猪粪堆肥臭气产生与调控的研究

通过两次室外中型堆肥试验，研究在相同水分条件(68.8%)，不同调理剂、不同碳氮比(C/N)、不同通气方式以及不同添加剂对猪粪堆肥过程中臭气产生与控制的影响。研究表明：猪粪堆肥中，臭气的主要形式是氨气，主要产生在堆肥的升温及高温期。降低堆肥的pH值、增加微生物对NH⁺₄-N的固定等是控制臭气的有效措施；过磷酸钙添加量为1.5%时，可以降低堆肥的pH值，使NH₃浓度减小，促进NH⁺₄-N向其它形式的氮转变，且不影响堆肥的腐熟；除臭剂试验组堆肥过程中臭味小，堆肥结束后的物理性状最好，不影响猪粪堆肥进程，可在生产中推广。     

添加玉米秸秆对胡萝卜尾菜堆肥过程的影响

为解决规模化胡萝卜种植过程尾菜处理难的问题，在通风速率为0.05 m³/min的条件下，探讨不同添加比例的玉米秸秆对胡萝卜尾菜堆肥过程中腐熟度、气体排放和酶活性的影响。通过分析腐熟度、气体排放和酶活性之间的响应关系，确定最优辅料添加比例，以期实现胡萝卜尾菜无害化、资源化利用。结果表明：不同胡萝卜尾菜好氧堆肥产品均能满足种子发芽率指数≥70%的无害化标准；NH₃和CO₂排放集中在前7 d，排放速率主要受温度、pH值等理化性质影响，同时鸡粪的添加导致NH₃ 累积排放量增加，不添加任何辅料的胡萝卜尾菜单独堆肥处理（CK）其CO₂ 排放速率最高； 胡萝卜尾菜单独堆肥处理（CK）及7.5%秸秆添加处理（T1）在堆肥期间含水率较高，易产生渗滤液；通过相关性热图、冗余分析对5个处理的气体排放、腐熟度、酶活性进行显著性、相关性分析，进一步证实NH₃、CO₂的排放与温度呈正相关，与pH值呈负相关关系；同时过氧化氢酶与腐熟度指标有显著正相关关系，纤维素酶活性影响堆肥产品的腐熟度。因此，胡萝卜尾菜好氧堆肥过程中，添加15%玉米秸秆辅料（T2）可以提高C/N比、孔隙度，降低渗滤液产出，同时CO₂ 排放量较胡萝卜尾菜单独堆肥（CK）降低6.63%。该研究可为胡萝卜尾菜无害化和资源化利用提供技术支持。     

脲酶抑制剂NBPT对鸡粪好氧堆肥的保氮效果

利用堆肥反应器, 以鸡粪和蘑菇渣为原料进行好氧堆肥, 在堆肥中添加不同浓度的脲酶抑制剂NBPT, 研究其对堆肥氮素转化的影响及保氮效果。结果表明: 添加不同浓度的脲酶抑制剂NBPT对堆肥进程中温度无显著影响, 在堆肥的高温阶段可有效控制堆料pH的升高, 在堆肥高温前期的0~10 d可有效降低堆肥的脲酶活性, 在堆肥中后期10~25 d明显提高全氮含量。堆肥25 d后, 添加0.04 mL·kg^-1、0.08 mL·kg^-1、0.16 mL·kg^-1脲酶抑制剂NBPT分别比CK减少氮素损失6.61%、4.89%和13.51%。堆肥过程中, 堆料铵态氮含量呈升-降-升-降的双峰趋势, 且大部分时间CK处理的铵态氮含量高于添加脲酶抑制剂NBPT处理, 且CK处理铵态氮的两次升高速度均高于添加脲酶抑制剂NBPT处理。在堆肥的升温和高温期硝态氮含量不稳定, 但堆肥结束时, 各添加脲酶抑制剂NBPT处理的硝态氮含量显著高于CK处理。本试验结果表明, 在堆肥过程中添加脲酶抑制剂NBPT可延缓鸡粪中的尿素态氮向铵态氮的转化, 增加堆肥成品中的硝态氮含量。在畜禽粪好氧堆肥中加入脲酶抑制NBPT可起到一定的保氮作用。     

接种菌剂对堆肥微生物数量和酶活性的影响

以牛粪和蘑菇渣为原料进行好氧堆肥,研究接种外源菌剂对堆肥中微生物数量和酶活变化的影响,为微生物菌剂的应用和堆肥工艺的改进提供依据。结果表明,加菌处理微生物数量高于CK处理。堆肥中酶活分析结果表明,各类酶活变化趋势有所不同。其中过氧化氢酶是由低到高的趋势,堆肥中加入外源菌剂对过氧化氢酶活性没有影响,加菌和CK处理最终活性为原始值的2倍以上;脲酶和纤维素酶的变化趋势都是先升高,再降低。加菌和CK处理脲酶活性峰值分别为37．38和30．17mgNH3-N·g^-1·24h^-1;纤维素酶活性峰值分别是51．84和30．62μg·min^-1,外源菌剂对二者酶活性均有明显提高。转化酶也是由高到低的变化趋势,但出现两个波峰。加菌处理转化酶活性峰值分别在第3和第14d出现,峰值为14．20和21．70．mg葡萄糖·g^-1·24h^-1;CK处理出现在第3和第21d,其峰值分别为11．77和20．71mg葡萄糖·g^-1·24h^-1。外源菌剂不仅可提高转化酶活性,还可以使其提前到达峰值。多酚氧化酶与其他酶有较大差别,它是降低-升高-降低的趋势。加菌和CK处理多酚氧化酶活性峰值分别为36．30和47．55mg没食子素·g^-1·3h^-1。以上结果表明,在好氧堆肥中接种外源菌剂可以加快堆肥中有机质分解和转化,促进腐熟。     

淹水稻田氮的损失

A field microplot experiment was conducted during the tillering stage of paddy rice to investigate nitrogen(N) Iosses from flooded rice fields following fertilizer application. After application of ammonium bicarbonate, most of nitrogen in the flood water was present as NH₄-N and its concentration varied widely with time. Concentrations of both NO₃-N and NO₂-N in the floodwater were low due to the weakened nitrification. Under flooded anaerobic reducing conditions, soil solution concentrations of NO₃-N and NH₄-N were nothigh, ranging from 0.6 mg L^-1 to 4.8 mg L^-1, and decreased with soil depth. However, the ground water wasstill contaminated with NO₃-N and NH₄-N. Rainfall simulation tests showed that the N losses via runoff inrice fields were closely related to the time intervals between fertilizer applications and rainfall events. Whena large rain fell for a short period after fertilizer application, the N losses via runoff could be large, which could have a considerable effect on surface water quality. Both irrigation and N fertilizer application must be controlled and managed with great care to minimize N losses via runoff from agricultural land.     

不同来源有机物料对菜用蚕豆生长和品质及根际土壤性状的影响

通过盆栽试验，分析了不同来源有机物料(鸡粪、牛粪、菇渣)对菜用蚕豆生长和品质、根际土化学和生物学性状的影响。结果表明：①3种有机物料对蚕豆分枝数、荚干重、籽粒干重、大粒重、大粒蚕豆占比、籽粒淀粉含量均有积极作用，其中牛粪和菇渣能显著(P<0.05)提高大粒蚕豆占比，鸡粪能显著(P<0.05)提高二粒荚和三粒荚的占比，并且对籽粒淀粉含量的提升效果最为明显(比对照增加69.1%)；②3种有机物料增加了根际土中细菌、真菌数量，显著(P<0.05)提高了根际土中性转化酶、脲酶、酸性磷酸酶、多酚氧化酶活性(除牛粪使中性转化酶活性提高不显著外)，其中鸡粪对细菌数量、中性转化酶活性、脲酶活性的提高程度均最大；③鸡粪能显著(P<0.05)增加根际土有机碳、全氮、NH₄⁺-N含量，牛粪、鸡粪能显著(P<0.05)提高土壤pH。大粒蚕豆占比与土壤酸性磷酸酶活性、有效磷含量呈显著正相关。蚕豆淀粉含量与细菌数量、中性转化酶活性、有机碳、全氮、NH₄⁺-N含量呈显著正相关，这说明有机物料的施用可能为细菌生长提供了更多的碳源和能源，导致细菌数量增加。细菌是酶的重要产生者，细菌数量的增加可能提高了碳氮循环相关酶(中性转化酶、脲酶)的产生量和活性，从而使更多的有机氮转变为无机氮(NH₄⁺-N)，提高了土壤养分(NH₄⁺-N、全氮)水平，进而提高了蚕豆营养品质。     

厨余垃圾沼渣堆肥与化学改良剂对城市搬迁地土壤团聚体形成的影响

为改善城市土壤团粒结构，以上海典型搬迁地土壤为研究对象，通过室外培养试验，研究了不同用量厨余垃圾沼渣堆肥和化学改良剂分别单施以及混施对土壤水稳定性团聚体、团粒结构形成的影响。结果表明：20%、30%沼渣堆肥单施处理可显著增加搬迁地土壤0.5~1.0、1.0~2.0 mm粒径大团聚体以及0.106~0.25 mm粒径微团聚体质量分数（P<0.05），而显著降低<0.106 mm粒径微团聚体质量分数（P<0.05）。化学改良剂β-环糊精单施处理可显著增加土壤微团聚体总量（P<0.05）；3 kg/m³用量硫酸钙、氧化铁单施处理均可显著促进土壤大团聚体的形成（P<0.05）。沼渣堆肥和化学改良剂混施处理较单施处理显著增加土壤>2.0、0.25~0.5 mm粒径大团聚体质量分数（P<0.05），而降低<0.106 mm粒径微团聚体质量分数（P<0.05）。在沼渣堆肥处理中，以20%沼渣堆肥添加量对土壤团粒结构改良效果最佳；在化学改良剂处理中，以3 kg/m³硫酸钙处理对土壤团粒结构改良效果最佳，其次是3 kg/m³氧化铁处理。WG₂₀+SM_mix处理（20%沼渣堆肥+化学改良剂混施）对搬迁地土壤团粒结构改良效果最佳，团粒结构达19.03%，较CK（对照组）、SM_mix（化学改良剂混施）、WG₂₀（20%沼渣堆肥）处理分别提高了94.0%、73.5%和26.0%。     

秸秆覆盖对旱作冬小麦农田土壤呼吸、作物产量及经济 环境效益的影响

基于2009-2011年田间试验, 研究了黄土旱塬区不同秸秆覆盖措施下冬小麦农田土壤呼吸和小麦产量变化, 计算了生产每千克籽粒产量下土壤CO₂的释放量, 并以此比较了处理间的经济 环境效益值。试验包括4个处理: 无覆盖对照(CK)、全年9 000 kg·hm^-2秸秆覆盖(M₉₀₀₀)、全年4 500 kg·hm^-2秸秆覆盖(M₄₅₀₀)和夏闲期秸秆覆盖(SF)。结果表明: 冬小麦生育期内土壤CO₂累积释放量在处理间无显著差异, 但第1年生育期为14.92~17.43 t(CO₂)·hm^-2, 显著高于第2年[12.95~13.69 t(CO₂)·hm ^-2](P<0.05), 处理和年份的交互作用不显著。与CK(产量5.03 t·hm^-2)相比, 秸秆覆盖降低了作物产量, 其中M₉₀₀₀ (4.71 t·hm^-2)与CK差异显著。经济 环境效益值计算结果显示, 冬小麦生育期内生产每千克籽粒释放2.96~3.16 kg CO₂, 处理间无显著差异。从各处理平均值看, 小麦产量以及经济 环境效益值均存在显著的年际差异, 降水偏少的第1年度作物产量(4.60~4.98 t·hm^-2)显著低于降水相对丰富的第2年度(4.50~5.47 t·hm^-2), 但经济 环境效益值(3.03~3.69 kg·kg 1、2.45~2.88 kg·kg^-1)结果相反。处理和年份对作物产量和经济 环境效益值具有显著的交互影响, 在缺水年份秸秆覆盖能够提高作物产量, M₉₀₀₀处理具有最优的经济 环境效益; 而在丰水年份, 秸秆覆盖导致产量显著下降, CK具有更好的经济 环境效益。     

厨余堆肥污染气体减排的工艺参数优化

好氧堆肥处理厨余垃圾具有规模灵活、参数易调整、工艺适配性高等优点,但存在发酵周期长且易产生污染气体等问题,严重限制了就近就地处理利用的推广。污染气体产生与堆体内氧气供应与利用直接相关,为提高发酵速率、减少污染气体排放,优化厨余垃圾堆肥的工艺参数,该研究采用三因素三水平正交堆肥试验L₉（3⁴）,探究粒径、含水率和通风速率三大因素对堆体温度、O₂、pH值、EC值、GI值以及污染气体（H₂S、NH₃、N₂O及CH₄）的影响。结果表明,当初始物料粒径为0.5～10 mm时能够显著加快堆肥进程,在第11 天时GI值即可达80%以上,有效地缩短了堆肥周期。通过对污染气体做极差以及方差分析发现,物料粒径对H₂S排放影响显著,含水率和通风速率对H₂S和N₂O排放影响显著。综合堆肥周期以及污染气体减排效果,厨余垃圾堆肥最优的工艺参数组合为：初始物料粒径为0.5～10 mm、初始含水率为60%、通风速率为0.2 L/（min·kg⁻¹）,研究结果可为厨余垃圾利用提供参考。     

生物质炭对土壤N2O消耗的影响及其微生物影响机理

生物质炭在温室气体减排方面具有很大的发展前景,它不仅能实现固碳,对于在大气中停留时间长且增温潜势大的N₂O也能发挥积极作用。本研究采用室内厌氧培养试验,按照生物质炭与土壤质量比（0、1%和5%）加入一定量生物质炭,土壤重量含水率控制在20%。利用Robotized Incubation平台实时检测N₂O和N₂浓度变化,通过测定土壤中反硝化功能基因丰度（nirK、nirS、nosZ）分析生物质炭对N₂O消耗的影响及其微生物方面的影响机理。结果表明：经过20 h厌氧培养后,0生物质炭处理的反硝化功能基因丰度（基因拷贝数·g^-1）分别为6.80×10⁷（nirK）、5.59×10⁸（nirS）和1.22×10⁸（nosZ）。与0生物质炭处理相比,1%生物质炭处理的nirS基因丰度由最初的2.65×10⁸基因拷贝数·g^-1升至7.43×10⁸基因拷贝数·g^-1,nosZ基因丰度则提高了一个数量级,由4.82×10⁷基因拷贝数·g^-1升至1.50×10⁸基因拷贝数·g^-1,然而nirK基因丰度并无明显变化;5%生物质炭处理的反硝化功能基因丰度并未发生显著变化。试验结束时,添加生物质炭处理的N₂/（N₂O+N₂）比值也明显高于0生物质炭处理。相关性分析结果表明,nirS基因丰度和nosZ基因丰度均与N₂O浓度在0.01水平上显著相关。试验末期nirS基因丰度和nosZ基因丰度均随着N₂O浓度的降低而升高。因此在本试验中,添加1%生物质炭可显著提高nirS和nosZ基因型反硝化细菌的丰度,增大N₂/（N₂O+N₂）比值,促进N₂O彻底还原成N₂。生物质炭对于N₂O主要影响机理是增大了可以还原氧化亚氮的细菌活性,促进完全反硝化。     

模拟土柱条件下黑土中肥料氮素的迁移转化特征

为明确肥料氮素在土壤中的迁移转化动态特征,利用模拟土柱方法,研究了3倍常规施肥量条件下不同肥料处理(尿素、硫铵)黑土的矿质氮变化。结果表明:不同氮肥处理的氮素养分迁移转化特征有明显差异。对照处理(不施肥)土柱内各层次间NH4+-N和NO3--N含量差异不明显;施用尿素或硫铵后,表层0~50mm土层的NH4+-N和NO3--N含量比不施肥对照分别升高100.8~3408.1mg·kg-1、113.4~388.0mg·kg-1和126.7~4671.1mg·kg-1、51.4~63.3mg·kg-1,且在培养前14d内变化最大。在整个培养期内,施用硫铵处理各层次NH4+-N平均含量比尿素处理高2.54~1423.7mg·kg-1,NO3--N平均含量低4.38~335.1mg·kg-1;而尿素处理各层次的硝化率是硫铵处理的0.79~9.12倍。表明肥料氮素的迁移与转化集中在0~50mm土层内,尿素处理的氮素转化速率较硫铵处理高。     

添加脲酶抑制剂NBPT对麦秆还田稻田氨挥发的影响

氨挥发是稻田氮素损失的重要途径,为探明脲酶抑制剂NBPT对小麦秸秆还田稻田中氨挥发的影响,采用密闭室通气法,在太湖地区乌珊土上,研究了脲酶抑制剂n-丁基硫代磷酰三胺(NBPT)对小麦秸秆还田稻田中施肥后尿素水解和氨挥发动态变化的影响。结果表明:稻田氨挥发损失主要集中在基肥和分蘖肥时期。添加NBPT可明显延缓尿素水解,推迟田面水NH4+-N峰值出现的时间,并降低NH4+-N峰值,降低了田面水氨挥发速率和挥发量。NBPT的效果在基肥和分蘖肥施用后尤为明显,不加NBPT时施入的尿素在2~3 d内基本水解彻底,NH4+-N和氨挥发速率在第2 d即达到峰值,两次施肥后NH4+-N峰值分别为132.3 mg·L-1和66.3mg·L-1,氨挥发峰值为15.6 kg·hm-2·d-1和10.4 kg·hm-2·d-1;而添加NBPT后,NH4+-N峰值推迟至施肥后第4 d出现,NH4+-N峰值降至70.7 mg·L-1和51.6 mg·L-1,氨挥发峰值降至4.7 kg·hm-2·d-1和2.6 kg·hm-2·d-1。添加NBPT使稻田氨挥发损失总量从73.3 kg(N)·hm-2(占施氮量的24.4%)降低至34.5 kg(N)·hm-2(占施氮量的11.5%),降低53%。在添加小麦秸秆稻田中添加NBPT通过延缓尿素水解而显著降低了氨挥发损失。     

Nitrogenase (C2H2) Activity in Roots of Non-Cultivated and Cereal Plants: Influence of Nitrogen Fertilizer on Populations and Activity of Nitrogen-Fixing Bacteria

Root samples of 11 non-cultivated monocotyledonous and 7 dicotyledonous species taken during a wet summer had low mean nitrogenase activities of 10.2 and 7.1 nmol C₂H₄·g^?1 DW·h^?1 after preincubation at pO₂ 0.02, respectively. Maxima of 139–169 nmol·g^?1·h^?1 were observed with Agrostis vulgaris and Agropyron repens on a sandy soil poor in C_org. Three of 6 early, but none of 4 late fodder maize cultivars had a very low activity up to 0.5 nmol·g^?1h^?1. Oat, rye and wheat roots from plots with organic or mineral N fertilizers had activities between 1.3 and 7.3 nmol·g^?1h^?1 at flowering, which were not correlated with their Azospirillum populations (10²-10⁷·g^?1 after preincubation). Winter wheat and barley roots given 0, 40, 80 and 120 kg. ha^?1 NH₄NO₃-N in 0–3 applications had mean activities of 0.08, 4.06, 0.09 and 0.08 nmol or 1.77, 2.67, 0.36 and 0.23 nmol C₂H₄g^?1·h^?1 after flowering, respectively. An appreciable part of this activity could be removed by root washing. In preincubated rhizosphere soil of wheat and barley populations of N₂-fixing, facultative anaerobic Klebsiella and Enterobacter spp. were 10–100 times higher than those of Azospirillum sp., both being higher in O N than in 80 kg N·ha^?1 trials.     

Anaerobic ammonium oxidation and denitrification in a paddy soil as affected by temperature,pH, organic carbon,and substrates

Anaerobic ammonium oxidation (anammox process) widely occurs in paddy soil and may substantially contribute to permanent N removal; however, little is known about the factors controlling this process. Here, effects of temperature, pH, organic C, and substrates on potential rate of anammox and the relative contribution of anammox to total N₂ production in a paddy soil were investigated via slurry incubation combined with ¹⁵N tracer technique. Anammox occurred over a temperature range from 5 to 35 °C with an optimum rate at 25 °C (1.7 nmol N g^?1 h^?1) and a pH range from 4.8 to 10.1 with an optimum rate at pH 7.3 (1.7 nmol N g^?1 h^?1). The presence of glucose and acetate (5–100 mg C L^?1) significantly inhibited anammox activities and the ratio of anammox to total N₂ production. The response of potential rates of anammox to ammonium concentrations fitted well with Michaelis-Menten relationship showing a maximum rate (V_max) of 4.4 nmol N g^?1 h^?1 and an affinity constant (K_m) of 6.3 mg NH₄⁺-N L^?1. Whereas, nitrate addition (5–15 mg ¹⁵NO₃^?-N L^?1) significantly inhibited anammox activities and the ratio of anammox to total N₂ production. Our results provide useful information on factors controlling anammox process and its contribution to N loss in the paddy soil.     

Nutrient dynamics,dehydrogenase activity,and response of the rice plant to fertilization sources in an acid lateritic soil

Abstract

Rice variety IR 36, grown under flooding, was studied in 1998 to determine the effects of fly ash, organic, and inorganic fertilizers on changes in pH and organic carbon, release of nutrients (NH₄ ⁺-N, Bray's P, and NH₄OAc K), and dehydrogenase activity in an acid lateritic soil at 15-day intervals. Application of fly ash at 10?t?ha^?1 alone did not improve the availability of NH₄ ⁺-N, or P, as well as the rice grain yield. Availability of NH₄ ⁺-N (35.3–36.9?mg?kg^?1), and P (12.3–14.6?mg?kg^?1) at 15 days after transplanting, and rice grain yields (48.0–51.7?g per pot) were similar under the various fertilization sources such as inorganic fertilizer alone, inorganic fertilizer?+?fly ash or inorganic fertilizer?+?green manure?+?fly ash. Mean dehydrogenase activity was the highest (8.47?µg triphenyl formazon g^?1 24?h^?1) under the mixed fertilization treatments with green manure. At the end of the cropping season (75 days after transplanting), pH, organic carbon, and dehydrogenase activity were higher under the mixed fertilization treatments involving green manure by 3, 15 and 154%, respectively, compared with the inorganic fertilizer alone.     

薄层营养液膜技术(NFT)水培多年生黑麦草对不同富氮废水的净化效果

采用薄层营养液膜技术(NFT)培育多年生黑麦草(Lolium perenne L),以草带为植物滤器净化5种不同配置的富氮废水,废水10 d更换一次.试验结果表明在短期内(2d),TAN、NO-2-N和NO-3-N的去除量均在本身高水平而其他成分低水平的试验组达到最高,4组非离子氨UIA的净化率均高于99%.所有废水的pH值在2 d后均被控制在6.5～8.0.以上述3种氮90%的净化率为目标,废水G3(初始浓度为TAN:40 mg·L-1,NO-2-N:40 mg·L,NO-3-N:10 mg·L-1)和CK(仅在26.77 L自来水中加入18.36 g四水硝酸钙)需2d,废水G4(TAN:40 mg·L-1,NO-2-N:4 mg·L-1,NO-3-N:10 mg·L-1)需4 d,废水G1(TAN:140 mg·L-1,NO-2-N:40 mg·L-1,NO-3-N:80 mg·L-1)、废水G2(TAN:140mg·L-1,NO-2-N:40 mg·L-1,NO-3-N:10 mg·L-1)仅TAN和NO-2-N在6 d内完成.试验结束时G3草净增长最高(169.3 mm),并获得最大干草产量0.205 kg·m-2,G4获得最大鲜草产量1.48 kg·m-2.     

Die Rolle der mikrobiellen Biomasse und des mineralisch fixierten Ammoniums bei den Stickstoff-Transformationen in niedersächsischen Löß-Ackerböden unter Winter-Weizen. I. Poolgrößenveränderungen

Significance of microbial biomass and non-exchangeable ammonium with respect to the nitrogen transformations in loess soils of Niedersachsen during the growing season of winter wheat. I. Change of pool sizes Nitrogen transformations in loess soils have been examined by laboratory and field experiments. After straw application (· 8 t · ha^?1), N in microbial biomass (N_mic) increased by about 20 mg · kg^?1 soil (· 90 kg N · ha^?1 · 30 cm^?1) after 9 days of incubation (20 °C). Another laboratory experiment yielded an increase of about 400 mg of NH₄+-N · kg^?1 fixed by minerals within 1 h after addition of 1 M NH₄+-acetate. Defixation of the recently fixed NH₄+ after addition of 1 M KCl amounted to only 60 mg · kg^?1 within 50 days. In a field experiment with winter wheat 1991, an increase in N_mic of about 80 kg N · ha^?1 · 30 cm^?1 was observed from March to June. After July, growth of the microbes was limited by decreased soluble carbon concentrations in the rhizosphere. Different levels of mineral N-fertilizer (0, 177 and 213 kg N · ha^?1) did not affect significantly the microbial biomass. The same field experiment yielded a decrease of non-exchangeable ammonium on the “zero”-fertilized plot in spring by 200 kg N · ha^?1 · 30 cm^?1. The pool of fixed ammonium increased significantly after harvest. After conventional mineral N-fertilizer application (213 kg N · ha^?1). NH₄+-defixation was only about 120 kg N · ha^?1 · 30 cm^?1 until July.     

旱作地区长期小麦连作和苜蓿连作土壤剖面的矿质氮研究

对不同施肥条件下23年小麦连作地和苜蓿连作地土壤矿质氮分布和累积进行研究,探讨种植浅根系和深根系植物对硝态氮淋溶的影响。结果表明,不施肥(CK)和单施磷(P)肥,小麦和苜蓿连作地土壤硝态氮主要集中在0—60 cm土层,0—60 cm土层以下硝态氮含量变化稳定并小于2 mg/kg。氮肥、磷肥和有机肥配施(NPM)时,小麦连作地土壤硝态氮累积在20—100 cm和140—320 cm土层,年累积速率可达42.12 kg/(hm2.a);苜蓿连作土壤硝态氮主要集中在0—60 cm土层,仅在200—300 cm土层出现轻微累积,年累积速率仅为1.01 kg/(hm2.a)。在不施肥和单施磷肥下,种植小麦或苜蓿对土壤硝态氮残留量影响不显著,而氮、磷和有机肥配施时,小麦连作地土壤硝态氮残留量迅速增加,并与不施肥、单施磷肥处理有显著差异;苜蓿连作地土壤硝态氮残留量虽有少量增加,但与不施肥、单施磷肥处理无显著差异。不施肥、单施磷肥和氮、磷和有机肥配施,小麦连作、苜蓿连作地土壤剖面铵态氮含量主要在10—20 mg/kg之间波动,在土壤剖面无明显的累积现象,铵态氮残留量受施肥和作物种类的影响不显著。     

A method for determining microbially available N and P in an organic soil

Summary A bioassay of microbially available soil N and P is described. It is based on the addition of glucose together with N or P to soil, followed by monitoring of the respiration rate. The addition of glucose + N resulted in an immediate increase in the soil respiration rate followed by a short period of exponential increase, reflecting the growth of microorganisms on the added substrate. The exponential phase levelled off, when lack of P prevented further growth of the soil microorganisms. The soil respiration rate then remained constant for several hours before decreasing, when glucose became limiting. The addition of glucose + P resulted in a lower plateau of the soil respiration rate, indicating that microbial growth was more limited by N than P in this forest soil (0.28 and 0.79 mg CO₂ g^-1 organic matter h^-1, respectively). Additions of the limiting nutrient resulted in a proportional increase in the constant level of the soil respiration rate. This was used to calculated the increase in the soil respiration rate per mg N (0.71 mg CO₂ h^-1) or mg P (4.6 mg CO₂ h^-1) added to this particular soil. Microbially available N was then calculated in two ways from the regression equation (0.15 or 0.40 mg g^-1 organic matter) and P (0.13 or 0.17 mg g^-1 organic matter). A comparison with 2 M KCl extraction showed that in nutrient-poor forest soils the microbially available N was 6.3 or 18.5 times higher than the KCl extractable N.     

Effect of sodium chloride on CO2 evolution,ammonification, and nitrification in a Sassafras sandy loam

Sodium chloride, at rates up to 100 mg g^?1, was added to a Sassafras sandy loam amended with finely-ground alfalfa to determine the effect of NaCl on CO₂ evolution, ammonification, and nitrification in a 14-week study. A NaCl concentration of 0.25 mg g^?1 significantly reduced CO₂ evolution by 16% in unamended soil and 5% in alfalfa-amended soil. Increasing NaCl progressively reduced CO₂ evolution, with no CO₂ evolved from the soil receiving 100 mg NaCl g^?1. A 0.50 mg NaCl g^?1 rate was required before a significant reduction in decomposition of the alfalfa occurred. The NO^?₂-N + NO^?₃-N content of the soil was significantly reduced from 40 to 37 μg g^?1 at 0 and 0.25 mg NaCl g^?1, respectively in the unamended soil. In the alfalfa amended soil, nitrification was significantly reduced at 5 mg NaCl g^?1. At 10 mg NaCl g^?1, nitrification was completely inhibited, there being only 6 and 2 μg NO^?₂-N + NO^?₃-N g^?1 in the alfalfa amended and unamended soil, respectively. In the alfalfa amended soil NH⁺₄-N accumulated from 6 μg g^?1 at the 0 NaCl rate to a maximum of 54 μg g^?1 with 25 mg NaCl g^?1. These higher NH⁺₄-N values resulted in a 0.5 unit increase in the pHw over that of the 0 NaCl rate in the alfalfa amended soil. At NaCl concentrations above 25 mg g^?1 there was a reduction in NH⁺₄-N. The addition of alfalfa to the soil helped to alleviate the adverse affects of NaCl on CO₂ evolution and nitrification.