assimilation by floodwater algae caused higher gaseous losses. Addition of green manure maintained higher NH₄⁺‐N concentration in floodwater mainly because of lower nitrification rates but resulted in highest NH₃ volatilization losses. Although green manure did not affect the KCl extractable NH₄⁺‐N from applied fertilizer, it maintained higher NH₄⁺‐N content due to its decomposition and increased mineralization of organic N. After 32 days about 36.9 % (T₁), 23.9 % (T₂), and 36.4 % (T₃) of the applied urea N was incorporated in the pool of soil organic N in treatments. It was evident that the presubmergence has effected the recovery of applied urea N.