两种硝化抑制剂对土壤氮转化的影响

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。     

脲酶/硝化抑制剂对尿素氮在白浆土中转化的影响

采用室内恒温培养方法,研究了脲酶抑制剂（NBPT）、硝化抑制剂（DMPP）及其协同对尿素氮在三江平原白浆土中转化作用效果。研究表明,在白浆土中NBPT有效作用时间小于13 d,作用时间较在棕壤和黑土中短;对土壤中铵态氮、硝态氮及表观硝化率影响与普通尿素基本一致。NBPT与DMPP组合缓释尿素施入4-7 d,能够有效抑制脲酶活性,减缓尿素水解;只添加DMPP与添加NBPT与DMPP协同作用对抑制铵态氮硝化作用效果相同,二者能保持土壤中NH4+-N高含量时间超过80 d。DMPP作用时间可达80 d以上,能有效抑制NH4+-N向NO3--N的转化;在第80 d,土壤中仍有54.58%～56.85%的氮以铵态氮形式存在,表观硝化率只有50%左右。DMPP抑制硝化作用效果十分显著,因此,在白浆土中施用添加NBPT缓释尿素、DMPP缓释尿素、NBPT与DMPP缓释尿素时,应首选添加1%DMPP的缓释尿素肥料。     

Effect of urease and nitrification inhibitors on ammonia volatilization and abundance of N‐cycling genes in an agricultural soil

The effect of the combined application of urease and nitrification inhibitors on ammonia volatilization and the abundance of nitrifier and denitrifier communities is largely unknown. Here, in a mesocosm experiment, ammonia volatilization was monitored in an agricultural soil treated with urea and either or both of the urease inhibitor N‐(n‐butyl) thiophosphoric triamide (NBPT) and the nitrification inhibitor 3,4‐dimethylpyrazole phosphate (DMPP), with 50% and 80% water‐filled pore space (WFPS). The effect of the treatments on the abundance of bacteria and archaea was estimated by quantitative PCR (qPCR) amplification of their respective 16S rRNA gene, that of nitrifiers using amoA genes, and that of denitrifiers by qPCR of the norB and nosZI denitrification genes. After application of urea, N losses due to NH₃ volatilization accounted for 23.0% and 9.2% at 50% and 80% WFPS, respectively. NBPT reduced NH₃ volatilization to 2.0% and 2.4%, whereas DMPP increased N losses by up to 36.8% and 26.0% at 50% and 80% WFPS, respectively. The combined application of NBPT and DMPP also increased NH₃ emissions, albeit to a lesser extent than DMPP alone. As compared with unfertilized control soil, both at 50% and 80% WFPS, NBPT strongly affected the abundance of bacteria and archaea, but not that of nitrifiers, and decreased that of denitrifiers at 80% WFPS. Regardless of moisture conditions, treatment with DMPP increased the abundance of denitrifiers. DMPP, both in single and in combined application with NBPT, increased the abundance of nitrification and denitrification genes.     

旱地土壤施用生物炭减少土壤氮损失及提高氮素利用率

该试验采用土柱室内模拟的方法,旱地土壤上分别添加不同比例的生物炭(0、0.5%、2%、4%、6%、8%),通过模拟降雨淋洗,探讨生物炭对旱地土壤氮素动态变化的影响。结果表明:添加生物炭能延缓NO3-和总氮淋洗速度,生物炭添加质量百分数达2%及以上时,可显著降低总氮和NH4+淋洗,其添加质量百分数达4%及以上时,可显著降低NO3-淋洗,而添加少量生物炭对氮的淋洗无影响;NO3-淋洗量占旱地土壤氮素淋洗总量的84%~90%,而NH4+仅占0.4%~2%;各处理下不同土层间土壤全氮含量均无差异,而不同处理间土壤全氮含量差异显著,当生物炭添加质量百分数达2%及以上时,土壤全氮含量随生物炭添加量的增加而增加,且生物炭添加百分数与土壤全氮之间满足极显著的指数关系(R2=0.9944)。因此,在旱地土壤上施用生物炭量至少达2%以上才能显著减少氮素淋洗和增加土壤全氮含量,达到减少土壤氮素损失和提高氮素利用率,减少由氮素带来的环境污染以及改善土壤肥力的综合目标。     

Effect of the nitrification inhibitor nitrapyrin on the fate of nitrogen applied to a soil incubated under laboratory conditions

The aim of this study was to examine the effect of the nitrification inhibitor nitrapyrin on the fate and recovery of fertilizer nitrogen (N) and on N mineralization from soil organic sources. Intact soil cores were collected from a grassland field. Diammonium phosphate (DAP) and urea were applied as N sources. Cores were equilibrated at –5 kPa matric potential and incubated at 20 °C for 42 to 56 days. Changes in NH₄⁺‐N, accumulation of NO₃^–‐N, apparent recovery of applied N, and emission of N₂O (acetylene was used to block N₂O reductase) were examined during the study. A significant increase in NH₄⁺‐N released through mineralization was recorded when nitrapyrin was added to the control soil without N fertilizer application. In the soils to which N was added either as urea or DAP, 50–90 % of the applied N disappeared from the NH₄⁺‐N pool. Some of this N (8–16 %) accumulated as NO₃^–‐N, while a small proportion of N (1 %) escaped as N₂O. Addition of nitrapyrin resulted in a decrease and delay of NH₄⁺‐N disappearance, accumulation of much lower soil NO₃^–‐N contents, a substantial reduction in N₂O emissions, and a 30–40 % increase in the apparent recovery of added N. The study indicates that N recovery can be increased by using the nitrification inhibitor nitrapyrin in grassland soils at moisture condition close to field capacity.     

Nitrous oxide emissions and dynamics of soil nitrogen under 15N‐labeled cow urine and dung patches on a sandy grassland soil

Grazing animals highly influence the nutrient cycle by a direct return of 80% of the consumed N in form of dung and urine. In the autumn‐winter period, N uptake by the sward is low and rates of seepage water in sandy soils are high, hence high mineral‐N contents in soil and in seepage water as well as large losses of N₂O are expected after cattle grazing in autumn. The objective of this study was the quanitfication of N loss deriving from urine and dung leaching and by N₂O emission. Therefore the deposition of urine and dung patches was simulated in maximum rates excreted by cows by application of ¹⁵N‐labeled cow urine and dung (equivalent to 1030 kg N ha^–1 and 1052 kg N ha^–1, respectively) on a sandy pasture soil in N Germany. Leachate was collected in weekly intervals from free‐draining lysimeters, and ¹⁵N‐NO , ¹⁵N‐NH , and ¹⁵N‐DON (dissolved organic N) were monitored over 171 d. Furthermore, the ¹⁵N‐N₂O emission rates and the dynamics of inorganic ¹⁵N in the upper soil layer were monitored in a field trial, adjacent to the lysimeters. After 10 d following the urine application, the urea was completely hydrolyzed, shown by a 100% recovery of urine‐N in the soil NH . The following decrease of ¹⁵N‐NH in the soil was higher than the increase of ¹⁵N‐NO , and some N loss was explained by leaching. Amounts of 51% and 2.5% of the applied ¹⁵N were found in leachate as inorganic N, 2.4% and 0.7% as DON derived from urine and dung, respectively. Release of N₂O from urine and dung patches applied to the pasture was low, with losses of 0.05% and 0.33% of the applied ¹⁵N, respectively. Overall loss of dung‐derived N was very low, but as the bulk dung N remained in the soil, N loss after mineralization of the dung needs to be investigated.     

不同氮肥在石灰性潮土中的转化及ATS对尿素氮转化的调控效应

根据氮肥施入土壤后的转化特性进行氮肥的高效调控和管理是提高氮肥利用效率、缓解氮肥污染的重要措施。为探究不同氮肥在石灰性潮土中的转化特性差异及硫代硫酸铵（ammonium thiosulfate,ATS）作为氮肥调控剂对尿素氮转化的影响,该研究采用室内土壤培养（土壤水分含量为田间持水量的60%,温度25 ℃）试验方法,以尿素、硫酸铵、氯化铵和ATS作为供试肥料,比较4种氮肥施入石灰性潮土后的转化特性差异,并以ATS作为氮素调控剂,以单施尿素作为对照,探究尿素配施不同用量ATS对尿素氮转化的影响。结果表明,4种供试氮肥在石灰性潮土中的转化过程明显不同。尿素在石灰性潮土中的水解速率最快,硝化作用强度也最高,硫酸铵其次;氯化铵由于Cl^-的硝化抑制作用,土壤表观硝化率在7～21 d显著低于尿素和硫酸铵（P＜0.05）;ATS施入土壤后,NH₄⁺-N转化为NO₂^--N的速率最高,而NO₂^--N转化为NO₃^--N的速率最低,NH₄⁺-N在土壤中的存留时间最长,出现峰值之后也一直保持最高的含量,表观硝化率最低。将ATS作为氮素调控剂与尿素配合施用,当其用量在60 mg/kg（含S量）以上时,既表现出了明显的抑制尿素水解的作用效果,也表现出了显著的硝化抑制作用（ P <0.05）,且随着ATS用量的增加,抑制效应明显增强。这对于减少氮素损失,提高氮肥利用效率具有积极意义。但供试4种氮肥施入土壤后均出现了亚硝酸盐的累积,其中ATS处理的累积量显著高于尿素、硫酸铵和氯化铵（P＜0.05）,累积持续时间也最长。ATS作为氮素调控剂调控氮素转化,也出现了类似的结果,且随着ATS用量增加,亚硝酸盐在土壤中存留时间明显延长,含量和峰值明显提高,出现峰值的时间也明显延后。     

无机硒肥对土壤有效氮含量及菠菜品质的影响

【目的】研究不同浓度亚硒酸钠(Na_2SeO_3)对土壤脲酶活性、铵态氮(NH_4^+-N)和硝态氮(NO_3~–-N)含量及菠菜品质的影响,综合分析Na_2SeO_3在土壤-根部-作物之间被吸收、转运、转化的可能路径,为生物强化生产富硒农产品及调控硒的安全水平提供参考。【方法】进行连续42天盆栽试验,共设置4个处理,每千克土施Na_2SeO_3 0 (对照)、1、10、30 mg,分别于定植后的14、28、42天测定菠菜叶可溶性糖、可溶性蛋白、维生素C、硝酸盐含量,并测定土壤铵态氮、硝态氮含量及土壤脲酶活性等指标。【结果】在菠菜生长期间,≤10mg/kg Na_2SeO_3处理可使土壤脲酶活性表现为先被激活后减弱至对照水平,土壤硝态氮含量也表现出相同的变化趋势,但铵态氮变化趋势正好相反;30 mg/kg Na_2SeO_3处理对土壤脲酶活性没有明显的影响,在整个培养时期与对照水平相当,土壤NH_4^+-N含量后期明显减少,转化成的NO_3~–-N含量明显增加,有利于菠菜吸收利用。同等Na_2SeO_3添加量条件下,Na_2SeO_3对三个取样时间菠菜叶的硝酸盐、维生素C (Vc)、可溶性蛋白、可溶性糖含量影响各异。1 mg/kg Na_2SeO_3处理组可使菠菜叶的硝酸盐含量明显增加,Vc含量先增后减,可溶性蛋白含量减少,可溶性糖含量没有变化;10 mg/kg处理组可使菠菜叶中的硝酸盐、可溶性糖含量表现为先增后减,Vc含量、可溶性蛋白含量均有不同程度增加;30 mg/kg处理组可使菠菜叶的硝酸盐含量先增后减,可溶性蛋白、可溶性糖含量减少,Vc含量没有变化。【结论】不同浓度亚硒酸钠对土壤有效氮及菠菜品质有不同程度的影响。富硒作物生产中无机硒肥施用量要综合考虑硒在作物体内的转化率及硒对作物品质影响的各项因素而确定。     

Suppression of methane oxidation in aerobic soil by nitrogen fertilizers,nitrification inhibitors,and urease inhibitors

Concentrations of CH₄, a potent greenhouse gas, have been increasing in the atmosphere at the rate of 1% per year. The objective of these laboratory studies was to measure the effect of different forms of inorganic N and various N-transformation inhibitors on CH₄ oxidation in soil. NH ₄ ⁺ oxidation was also measured in the presence of the inhibitors to determine whether they had differential activity with respect to CH₄ and NH ₄ ⁺ oxidation. The addition of NH₄Cl at 25 g N g^-1 soil strongly inhibited (78–89%) CH₄ oxidation in the surface layer (0–15 cm) of a fine sandy loam and a sandy clay loam (native shortgrass prairie soils). The nitrification inhibitor nitrapyrin (5 g g^-1 soil) inhibited CH₄ oxidation as effectively as did NH₄Cl in the fine sandy loam (82–89%), but less effectively in the sandy clay loam (52–66%). Acetylene (5 mol mol^-1 in soil headspace) had a strong (76–100%) inhibitory effect on CH₄ consumption in both soils. The phosphoroamide (urease inhibitor) N-(n-butyl) thiophosphoric triamide (NBPT) showed strong inhibition of CH₄ consumption at 25 g g^-1 soil in the fine sandy loam (83%) in the sandy clay loam (60%), but NH ₄ ⁺ oxidation inhibition was weak in both soils (13–17%). The discovery that the urease inhibitor NBPT inhibits CH₄ oxidation was unexpected, and the mechanism involved is unknown.     

How does the application of different nitrification inhibitors affect nitrous oxide emissions and nitrate leaching from cow urine in grazed pastures?

Nitrous oxide (N₂O) is a potent greenhouse gas, and nitrate () is a water contaminant. In grazed grassland, the major source of both leaching and N₂O emissions is nitrogen (N) deposited in animal excreta, particularly in the urine. The objective of this study was to determine the effectiveness of two nitrification inhibitors: (i) a solution of dicyandiamide (DCD) and (ii) a liquid formulation of 3,4‐dimethylpyrazole phosphate (DMPP) for reducing N₂O emissions and leaching from urine patch areas in two grazed pasture soils under different environmental conditions. In the Canterbury Templeton soil, the nitrification rate of ammonium from the animal urine applied at 1000 kg N/ha was significantly decreased by the application of DCD (10 kg/ha) and DMPP (5 kg/ha). N₂O emissions, measured over a 3‐month period, from dairy cow urine applied to the Canterbury Templeton soil were 1.14 kg N₂O‐N/ha, and this was reduced to 0.43 and 0.39 kg N₂O‐N/ha by DCD and the liquid DMPP, respectively. These are equivalent to 62–66% reductions in the total N₂O emissions. Nitrate leaching losses from dairy cow urine applied to the Waikato Horotiu soil lysimeters were reduced from 628.6 kg ‐N/ha to 400.6 and 451.5 kg ‐N/ha by the application of DCD (10 kg/ha) or DMPP (1 kg/ha), respectively. There was no significant difference between the DCD solution and the liquid DMPP in terms of their effectiveness in reducing N₂O emissions or leaching under the experimental conditions of this study. These results suggest that both the liquid formulations of DCD and DMPP have the potential to be used as nitrification inhibitors to reduce N₂O emissions and leaching in grazed pasture soils.     

Nanoclay polymer composites loaded with urea and nitrification inhibitors for controlling nitrification in soil

Nanoclay polymer composites (NCPCs) were synthesized with partially neutralized acrylic acid and bentonites and loaded with urea and nitrification inhibitors (NIs) to act as a slow release carrier of nitrogen (N). The resulting product was characterized by Fourier transform infrared spectroscopy (FTIR), scanning electron microscopy (SEM) and X-ray diffraction (XRD). The XRD of NCPCs revealed that the bentonite layers were completely exfoliated and dispersed in the composite after the polymerization. The water absorbency of pure polymer (Acrylic acid + Acrylamide) was 197.53 g g^?1 and 137.75 g g^?1 by nanocomposite (8% nanobentonite) in distilled water. The nitrification inhibition ability of these NCPCs was evaluated by incubation study for 60 days in laboratory at 28°C and 50% water-holding capacity. The Schiff base -NCPCs were most effective at inhibiting nitrification (30–87%) compared to dicyandiamide and Neem oil. A column study was performed to know the movement of NH₄-N and NO₃-N at three different depths. Result showed that the Schiff base -NCPC decreased nitrate movement by 78.5% at the depth of 5 cm in soil column. The slow release of nitrogen and good water retention capacity confirmed that these NCPCs can be viably exploited for application in agriculture.     

Phosphorus uptake by cowpea plants from sparingly available or soluble sources as affected by nitrogen form and arbuscular‐mycorrhiza‐fungal inoculation

In most plant species, nutrient uptake is facilitated upon root association with symbiotic arbuscular mycorrhizal (AM) fungi. The aim of the present experiment was to test how the form in which nitrogen (N) is supplied to the growth medium affects substrate pH, AM development, and contribution of the symbiosis to phosphorus (P) uptake from sparingly available or soluble resources. Cowpea (Vigna unguiculata L. Walp) plants inoculated or noninoculated with AM fungi (Glomus sp.) were grown in pots with a sand substrate supplied with nutrient solution. The nutrient solution was prepared either with a high or a low concentration of soluble P, and NO ‐N : NH ‐N ratios of 9:1 or 5:5. The substrate supplied with low‐P nutrient solution was either or not additionally amended with ground rock phosphate. Despite a high level of root colonization, AM fungi used in the present study did not appear to increase plant availability of rock phosphate. It cannot be excluded that the ability of AM root systems to acquire P from sparingly available resources differs depending on the plant and fungal genotypes or environmental conditions. The absence from the growth substrate of P‐solubilizing microorganisms able to associate with AM mycelia might also have been a reason for this observation in our study. Increased supply of NH relative to NO improved plant P availability from rock phosphate, but also had a negative effect on the extent of AM‐fungal root colonization, irrespective of the plant P‐nutritional status. Whether increasing levels of NH can also negatively affect the functioning of the AM symbiosis in terms of plant element uptake, pathogen protection or soil‐structure stabilization deserves further investigation.     

硝化/脲酶抑制剂对秋马铃薯植株及土壤氮素利用的影响

通过添加硝化/脲酶抑制剂达到秋马铃薯生产中减氮增效的目的,为制定秋马铃薯的农田氮素管理措施及节肥增效策略提供依据.采用随机区组试验设计,设置30、60、90、120 kg/hm24个施氮水平与硝化/脲酶抑制剂N-丁基硫代磷酰三胺(NBPT)、双氰胺(DCD)、2-氯-6-三氯甲基吡啶(CP)、未添加硝化/脲酶抑制剂(C...     

不同氮磷钾肥对土壤pH和镉有效性的影响

采用土壤培养方法研究了不同氮、磷、钾肥对土壤pH和镉有效性的影响。结果表明,在培养60 d时,所有氮肥处理均降低了土壤pH,增加了Cd的提取量;但高量尿素和氯化铵处理土壤pH降低最多,提取的Cd也最多;硫酸铵提取的Cd较对照增加最小。所有磷肥处理均引起土壤pH小幅降低,但对土壤Cd提取量的影响以普钙稍大。3种钾肥处理均降低了土壤pH,其中氯化钾在0 d时提取的Cd在所有钾肥处理中为最高,其提取能力15 d后逐渐消失,试验结束时所有钾肥处理对Cd提取量均低于对照。本研究进一步表明,在土壤Cd含量处于污染临界值附近或已受Cd污染的土壤上,应避免施用高量的酸性肥料如尿素、氯化铵、普钙,以及其他酸性物料。在常用磷、钾肥中,磷酸二铵和硫酸钾在Cd污染土壤上施用更为适合。     

添加不同外源氮对水稻秸秆腐解和养分释放的影响

探究添加不同外源氮对水稻秸秆腐解规律和养分释放特征的影响,为提高水稻秸秆养分利用提供理论依据.该研究采用室内恒湿网袋培养法,设置4个处理:不添加外源氮(CK);添加尿素(PU);添加尿素硝酸铵(UAN);添加石灰氮(CaCN2).结果表明:水稻秸秆腐解规律表现为0～5 d腐解速率最大,为0.39～0.47 g/d;5～...     

Crop nitrogen recovery and soil nitrogen dynamics in a 10‐year field experiment with biowaste compost

When fertilizing with compost, the fate of the nitrogen applied via compost (mineralization, plant uptake, leaching, soil accumulation) is relevant both from a plant‐production and an environmental point of view. In a 10‐year crop‐rotation field experiment with biowaste‐compost application rates of 9, 16, and 23 t ha^–1 y^–1 (f. m.), the N recovery by crops was 7%, 4%, and 3% of the total N applied via compost. Due to the high inherent fertility of the site, N recovery from mineral fertilizer was also low. In the minerally fertilized treatments, which received 25, 40, and 56 kg N ha^–1 y^–1 on average, N recovery from mineral fertilizer was 15%, 13%, and 11%, respectively. Although total N loads in the compost treatments were much higher than the N loads applied with mineral fertilizer (89–225 kg N_tot ha^–1 y^–1 vs. 25–56 kg N_tot ha^–1 y^–1; both on a 10‐year mean) and the N recovery was lower than in the treatments receiving mineral N fertilizer, soil NO ‐N contents measured three times a year (spring, post‐harvest, autumn) showed no higher increase through compost fertilization than through mineral fertilization at the rates applied in the experiment. Soil contents of N_org and C_org in the plowed layer (0–30 cm depth) increased significantly with compost fertilization, while with mineral fertilization, N_org contents were not significantly higher. Taking into account the decrease in soil N_org contents in the unfertilized control during the 10 years of the experiment, 16 t compost (f. m.) ha^–1 y^–1 just sufficed to keep the N_org content of the soil at the initial level.     

Effects of urease and nitrification inhibitors added to urea on nitrous oxide emissions from a loess soil

Urea fertilizer‐induced N₂O emissions from soils might be reduced by the addition of urease and nitrification inhibitors. Here, we investigated the effect of urea granule (2–3 mm) added with a new urease inhibitor, a nitrification inhibitor, and with a combined urease inhibitor and nitrification inhibitor on N₂O emissions. For comparison, the urea granules supplied with or without inhibitors were also used to prepare corresponding supergranules. The pot experiments without vegetation were conducted with a loess soil at (20 ± 2)°C and 67% water‐filled pore space. Urea was added at a dose of 86 kg N ha^–1 by surface application, by soil mixing of prills (<1 mm) and granules, and by point‐placement of supergranules (10 mm) at 5 cm soil depth. A second experiment was conducted with spring wheat grown for 70 d in a greenhouse. The second experiment included the application of urea prills and granules mixed with soil, the point‐placement of supergranules and the addition of the urease inhibitor, and the combined urease plus nitrification inhibitors at 88 kg N ha^–1. In both experiments, maximum emissions of N₂O appeared within 2 weeks after fertilization. In the pot experiments, N₂O emissions after surface application of urea were less (0.45% to 0.48% of total fertilization) than from the application followed by mixing of the soil (0.54% to 1.14%). The N₂O emissions from the point‐placed‐supergranule treatment amounted to 0.64% of total fertilization. In the pot experiment, the addition of the combined urease plus nitrification inhibitors, nitrification inhibitor, and urease inhibitor reduced N₂O emissions by 79% to 87%, 81% to 83%, and 15% to 46%, respectively, at any size of urea application. Also, the N₂O emissions from the surface application of the urease‐inhibitor treatment exceeded those of the granules mixed with soil and the point‐placed‐supergranule treatments receiving no inhibitors by 32% to 40%. In the wheat growth experiment, the N₂O losses were generally smaller, ranging from 0.16% to 0.27% of the total fertilization, than in the pot experiment, and the application of the urease inhibitor and the combined urease plus nitrification inhibitors decreased N₂O emissions by 23% to 59%. The point‐placed urea supergranule without inhibitors delayed N₂O emissions up to 7 weeks but resulted in slightly higher emissions than application of the urease inhibitor and the urease plus nitrification inhibitors under cropped conditions. Our results imply that the application of urea fertilizer added with the combined urease and nitrification inhibitors can substantially reduce N₂O emissions.     

不同外源氮对石灰性土壤硝化作用的影响及其动力学分析

为了揭示外源氮源对石灰性土壤硝化作用的影响机理,以钙积半干润均腐土（Cal-Ustic Isohumasols）为材料,采用室内培养方法研究了不同添加量和不同氮源对土壤硝化作用的影响,并建立了对应的硝化模型。结果表明,NH4+-N消耗速率和NO3--N增加速率呈S曲线变化,NH4+-N消耗速率高于NO3--N增加速率。氮素添加量与NH4+-N消耗速率和NO3--N增加速率呈正相关,硝化菌外的因子对NH4+-N和NO3--N的吸收与NH4+-N添加量呈正相关;不同氮素添加量对硝化作用影响程度不同,当氮素添加量为N 75 mg /kg,干土时,硝化作用较彻底。SO42-可加快硝化作用速率,同时也可改变其他因子对NH4+-N和NO3--N的利用。     

氮肥形态及配比对菠菜生长和安全品质的影响

【目的】铵态氮肥和硝态氮肥是蔬菜生长过程中经常施用的氮肥种类,氮肥形态及配比对蔬菜生长和安全品质有着重要影响。菠菜是一种叶菜类蔬菜,富含矿质元素、维生素C和维生素E。本文通过施用铵态氮和硝态氮肥,探究氮肥形态及其配比(NH+4-N/NO-3-N)对菠菜生长和安全品质的影响。【方法】采用水培试验,设置5种不同氮素形态配比(NH+4-N/NO-3-N比值分别为100∶0、75∶25、50∶50、25∶75和0∶100)的营养液,定期采集菠菜样品并测定菠菜的生物量、株高、根系长度、硝酸盐和亚硝酸盐、有机酸和氨基酸参数值。【结果】随着NH+4-N/NO-3-N比值从100∶0变化到0∶100,菠菜的生物量、株高、根系长度、硝酸盐和亚硝酸盐累积量以及有机酸含量均呈增加趋势,而氨基酸总量则明显下降;当NH+4-N/NO-3-N比值为0∶100时,菠菜茎叶生物量为6.2g/plant,株高和根系长度分别为16.3 cm和22.5 cm,分别是NH+4-N/NO-3-N比值为100∶0时的6倍、2.2倍和2.0倍,表明菠菜是一种喜硝酸盐氮的蔬菜;当NH+4-N/NO-3-N比值由0∶100变为25∶75时,即在氮肥组合中增加25%的铵态氮肥,此时的硝酸盐和亚硝酸盐含量分别由398.5 mg/kg、1.42 mg/kg降为249.1 mg/kg、0.98mg/kg,降幅为37.5%和8.0%,表明在菠菜生长过程中适当增施铵态氮肥可有效降低硝酸盐和亚硝酸盐在茎叶中的累积;当NH+4-N/NO-3-N比值从100∶0变化到0∶100,对6种有机酸(苹果酸、富马酸、琥珀酸、α-酮戊二酸、柠檬酸和丙酮酸)而言,增加幅度最大的是富马酸,约8.6倍,增加幅度最小的是柠檬酸,约2.5倍,苹果酸则在NH+4-N/NO-3-N=25∶75时达到最大值,为985.3 mg/L;随着NH+4-N比例的减少,菠菜茎叶中的氨基酸总量呈下降趋势,NH+4-N/NO-3-N比值为100∶0、75∶25、50∶50、25∶75和0∶100的氨基酸总量分别为21.80μmol/g、12.92μmol/g、9.20μmol/g、8.30μmol/g和7.50μmol/g,表明菠菜的营养价值降低,这一趋势与上述所研究的指标(株高、根系长度、硝酸盐和亚硝酸盐含量以及有机酸含量)有着明显的区别。【结论】菠菜是一种典型的喜硝态氮类蔬菜,施用硝态氮肥可明显提高菠菜产量,但过高的施用量可导致菠菜安全品质下降。适当增施铵态氮肥可降低硝酸盐和亚硝酸盐在菠菜体内的累积,并有效调节氨基酸和有机酸的代谢。因此,在菠菜种植过程,应该合理地搭配铵态氮肥和硝态氮肥,以便在保证安全性和营养价值的基础上获取最大的生物量。     

不同氮肥对潮土中磷肥转化的动态影响

利用室内土培试验研究了不同氮肥对潮土中磷肥转化的动态影响。结果表明，除硝酸铵，不同氮肥均显著降低土壤有效磷含量，其中以硝酸钙和尿素处理作用最显著；不同氮肥均显著降低土壤水溶性磷含量，但硝酸铵的作用显著小于其他氮肥；各氮肥处理在培养15d时，土壤水溶性磷含量差异最显著，硝酸钙和尿素处理的土壤水溶性磷含量有小于氯化铵和硫酸铵处理的趋势，但随着时间延长，除硝酸铵外，各氮肥处理间差异不大。