转BADH基因大豆对盐碱土壤氮素转化的影响

以转甜菜碱醛脱氢酶(betaine aldehyde dehydrogenase)基因(BADH)大豆、非转基因亲本‘黑农35’、野生大豆、当地栽培种‘抗线王’、耐盐碱性较差品种‘合丰50’等5种大豆品种为材料,在典型盐碱土封闭种植,于大豆苗期、花荚期、鼓粒期和成熟期取根际土,采用经典方法测定氮素转化过程相关的细菌数量、生化功能及速效氮含量等指标的动态变化,为揭示转BADH基因大豆对土壤氮素转化的影响机制提供理论支持。结果表明:与非转基因亲本相比,转BADH基因大豆对苗期和花荚期根际土壤固氮菌数量有促进作用,但抑制苗期和花荚期根际土壤氨化细菌数量,对硝化细菌数量无显著性影响;显著促进成熟期大豆根际土壤固氮作用强度,对大豆苗期、花荚期和鼓粒期根际土壤氨化作用强度有显著抑制作用,显著促进各生育时期硝化作用强度;转BADH基因大豆苗期和花荚期根际土壤铵态氮含量显著降低,对鼓粒期根际土壤铵态氮含量无显著性影响,成熟期根际土壤铵态氮含量显著增高,大豆苗期、鼓粒期和成熟期根际土壤硝态氮含量显著升高,花荚期根际硝态氮含量显著降低。研究结果说明,转BADH基因大豆通过调节苗期、花期根际土壤氮素转化功能菌数量和生化过程强度进而影响氮素转化。     

4种熏蒸剂对土壤氮素转化的影响

采用室内恒温通气培养法,以北京大棚蔬菜地土壤为对象,研究熏蒸剂氯化苦(Pic)、碘甲烷(MeI)、1,3-二氯丙烯(1,3-D)和二甲基二硫(DMDS)对土壤氮素矿化和硝化的影响。结果表明,4种熏蒸剂处理后短期内均能显著增加土壤中氮累积矿化量,在处理后第0d,1,3-D、MeI、DMDS、Pic处理的氮累积矿化量分别为320.62mg·kg-1、317.25mg·kg-1、287.87mg·kg-1、278.73mg·kg-1,较对照(189.89mg·kg-1)分别增加68.85%、67.07%、51.60%、46.78%。4种熏蒸剂处理后土壤硝化作用过程受到显著抑制,在药剂熏蒸处理第0d,各熏蒸处理土壤中铵态氮含量均高于对照组,其中MeI处理组铵态氮含量最高,为194.97mg·kg-1,对照组铵态氮含量最低,为28.82mg·kg-1。Pic、1,3-D、DMDS、MeI处理后第0d硝化抑制率分别为40.8%、20.8%、26.9%、24.1%。Pic、1,3-D、MeI对硝化作用的抑制至少维持两周,DMDS的抑制作用至少维持1周。在后期培养过程中,各处理矿化作用和硝化作用都逐渐恢复至对照水平。     

氯甲基吡啶对滴灌棉田土壤微生物群落功能多样性的影响

已知硝化抑制剂氯甲基吡啶能有效抑制土壤硝化,减少氮的淋洗和硝化-反硝化损失,促进作物对氮素的吸收,但是其对干旱区滴灌条件下土壤微生物群落功能多样性的影响尚不明确。本试验研究了尿素添加氯甲基吡啶(Nitrapyrin)分次随水滴施对干旱区滴灌棉田土壤微生物碳代谢和群落功能多样性的影响。试验采用随机区组设计,设置不施氮肥[CK,0 kg(N)·hm~(-2)]、单施尿素[Urea,225 kg(N)·hm~(-2)]和尿素添加氯甲基吡啶[Urea+nitrapyrin,225 kg(N)·hm~(-2)+2.25 kg(nitrapyrin)·hm~(-2)]3个处理,重复4次,采用Biolog-ECO法进行土壤微生物碳代谢和功能多样性研究。结果表明:与不施氮肥(CK)相比,施用尿素和尿素添加氯甲基吡啶均能显著提高土壤微生物对31种碳源的代谢能力(AWCD)和代谢强度(S)(P0.05),增加土壤微生物多样性和丰富度(Shannon指数、Simpson指数、Mc Intosh指数和Richness指数)以及对各类碳源的利用能力。尿素添加氯甲基吡啶随水滴施后,土壤微生物AWCD值、碳代谢强度、Shannon指数、Simpson指数、Mc Intosh指数以及Richness指数均大于单施尿素处理,且较单施尿素处理分别提高13.83%、9.33%、1.29%、1.34%、11.26%、11.79%(P0.05),均匀度指数则低于单施尿素处理(P0.05)。PCA和聚类分析结果表明,施用尿素和尿素添加氯甲基吡啶对土壤微生物群落功能多样性均产生了显著影响,但尿素添加氯甲基吡啶与单施尿素处理差异不显著;氯甲基吡啶的添加提高了土壤微生物对聚合物、酚酸、羧酸、氨基酸以及胺类的利用,降低了对碳水化合物的利用(P0.05)。上述研究结果得出,在干旱区滴灌棉田,尿素添加氯甲基吡啶分次随水滴施可调控土壤的微生态环境,在一定程度上提高土壤微生物的代谢能力,增加微生物群落功能多样性,缓解因长期施用无机氮肥导致的土壤微生物活性的降低。     

Effect of Baythroid on nitrogen transformations in soil

Laboratory incubation experiments were conducted in soil to study the influence of the insecticide Baythroid on immobilization-remineralization of added inorganic N, mineralization of organic N, and nitrification of added NH _inf4 ^su+ -N. Baythroid was applied at 0, 0.4, 0.8, 1.6, 3.2, and 6.4 g g^-1 soil (active ingredient basis). The treated soils were incubated at 30°C for different time intervals depending upon the experiment. The immobilization and mineralization of N were significantly increased in the presence of Baythroid, the effect being greater with higher doses of the insecticide. Conversely, nitrification was retarded at lower doses of Baythroid and significantly inhibited at higher doses. The results of these studies suggest that excessive amonts of insecticide residues affect different microbial populations differently, leading to changes in nutrient cycling.     

除草剂对不同种植年限柑橘园土壤氮转化过程及温室气体排放的影响

为探讨除草剂施用对柑橘园土壤氮转化及温室气体排放的影响,在实验室培养条件下,研究了0年(林地)、种植10年和30年的柑橘园土壤中分别添加除草剂草甘膦和丁草胺后,尿素态氮含量、硝化和反硝化作用以及温室气体排放的变化。研究结果表明,橘园土壤中尿素第1 d的水解率、氮肥硝化率、反硝化作用损失总量以及N_2O和CO_2排放量显著高于林地土壤(P0.05)。与10年橘园土壤相比,30年橘园土壤显著增加了尿素的水解速率、氮肥硝化率和CO_2排放量(P0.05),但二者的反硝化损失量没有显著差异。施用草甘膦和丁草胺都显著促进了林地土壤的尿素水解(P0.05),第1 d尿素态氮含量分别降低11.20%和12.43%;但对3种土壤氮肥的硝化率均没有明显影响。施用丁草胺显著降低了林地土壤的CO_2排放量(P0.05),对两种橘园土壤的CO_2排放没有明显影响,但明显增加了两种橘园土壤的N_2O排放总量(P0.05),分别比不施除草剂增加56.27%和85.41%;施用草甘膦对3种土壤的N_2O和CO_2排放均没有明显影响。可见,草甘膦和丁草胺的施用不会对柑橘园土壤的氮转化过程产生影响,但丁草胺显著增加了柑橘园土壤的N_2O排放。     

通过调节土壤氮素转化提高有机物料对红壤酸度的改良效果

通过培养试验,比较研究了油菜秸秆、稻草、香樟叶和豌豆秸秆单独施用以及油菜秸秆、稻草和香樟叶与豌豆秸秆混合施用对红壤酸度的改良效果。结果表明,在60天培养期内,添加4种物料均提高了土壤pH。培养试验结束时香樟叶、油菜秸秆、豌豆秸秆和稻草分别使土壤pH相对对照增加0.53、0.42、0.30和0.26。对于灰化碱含量很高的非豆科物料如香樟,其对土壤酸度的改良效果主要来源于物料所含碱性物质和物料对土壤硝化反应的抑制,但对灰化碱含量较低的非豆科物料如油菜秸秆和稻草,其改良效果主要来源于后者。豆科类豌豆秸秆主要通过所含碱性物质和有机氮矿化提高土壤pH,但培养试验后期铵态氮硝化反应释放的质子抵消了其部分改良效果。将油菜秸秆、稻草和香樟叶与豌豆秸秆配合施用,使硝化反应受到一定程度的抑制,提高了物料对土壤酸度的改良效果。培养试验结束时,香樟叶、稻草和油菜秸秆与豌豆秸秆配合施用比豌豆秸秆单独施用土壤pH分别高0.25、0.18和0.12。研究发现,香樟叶灰化碱含量很高,无论单独施用,还是与豌豆秸秆配合施用均有很好的改良效果,因此在南方地区推广种植香樟可以通过其凋落物修复酸化的森林土壤。     

Effects of nitrapyrin,terrazole, and simazine on soil nitrogen transformation and corn growth

Abstract

Nitrapyrin, terrazole and simazine were evaluated as chemical inhibitors of biological nitrification and denitrification. Corn (Zea mays L. cv. Hybrid Pioneer 3343) was grown in 60‐liter pots filled with a 50/50 (V/V) sand/Cecil clay mixture. Chemical treatments consisted of weekly applications of 0.25 ppm nitrapyrin, terrazole and/or simazine concurrently with 20 ppm N as either (NH₄)₂SO₄ or Ca(NO₃)₂ for 9 weeks. Thereafter, only N (20 ppm per pot) was applied to the media every three days for 4 weeks. Nitrapyrin, terrazole and simazine reduced nitrification resulting in both higher total plant N and residual soil NH₄ content relative to the control plants and soil. Plant growth was reduced by the inhibitory effects of the chemicals on nitrification and subsequent NH₄ accumulation in the medium. All chemicals reduced denitrification with terrazole being more effective than nitrapyrin as reflected by higher N contents of plants and residual soil NO₃‐N. Nitrapyrin and/or terrazole applied with Ca(NO₃)₂ increased plant biomass, but simazine, by inducing higher N0₂ concentration in the plant tissues, sharply reduced plant growth relative to the other treatments. When simazine was part of the chemical treatment, its effects on plant growth and total N contents generally outweighed or masked those of nitrapyrin or terrazole.     

花生补灌条件下施氮对土壤氮素吸收与转化的影响

为提高辽西地区花生产量和水氮利用率,本文以‘白沙1016’为对象,采取裂区试验,主区为雨养(W0)和测墒补灌(W1)两种灌溉模式,子区为0 kg·hm~(-2)(N0)、40 kg·hm~(-2)(N1)、60 kg·hm~(-2)(N2)和80 kg·hm~(-2)(N3)4个施氮水平,研究施氮对测墒补灌条件下花生干物质积累和氮素积累及分配的影响。试验结果表明:在雨养和测墒补灌条件下,花生成熟期的单株干物质量分别为64.66~74.92 g和71.65~92.81 g,以W1N3处理最高,W0N0最低,且随施氮量呈现二次曲线变化趋势。花生植株氮积累量随施氮量变化趋势与干物质量一致,W1N2较其他处理显著提高了氮素积累量、产量和水分利用效率。测墒补灌优化了花生植株中氮素的分配,延长了叶片氮素积累时长,同时提高了叶片氮素向荚果的转移量,继而相对雨养处理显著增加了花生荚果氮积累量所占植株氮积累总量的比重(氮收获系数)2.13%、氮肥农学利用率78.57%、氮肥表观回收率25.90%。花生收获后,土壤硝态氮主要分布在0~40 cm土层内,占0~60 cm土层的77.75%,且累积量随着施氮量的增高而增加,但补灌会使土壤硝态氮下移造成硝态氮淋失。因此,综合考虑水氮利用效率,在辽西半干旱地区推荐W1N2为适宜花生生产水氮管理,其产量、水分利用效率和灌溉水利用效率最高,分别为6 485.03 kg·hm~(-2)、2.02 kg·m~(-3)和10.21kg·m~(-3)。     

冻融对土壤氮素转化和N2O排放的影响研究进展

在中、高纬度及高海拔地区,土壤冻融现象常有发生。冻融作用通过影响土壤理化性质和生物学性状进而影响土壤氮素转化过程及N₂O的产生和释放,但迄今关于冻融对土壤氮素转化过程影响的研究结果还不尽一致,正效应或负效应均存在,土壤冻融期间N₂O排放对全年N₂O排放总量的贡献程度也存在着较大差异。本文重点论述了土壤冻结或冻融循环过程对土壤氮矿化、固持、硝化和反硝化等主要氮素转化过程的影响机制,同时分析了可引起冻融期间N₂O排放强度变化的四种可能机理（禁锢-释放、环境-底物诱导、N₂O还原酶抑制和化学反硝化增强）。指出在全球变暖背景下研究土壤冻融格局改变影响土壤氮素转化过程及N₂O排放的必要性,并简要提出了若干理论问题及研究方向。     

耕层土层交换对土壤氮素关键转化过程和玉米氮素利用的影响

翻耕会使耕层土壤发生显著位置交换。耕层土壤位置交换会通过影响土壤物理、化学和生物性状,改变氮素转化过程。本文研究了土层交换对黄淮海平原南端砂姜黑土硝化、反硝化过程和玉米生长及氮素利用的影响,为该区域选择合理的耕作方式、减少氮素损失及提高氮素利用效率提供理论依据。试验在人工气候室条件下,以土壤(0～35 cm)田间原位分层作为常规土层处理(CK),以原位0～10 cm和10～20 cm土层交换后作为土层交换处理(SE),并用20μm的尼龙网区分非根际和根际土壤。于玉米小喇叭口期利用荧光定量PCR技术测定土壤氨氧化微生物和反硝化菌群丰度,并结合非根际和根际土壤的硝化潜势、土壤呼吸、反硝化能力、反硝化潜势、土壤理化性质和玉米总氮含量及根系形态的测定,探讨土层交换对土壤氮素转化和玉米生长及氮素利用的影响。结果显示,SE处理的玉米植株氮吸收量比CK处理显著降低8.9%(P0.05)。土层交换显著影响根际而不是非根际土壤的硝化潜势,使其显著降低13.5%(P0.05);并使非根际和根际土壤的反硝化能力分别提高36.6%(P0.05)和8.4%(P0.05)。土层交换使非根际和根际土壤的可溶性有机碳含量分别提高11.7%(P0.05)和5.2%。相关分析显示硝化潜势与氨氧化细菌(AOB)丰度呈显著正相关(r=0.91**),与氨氧化古菌(AOA)丰度无显著相关关系;反硝化能力与土壤可溶性有机碳和呼吸速率呈显著正相关(r=0.89**和0.93**),与nirK、nirS拷贝数无显著相关性;玉米植株氮吸收量与根际土壤的硝化潜势、根表面积×AOB拷贝数都呈显著正相关(r=0.83*和0.86*),而与反硝化能力呈显著负相关(r=?0.88**)。以上结果表明砂姜黑土土壤硝化速率的降低和反硝化速率的增强,是土层交换后玉米氮素利用效率低的重要原因。AOB是硝化速率的主要驱动微生物。土层交换后土壤可溶性有机碳是反硝化能力的关键主导因子。在翻耕条件下,有效调节土壤可溶性有机碳含量是提高作物氮肥利用效率的关键。     

Temporal variability in plant and soil nitrogen pools in a high-Arctic ecosystem

This study determined temporal variability in N pools, both aboveground and belowground, across two contrasting plant communities in high-Arctic Spitsbergen, Svalbard (78°N). We measured N pools in plant material, soil microbial biomass and soil organic matter in moist (Alopecurus borealis dominated) and dry (Dryas octopetala dominated) meadow communities at four times during the growing season. We found that plant, microbial and dissolved inorganic and organic N pools were subject to significant, but surprisingly low, temporal variation that was controlled primarily by changes in temperature and moisture availability over the short growing season. This temporal variability is much less than that experienced in other seasonally cold ecosystems such as alpine tundra where strong seasonal partitioning of N occurs between plant and soil microbial pools. While only a small proportion of the total ecosystem N, the microbial biomass represented the single largest of the dynamic N pools in both moist and dry meadow communities (3.4% and 4.6% of the total ecosystem N pool, respectively). This points to the importance of soil microbial community dynamics for N cycling in high-Arctic ecosystems. Microbial N was strongly and positively related to soil temperature in the dry meadow, but this relationship did not hold true in the wet meadow where other factors such as wetter soil conditions might constrain biological activity. Vascular live belowground plant parts represented the single largest plant N pool in both dry and moist meadow, constituting an average of 1.6% of the total N pool in both systems; this value did not vary across the growing season or between plant communities. Overall, our data illustrate a surprisingly low growing season variability in labile N pools in high-Arctic ecosystems, which we propose is controlled primarily by temperature and moisture.     

施用铵态氮对森林土壤硝态氮和铵态氮的影响

对取自武夷山的红壤、黄壤、黄壤性草甸土分别在对照(CK,N 0 mg/kg)、低氮(LN,N 50 mg/kg)、高氮(HN,N 100 mg/kg)3种氮(N)水平处理下开展培养实验,研究施加NH4+-N对森林土壤N转化的短期影响.结果表明,添加NH4+-N可显著(p＜0.05)降低土壤NO3--N含量4.5％～25.7％,但LN与HN处理差异不显著,NO3--N降低可能与NO3--N反硝化和异氧还原有关;然而,黄壤性草甸土NO3--N没有降低.与培养前比较,在第56天红壤NO3--N含量显著增加5倍左右;桐木关黄壤增加40％左右,而黄冈山25 km黄壤仅在CK处理下增加16％,但是黄壤性草甸土显著降低;结果显示LN与HN处理土壤NO3--N含量变化幅度小于CK.与CK相比,LN和HN处理红壤NH4+-N分别显著(p＜0.05)升高24.1％ ～ 96.5％和68.7％～114.1％,且随培养进行没有累积,可能与微生物固N有关;桐木关NH4+-N分别升高17.6％ ～ 39.6％和37.6％～95.8％ (p＜0.05),LN处理黄冈山25 km黄壤NH4+-N只有第7天升高17.8％ (p＜0.05),HN处理第7、14、28、42天显著升高17.5％～48.6％(p＜0.05).LN处理黄壤性草甸土的NH4+-N在前3周显著降低11.6％～28.5％ (p＜0.01); HN处理在第7天和14天分别降低10.8％(p＜0.01)和7.5％,但是在第28～56天显著增加17.6％～20.4％(p=0.002).随着培养进行,CK处理红壤NH4+-N逐渐降低,桐木关黄壤、黄冈山25 km黄壤和黄壤性草甸土升高;LN和HN处理黄壤和黄壤性草甸土NH4+-N逐渐升高.可见,不同海拔土壤类型对NH4+-N添加响应存在差异.     

放牧对羊草草原土壤氮素循环的影响

研究了放牧对内蒙古羊草草原土壤中N素分解细菌以及固N作用、氨化作用和硝化作用的影响,结果表明,轻度放牧使土壤中4类N素转化细菌的数量显著增加,也显著加强了土壤中的固N作用、氨化作用和硝化作用。促进了土壤中的N素循环;随放牧强度的增加,重度放牧则导致草原土壤中4类N素转化细菌数量均显著降低。显著抑制土壤中的固N作用和氨化作用,会阻碍土壤中的N循环的进程。放牧强度对N素转化细菌以及N循环中的固N作用、氨化作用和硝化作用的季节性变化规律无明显影响。     

Responses of nitrogen transformation and microbial community composition to nitrogen enrichment patch

Fertilization produces many nutrient patches that have been confirmed to affect root growth. However, it is not clear how nutrient transformation and microbial community composition are affected in an inorganic nutrient patch. In this experiment, a nitrogen enrichment patch was formed by the diffusion of a urea fertilizer layer in a specially-designed container. Responses of nitrogen transformation and microbial community composition to the nitrogen enrichment patch were investigated at different incubation times. Results showed that nitrogen status and microbial community composition were slightly affected in the control patch (CK patch). In the nitrogen enrichment patch, however, soil pH was significantly increased in most soil layers close to the urea fertilizer layer; NO₂⁻-N was the predominant form of mineral N, and its transformation to NO₃⁻-N was delayed. Microbial community composition shifted significantly, especially before day 28 of incubation. Principal components analysis (PCA) of phospholipid fatty acids (PLFAs) patterns showed that the microbial community presented different sensitivity to high nitrogen concentration. Fungi (18:2ω6,9) showed the least sensitivity to high concentrations of NO₂⁻-N and NO₃⁻-N. Gram-positive bacteria showed the most sensitivity to NO₂⁻-N. Gram-negative bacteria (cy17:0, cy19:0, 18:1ω9, and 18:1ω7) and actinomycetes (10Me17:0 and 10Me18:0) presented similar responses to NO₂⁻-N and NO₃⁻-N. Results of this study indicate that changes in nitrogen transformation and microbial community composition are likely to occur in nitrogen enrichment patches, but the extent of those changes depend on the microbial species and the distance of soil layers from the urea layer.     

添加葡萄糖对不同肥力黑土氮素转化的影响

氮是作物生长必需的大量营养元素,增施化学氮肥,是农业生产采取的主要增产措施之一。我国的氮肥消费量已占世界总消费量的约30%,但我国农业中氮素的生产效率趋于下降,而带来的农业环境污染则趋于加重。提高氮素利用率,降低其对环境的负面影响,在保障粮食安全的同时兼顾生     

土壤增氧方式对其氮素转化和水稻氮素利用及产量的影响

以3种不同生态型水稻品种中浙优1号(水稻)、IR45765-3B(深水稻)和中旱221(旱稻)为材料,比较研究了不同增氧方式(T1-增施过氧化钙、T2-微纳气泡水增氧灌溉、T3-表土湿润灌溉和CK-淹水对照)下稻田土壤氮素转化和水稻氮素吸收利用特性。结果表明:1)增氧处理明显改善土壤氧化还原状况,3种增氧方式下土壤氧化还原电位均高于CK。稻田增氧促进土壤氮素硝化,在分蘖期和齐穗期T1、T2和T3的土壤硝化强度和脲酶活性均显著高于CK,反硝化强度显著低于CK。2)不同增氧处理对水稻氮素吸收的影响不同,在拔节期、齐穗期和完熟期3品种的植株氮素积累量均表现为T1、T2显著高于CK,而T3显著低于CK;在完熟期,T1处理下中浙优1号、IR45765-3B和中旱221植株氮素积累量分别较CK增加了21.2%、13.2%和17.0%,而T2处理下3品种的植株氮素积累量分别较CK增加了14.3%、6.9%和9.1%。3)与CK相比,T1和T2显著提高水稻籽粒产量和收获指数,氮素籽粒生产效率与CK无显著差异,而T3显著增加水稻氮素干物质生产效率和氮素籽粒生产效率。可见,施用过氧化钙和微纳气泡水增氧灌溉能有效改善稻田土壤氧化还原状况,不仅显著提高水稻产量,而且显著增强稻田氮的硝化而减少氮素损失,从而提高水稻氮素积累量和氮素收获指数。     

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。     

影响砂姜黑土麦田土壤氮素转化的生物学因素 及其对供氮量的响应

砂姜黑土是我国典型的中低产田土壤类型,研究其在土壤微生物驱动下的氮素转化过程及其机制,可为定向调控土壤氮素转化过程,提高氮素利用效率并减少其负面效应提供科学依据。试验设置0 kg·hm~(-2)、120 kg·hm~(-2)、225 kg·hm~(-2)和330 kg·hm~(-2) 4个供氮量,分别于冬小麦越冬期、拔节期、抽穗期、开花期、灌浆期和成熟期测定小麦根际土壤氮转化相关微生物作用(氨化作用、硝化作用和反硝化作用)强度和土壤氮素转化相关酶(脲酶、蛋白酶)活性,土壤净氮素矿化速率、土壤硝态氮和铵态氮含量的变化,研究影响砂姜黑土麦田土壤氮素转化的生物学因素及其对不同供氮量的响应。结果表明,土壤氮素转化微生物及酶活跃时期为拔节到灌浆期,灌浆期之后土壤氨化作用强度、硝化作用强度、脲酶及蛋白酶活性降低;土壤净氮素矿化速率与土壤氮素转化微生物作用强度及酶活性的活跃期较为一致,在开花前后达到最高。除脲酶活性随供氮量增加持续上升外,土壤氮素转化微生物作用强度及蛋白酶活性均随供氮量的增加,在225 kg·hm~(-2)处理下达到最高,进一步增加供氮量至330 kg·hm~(-2),微生物作用强度及酶活性均表现出不同程度的下降。可见,砂姜黑土土壤氮素转化的活跃期与小麦需氮高峰期基本一致,有利于冬小麦的生长。但由于砂姜黑土中土壤硝化作用强度较低,土壤硝化能力有限,从而降低了氮素可利用性,且增加了土壤氨挥发损失的潜在风险。在一定范围内增加供氮量,有利于土壤氮素的转化,但供氮过多(330 kg·hm~(-2))则不利于砂姜黑土供氮能力的提高。     

Effect of the inhibitors nitrapyrin and sodium chlorate on nitrification and N2O formation in an acid forest soil

An acid forest soil from beech forest gaps, which were either limed or unlimed, and the undisturbed forest was investigated for the type of nitrifying populations and the process of N₂O evolution. To see whether nitrifiers were of heterotrophic or autotrophic origin, the nitrification inhibitors nitrapyrin and sodium chlorate were applied to disturbed soil samples which underwent laboratory incubations. Nitrapyrin inhibits autotrophic nitrification. In different studies, sodium chlorate has been identified as an inhibitor either of autotrophic or of heterotrophic nitrification. In the samples investigated only nitrapyrin inhibited the autotrophic nitrification occurring in the limed soil. Sodium chlorate effectively inhibited heterotrophic nitrification. In the limed forest floor samples, where most autotrophic nitrification occured, sodium chlorate showed no inhibitory effect. In another laboratory incubation experiment, N₂O evolution from undisturbed soil columns, to which the above inhibitors were applied, was investigated. In those samples, in which nitrification had been reduced, neither inhibitor significantly reduced N₂O evolution. Thus it was concluded that the contribution of nitrification to N₂O losses is negligible, and that N₂O evolution arises from the activity of denitrifying organisms. Microbial biomass and respiration measurements showed that the inhibitors did not affect microflora negatively.     

Effects of the application of wastevater from olive processing on soil nitrogen transformation

Abstract

An incubation experiment was performed to study the effects of wastewater from olive processing on nitrogen transformation in a calcareous soil. The application of this wastewater was shown to decrease NO₃ ^‐ formation in comparison with control assays during approximately the first half of the experimental period (6 weeks). Results were similar although more marked when vegetation water plus ammoniacal nitrogen was applied as opposed to ammoniacal nitrogen alone. The incorporation of vegetation water during the initial phases of study also reduced soil N‐NH₄ ⁺ levels both when residue only treatments were compared with controls and when vegetation water plus ammoniacal nitrogen treatments were compared with ammoniacal nitrogen only.