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1.
《土壤通报》2019,(5):1210-1217
研究在我国亚热带红壤地区采集林地、竹林、茶园和旱地农田4种利用方式的土壤样品,测定了氮素净矿化和净硝化以及N_2O排放速率,定量了氨氧化细菌(AOB)和氨氧化古菌(AOA),以期阐明土地利用方式对红壤氮素矿化和硝化作用的影响。结果表明,不同利用方式红壤AOA基因拷贝数在6.20×10~6到6.58×10~6copies g~(-1)土;AOB基因拷贝数在4.18×10~6到7.41×10~6copies g~(-1)土,AOA和AOB丰度的最大值均出现在旱地红壤。旱地红壤0~7天和0~14天的氮素净矿化速率分别为3.46和1.62 mg kg~(-1),均显著高于其他利用方式。氮素净矿化速率与土壤pH值呈显著的正相关关系(P0.05),与C/N呈显著的负相关关系(P0.05),说明土壤pH和C/N是影响不同利用方式红壤氮素净矿化速率的主要因子。旱地红壤0~7天和0~14天的净硝化速率分别为5.33和3.06 mg kg~(-1),也均显著高于其他利用方式。净硝化速率与铵态氮(NH_4~+-N)含量(P0.01)、pH(P0.05)和AOB(P0.01)均呈显著的正相关关系,表明土壤p H和可利用NH_4~+-N含量是影响红壤净硝化速率的重要因素,高土壤pH和NH_4~+-N含量有利于AOB的生长和活性,从而明显增加净硝化速率。然而,不同利用方式红壤的N_2O排放速率却没有显著的差异,说明利用方式似乎不影响土壤N_2O排放,这与净硝化速率变化规律相矛盾。可能的原因是,除了硝化作用外,好氧培养条件下还存在其他重要的N_2O产生途径,将来的研究中需要关注不同利用方式红壤N_2O产生途径,以阐明红壤N_2O排放机制。 相似文献
2.
以我国小兴安岭地区凉水国家级自然保护区30年林龄的人工红松林为研究对象,建立对照(0 kg hm~(-2)a~(-1))、低氮(20 kg hm~(-2)a~(-1))、中氮(40 kg hm~(-2)a~(-1))和高氮(80 kg hm~(-2)a~(-1))四种模拟氮沉降水平的样地;采用室内培养试验,研究了短期模拟氮沉降对人工红松林土壤氮净矿化、净硝化速率和氧化亚氮排放的影响。结果表明,与对照处理相比,经过2年的模拟氮沉降处理,土壤的净矿化、净硝化速率都有降低趋势。与对照相比,低氮、中氮、高氮土壤净矿化速率分别降低了16.9%、20.6%和25.2%,土壤净硝化速率分别降低了16.7%、20.9%和25.5%,但是处理间差异没有达到显著水平。净硝化速率与净矿化速率呈显著正相关关系(P0.05),表明净矿化速率降低减少铵态氮供应量可能是氮沉降处理降低净硝化速率重要原因。另外,模拟氮沉降处理导致土壤p H降低也不利于硝化作用。中氮和高氮处理土壤氧化亚氮累积排放量分别比对照高84%和40%,但是差异不显著。高的氮沉降量使硝化过程中氧化亚氮的排放比例增加,可能是中氮和高氮处理下净硝化速率下降而土壤氧化亚氮排放量却增加主要原因。研究结果表明,氮沉降会影响我国小兴安岭地区森林土壤氮矿化和硝化过程,但是由于实验开展观测时间较短,其影响规律还需长期实验验证。 相似文献
3.
祁连山东段青海云杉林区土壤氮矿化与土壤因子的相关性 总被引:4,自引:0,他引:4
以祁连山东段青海云杉(Picea crassifolia)林分布带土壤为研究对象,采用顶盖埋管的野外取样法和室内分析法,对海拔梯度上土壤铵态氮(NH+4-N)、硝态氮(NO-3-N)净矿化速率、氮净矿化量和净矿化速率进行测定分析,旨在探讨土壤净氮矿化量与气温降水和土壤理化性质的相关关系,以期建立环境变量与土壤氮矿化量和矿化速率模型,进而提高祁连山青海云杉林生产力及水源涵养能力。其结果表明:(1)土壤硝态氮、铵态氮净矿化速率、土壤净氮矿化量和矿化速率随海拔的升高差异性均极显著;土壤氮净矿化量和矿化速率随海拔梯度的升高呈"W"形变化,与硝态氮净矿化速率随海拔升高的变化规律一致,与铵态氮净矿化速率变化规律相反;在海拔2 800m处,硝态氮净矿化速率、土壤净氮矿化量和矿化速率均达到最大值,为0.372,160.3,0.44 mg/(kg·d),铵态氮净矿化速率出现最低值0.067 mg/(kg·d);在海拔2 900m处出现最低值,为0.155,94.7,0.26mg/(kg·d),在海拔3 100m处,铵态氮的净矿化速率出现最大值0.13mg/(kg·d);(2)回归分析表明,土壤净氮矿化量与年均气温呈极显著负相关(P0.01),R2=0.717 3;与年降水量呈极显著正相关(P0.01),R2=0.383 5;得出气候变化对土壤净氮矿化量的影响程度为:年均气温年降水量;(3)回归分析表明,土壤氮净矿化量与土壤全氮、有机质、含水量、pH值呈极显著正相关(P0.01),其R2依次为0.910 1,0.906 0,0.842 8,0.797 9;与土壤容重呈极显著负相关(P0.01),其R2为0.222 4;由R2值大小可知土壤养分对土壤净氮矿化量的影响程度为:土壤全氮土壤有机质土壤含水量土壤pH土壤容重。 相似文献
4.
施用猪粪条件下重金属对土壤氮素净转化的影响 总被引:1,自引:0,他引:1
以东北耕作黑土为研究对象,在25℃和70%WHC水分条件下进行为期35天的室内培养试验,研究了施用猪粪条件下重金属Cu、Cd对土壤氮素净转化的影响。结果表明:添加单一重金属显著抑制了土壤的硝化作用和矿化作用。与对照处理相比,添加重金属Cu、Cd处理培养结束后土壤铵态氮含量分别增加了5.83和5.39倍,硝态氮含量分别下降了84.3%和79.5%,且土壤净氮矿化速率和净硝化速率均显著低于对照处理。添加重金属的同时施用猪粪加剧了重金属对硝化作用和矿化作用的抑制,土壤净硝化速率和净氮矿化速率均显著低于单一重金属处理。添加重金属抑制了土壤反硝化作用,但同时添加猪粪在一定程度上降低了重金属离子的活性和毒性,进而减轻重金属离子对反硝化作用的抑制程度。 相似文献
5.
苏打盐碱化稻田土壤氮素矿化和硝化特征及其影响因子 总被引:1,自引:0,他引:1
6.
浅层淹水条件下不同施肥处理对黑土氮素净转化的影响 总被引:1,自引:0,他引:1
以东北旱作黑土为对象,在25℃和浅层淹水条件下开展了为期35 d的室内培养试验,研究不同施肥处理对黑土矿化作用和硝化作用的影响。结果表明,浅层淹水条件下土壤矿化作用和硝化作用仍能进行。与不施肥对照处理相比,施用氮肥抑制了培养初期的有机氮矿化,但对后期氮矿化没有影响。氮肥施用初期对硝化作用没有影响,但2周后显著促进了硝化作用的进行。培养期间单施氮肥处理的平均净矿化速率为N 1.07 mg/(kg·d),与对照处理没有显著差异;平均净硝化速率为N 4.50 mg/(kg·d),是对照处理的2.43倍。浅层淹水条件下氮肥配施有机物料显著促进了土壤无机氮的生物固定,培养初期氮肥配施秸秆处理的无机氮固定量大于氮肥配施猪粪处理,后期则相对稍低,氮肥配施猪粪和配施秸秆处理的平均净氮矿化速率分别为N-5.61和-3.15 mg/(kg·d),两者间差异显著。与单施氮肥处理相比,浅层淹水条件下氮肥配施有机物料显著抑制了土壤硝化作用,培养期间氮肥配施猪粪和氮肥配施秸秆处理的平均净硝化速率分别为N 0.29和0.18 mg/(kg·d),分别比单施氮肥处理下降了93.5%和96.0%。 相似文献
7.
土壤pH值和含水量对土壤硝化抑制剂效果的影响 总被引:4,自引:0,他引:4
硝化抑制剂如2-氯-6-三氯甲基吡nitrapyrin,通常与氮肥配施来抑制硝化作用提高农田中肥料的利用率,但是其抑制效果会受到土壤理化性质的影响。采用新工艺重新合成后的新型nitrapyrin纯度高达98%,由于杂质减少而具有更好的硝化抑制效果。为了研究土壤pH值和含水量对新型nitrapyrin抑制效果的影响,明确nitrapyrin适合施用的土壤条件,采用室内培养试验,研究了在不同的土壤pH值和含水量下nitrapyrin对无机氮含量动态变化和硝化作用强度的影响,以及其硝化抑制率的变化规律。结果表明:随着土壤pH值的升高,铵态氮含量降低,硝态氮含量和表观硝化率呈现上升的趋势,并且在所有pH值处理下氮肥配施nitrapyrin均显著地降低了矿质氮库铵态氮的转化量,均不同程度地抑制了硝化作用;在培养的第9天,nitrapyrin在pH值7.70处理下对硝化作用抑制效果最好,硝化抑制率达到91.53%,但硝化抑制率的降低速率在高pH值处理上更快;在培养的第45天,当pH值为4.66时,硝化抑制率为36.43%,显著高于其他处理;在整个培养过程中,施用nitrapyrin能显著抑制各处理的硝化作用,硝化抑制率在不同土壤含水量上的表现为:40%WHC60%WHC80%WHC。可见,nitrapyrin更加适合施用在酸性土壤以及旱地土壤上,该研究可以为新型硝化抑制剂nitrapyrin在农田中施用的最优条件提供理论依据。 相似文献
8.
两种硝化抑制剂对土壤氮转化的影响 总被引:4,自引:2,他引:4
为比较硝化抑制剂双氰胺、硫代硫酸钾对土壤氮的硝化抑制效果,明确其对土壤氮转化作用效应,采用室内培养试验方法,研究了双氰胺、硫代硫酸钾及其配施对土壤矿质氮动态变化、硝化作用及氮回收率的影响。结果表明,单施氮肥土壤硝化作用活跃,77.7%的化肥氮以铵态氮形式从矿质氮库消失,其中56.6%的氮形成硝态氮。氮肥配施双氰胺、硫代硫酸钾分别显著降低矿质氮库铵态氮消失量74.1%(P0.01)和16.6%(P0.05),同时配施双氰胺和硫代硫酸钾处理铵态氮出现增加现象。氮肥配施双氰胺及同时配施2种抑制剂均不同程度地抑制氮的硝化作用,抑制率分别为35.5%~98.7%和82.2%~103.5%,硝化作用延滞时间均在20 d以上。氮肥配施硫代硫酸钾的硝化抑制率为1.6%~62.6%,硝化作用延滞时间为10 d。双氰胺硝化抑制效应优于硫代硫酸钾,且2种抑制剂同时配施作用效果优于其单独施用。施用硫代硫酸钾可促进土壤NO2--N积累,双氰胺可抑制NO2--N生成。氮肥配施双氰胺及同时配施两种抑制剂处理显著增加土壤矿质氮含量、降低其他去向氮含量同时显著提高土壤矿质氮回收率14.7%(P0.05)和12.0%(P0.05)。总体上,抑制剂双氰胺在铵态氮转化、硝化作用抑制及提高矿质氮回收率等方面作用效果均优于硫代硫酸钾,硫代硫酸钾与双氰胺配施在硝化抑制作用方面具有协同效应。该研究结果可为双氰胺、硫代硫酸钾在农田氮素面源污染控制中的应用提供科学依据,但对2种抑制剂硝化抑制特性的全面了解,尚需在田间试验条件下进行进一步的研究和验证。 相似文献
9.
土壤pH值和含水量对土壤硝化抑制剂效果的影响(英文) 总被引:1,自引:0,他引:1
《农业工程学报》2018,(8)
硝化抑制剂如2-氯-6-三氯甲基吡nitrapyrin,通常与氮肥配施来抑制硝化作用提高农田中肥料的利用率,但是其抑制效果会受到土壤理化性质的影响。采用新工艺重新合成后的新型nitrapyrin纯度高达98%,由于杂质减少而具有更好的硝化抑制效果。为了研究土壤pH值和含水量对新型nitrapyrin抑制效果的影响,明确nitrapyrin适合施用的土壤条件,采用室内培养试验,研究了在不同的土壤pH值和含水量下nitrapyrin对无机氮含量动态变化和硝化作用强度的影响,以及其硝化抑制率的变化规律。结果表明:随着土壤pH值的升高,铵态氮含量降低,硝态氮含量和表观硝化率呈现上升的趋势,并且在所有pH值处理下氮肥配施nitrapyrin均显著地降低了矿质氮库铵态氮的转化量,均不同程度地抑制了硝化作用;在培养的第9天,nitrapyrin在pH值7.70处理下对硝化作用抑制效果最好,硝化抑制率达到91.53%,但硝化抑制率的降低速率在高pH值处理上更快;在培养的第45天,当pH值为4.66时,硝化抑制率为36.43%,显著高于其他处理;在整个培养过程中,施用nitrapyrin能显著抑制各处理的硝化作用,硝化抑制率在不同土壤含水量上的表现为:40%WHC60%WHC80%WHC。可见,nitrapyrin更加适合施用在酸性土壤以及旱地土壤上,该研究可以为新型硝化抑制剂nitrapyrin在农田中施用的最优条件提供理论依据。 相似文献
10.
开垦年限对黑土氮初级转化速率和净转化速率的影响 总被引:2,自引:0,他引:2
以东北黑土区开垦2 a和开垦30 a的典型旱作土壤为研究对象,采用15N同位素成对标记技术开展室内培养试验,利用数值计算模型(FLUAZ)计算不同开垦年限土壤的氮初级转化速率,以比较不同开垦年限黑土氮初级转化速率和净转化速率的差异,明确开垦年限对黑土氮转化过程的影响。结果表明,与开垦2a土壤相比,开垦30a土壤的有机碳和水溶性有机碳含量显著降低,导致土壤氮初级矿化速率和初级固定速率也显著降低。但开垦30a土壤的初级硝化速率、净硝化速率和净氮矿化速率却显著高于开垦2a土壤。两个开垦年限土壤的初级硝化速率分别为净硝化速率的1.15倍和1.02倍,说明土壤微生物对硝态氮的固定很少。开垦30a土壤的m/i值(氮初级矿化速率与初级固定速率之比)和n/ia值(初级硝化速率与初级铵态氮固定速率之比)均显著大于1,而开垦2 a土壤的m/i值和n/ia值均接近1。表明开垦2 a土壤的氮矿化与固定过程紧密偶联,氮素损失的风险较小,而开垦30 a土壤中氮矿化量超过了固定量,这为硝化作用的进行提供了底物,增加了硝酸盐反硝化和淋溶风险。 相似文献
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13.
西藏高原自然生态系统转化为农田后提高了土壤的净矿化和净硝化 总被引:5,自引:0,他引:5
A comparative study was conducted to determine the NH4^+ and NO3^- concentrations in soil profiles and to examine the net nitrogen (N) mineralization and nitrification in adjacent forest, grassland, and cropland soils on the Tibetan Plateau. Cropland soil showed significantly higher inorganic N concentrations in soil profiles compared with forest and grassland soils. NO3^- -N accounted for 70%-90^ of inorganic N in cropland soil, while NH4^+ -N was the main form of inorganic N in forest and grassland soils. The average net N mineralization rate at 0 20 cm depth was approximately twice in cropland soil (1.48 mg kg^-1 d^-1) as high as in forest (0.83 mg kg^-1 d^-1) or grassland soil (0.72 mg kg^-1 d^-1). Cropland showed strong net nitrification, with the net rate almost equal to the total net N mineralization. Urea addition stimulated soil respiration, particularly in forest soil. Most urea-N, however, remained as NH4^+ in forest and grassland soils, while NO3^- was the main form of inorganic N to increase in cropland soil. Higher rates of net nitrification in cropland soils suggest that land use change on the Tibetan Plateau may lead to high N losses through nitrate leaching. 相似文献
14.
S. J. González-Prieto A. Cabaneiro M. C. Villar T. Carballas M. Carballas 《Biology and Fertility of Soils》1996,22(3):252-260
N mineralization capacity and its main controlling factors were studied in a large variety (n=112) of native (forest, bush) and agricultural (pasture, cultivated) soils from several climatic zones in Spain. The available inorganic N content, net N mineralization, and net N mineralization rate were determined after 6 weeks of aerobic incubation. NH
inf4
sup+
–N largely predominated over NO
inf3
sup-
-N (ratio near 10:1) except in some agricultural soils. Net N mineralization predominated (83% of soils) over net N immobilization, which was more frequent in agricultural soils (25%) than in native soils (9%). In forest soils, both net N mineralization and the net N mineralization rate were significantly higher than in the other soil groups. The net N mineralization rate of pasture and cultivated soils was similar to that of bush soils, but available inorganic N was lower. The net N mineralization rate decreased in the order: soils over acid rocks>soils over sediments>soils over basic rocks or limestone; moreover, the highest net N mineralization and available inorganic N were found in soils over acid rocks. The highest N mineralization was found in soils with low C and N contents, particularly in the native soils, in which N mineralization increased as the C:N ratio increased. N mineralization was higher in soils with a low pH and base saturation than in soils with high pH and base saturation values, which sometimes favoured N immobilization. Soils with an Al gel content of >1% showed lower net N mineralization rates than soils with Al gel contents of <1%, although net N mineralization and available inorganic N did not differ between these groups. The net N mineralization rate in silty soils was significantly lower than in sandy and clayey soils, although soil texture only explained a low proportion of the differences in N mineralization between soils. 相似文献
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Nitrification activities and N mineralization in paddy soils are insensitive to oxygen concentration
Yanju Yang Jinbo Zhang 《Acta Agriculturae Scandinavica, Section B - Plant Soil Science》2016,66(3):272-281
Oxygen concentration is considered to be the most important factor influencing nitrification and mineralization rates in agricultural soils. However, the sensitivities of nitrification and N mineralization in paddy soils to oxygen concentrations are not well known. We examined nitrification activities and N mineralization rates of six paddy soils with pH ranging from 5.23 to 7.83 and incubated at 25°C and 60% water-holding capacity in laboratory after ammonium was added at concentrations of 10, 30 and 50?mg?N?kg?1 of soil and the headspace gases were replaced with stock gases whose oxygen concentrations were 20%, 10% and 2%, respectively. The tested paddy soils had a very wide range of nitrification activities so that the nitrate ratio in inorganic N varied from >?95% after 1 day incubation to?25% after 7 days of incubation. The nitrate ratio correlated with the soil pH. Nitrate content and its ratio, and mineralization rate were not suppressed when the oxygen concentration in the headspace decreased from 20% to 2%. Our results suggested that nitrifiers and microbial communities involved in N mineralization might have adapted to the environment with low oxygen concentration in paddy soils in which oxygen concentration is deficient during the flooding period. However, oxygen concentration would be even lower than 2% in paddy soils under the flooding conditions. Thus, the minimum oxygen concentration at which nitrification activities in paddy soils are suppressed needs to be explored further. 相似文献
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强酸性茶园土壤中添加不同肥料氮后N2O释放量变化 总被引:4,自引:3,他引:1
茶园由于长期偏施氮肥,造成土壤酸化现象严重和 N2O 大量排放。本文对强酸性茶园土壤进行不同氮肥处理试验,结果表明, 通过31 d的好气培养,各施肥处理均显著提高N2O排放, 其中施硝酸钾(KNO3)处理平均每天排放的N2O最高,总排放量为对照(CK)的17倍,其次是硝酸铵(NH4NO3)处理, 尿素[CO(NH2)2]和硫酸铵[(NH4)2SO4]处理虽然能增加N2O 排放,但远远小于硝酸钾处理。对各氮肥处理硝化势的测定表明,尿素、 硫酸铵和硝酸铵处理均明显增加土壤硝化活性,而硝酸钾处理硝化势与对照相比显著降低。强酸性茶园土壤中N2O排放的主要来源是反硝化作用。氧化亚氮还原酶(nosZ)的定量PCR 分析表明,硝酸钾处理的nosZ 基因拷贝数与对照相比显著降低(P0.05)。因此,强酸性土壤中N2O还原酶活性被NO3-抑制是导致高N2O排放的重要原因之一。 相似文献
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采用1 4 C同位素示踪恒温密闭培养法 ,研究了秸秆和化肥配合施用体系中 ,无机氮对1 4 C秸秆碳矿化的影响 ,培养期一年。结果表明 ,在非石灰性土壤中 ,无机氮的施用促进了1 4 C秸秆碳的矿化 ,相对增加了土壤固有碳 ( 1 2 C)的固持 ,两者间的互补显示无机氮对土壤总碳矿化的影响不大 ;淹水土壤中的1 4 C秸秆碳年矿化率比旱地高 ,发现无机氮对1 4 C秸秆碳年矿化率的增加不论在旱地或水田状况是近似的。在石灰性土壤中 ,无机氮对1 4 C秸秆碳、土壤固有碳的矿化均起到抑制作用 ,没有发现无机氮对有机碳矿化的促进。对有机肥和无机肥配合施用体系中 ,化学氮肥对土壤有机碳转化影响 ,以及化学氮肥在土壤有机碳内循环中的作用功能等 ,提出了一些新的见解 相似文献
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《Communications in Soil Science and Plant Analysis》2012,43(12):1369-1381
Abstract The effect of liming on mineralization and soil nitrifier activity (NA) was investigated with Brookston clay (pH 5.7) and Haldimand clay (pH 4.7). Liming increased the rate of mineralization in both soils but at a rate about 4‐times greater in Haldimand clay than Brookston clay. A significant increase in N mineralization due to liming occurred in both soils only when pH was raised above 6.0. The rate of mineralization was greater than nitrification in the Haldimand soil resulting in NH4 + accumulation. Nitrifier activity increased with liming of Brookston clay, but decreased in Haldimand clay after 15 days of incubation. There was a significant increase in nitrifier activity due to liming from 15 to 60 days in Haldimand clay. After 60 days nitrifier activity in limed treatments increased by five times over the unlimed control. The nitrification of urea powder (1000 mg N.kg‐1) mixed into the soil was also studied in several soils incubated at 15°C for 28 days. There was evidence up to 14 days that nitrification of urea was correlated with initial nitrifier activity. Between 14 and 28 days, other factors such as soil pH and possible ammonia toxicity in coarser textured soils as well as nitrifier activity were important. Accumulation of nitrite occurred mainly in soils with a pH above 7.0 up to 28 days especially where nitrifier population enrichment was not done. 相似文献