施氮对水稻土N2O释放及反硝化功能基因(narG/nosZ)丰度的影响

以紫潮泥和红黄泥两种不同质地的水稻土壤作为研究对象,通过室内培养试验,分析施用硝态氮肥对N2O释放和反硝化基因(narG/nosZ)丰度的影响,并探讨反硝化基因丰度与N2O释放之间的关系。结果表明,施用硝态氮显著增加两种水稻土的N2O释放量。在72h培养过程中,施氮改变了紫潮泥反硝化基因(narG/nosZ)的丰度,但并未明显影响红黄泥反硝化基因(narG/nosZ)丰度。通过双变量相关分析发现,除了紫潮泥narG基因外,其它的反硝化基因丰度和N2O释放之间并没有显著相关性。     

设施菜田不同碳氮管理对反硝化菌结构和功能的影响

【目的】通过6年长期定位试验,比较设施菜田不同碳氮管理下反硝化菌结构和功能的差异。【方法】采用末端限制性片段多态性(T-RFLP)和变性梯度凝胶电泳(DGGE)方法分别分析nir K/nir S和nos Z型反硝化菌群结构特征,利用自动连续在线培养监测体系(Robot系统)测定分析NO/(NO3-+NO2-)和N2O/(N2O+N2)产物比,并通过乙炔抑制法测定反硝化酶活性。【结果】传统施肥处理(CN)显著改变了nir K和nos Z型反硝化菌的结构,增加了NO/(NO3-+NO2-)和N2O/(N2O+N2)产物比。nir S型菌受碳氮管理影响较小。减氮(RN)和添加秸秆处理(RN+S)的nir K和nos Z型反硝化菌结构与CN处理的差异性显著,且会显著降低NO/(NO3-+NO2-)和N2O/(N2O+N2)产物比;与CN和RN相比,RN+S显著增加反硝化酶活性。【结论】设施菜田长期传统施肥措施改变了反硝化菌的结构和功能,增加土壤自身的NO产生能力并减弱了N2O还原N2的能力。减氮和添加秸秆管理能形成自身的反硝化菌群结构,并降低NO和N2O排放风险;秸秆的添加会促进反硝化潜在速率,降低菜田NO3-淋洗风险。     

硫化物抑制潮土反硝化过程中氧化亚氮还原的菌群机制

【背景】土壤中的反硝化作用形成气态产物N_2O和N_2,会导致氮素的气态损失,并造成温室效应。硫化物对土壤的N_2O还原具有抑制作用,但其对菌群和功能基因的影响机制还不清楚。【目的】研究有无外加碳源情况下,硫化物对反硝化作用中间产物(NO、N_2O)的积累、反硝化功能基因(narG、nirS、nirK和nosZ)表达量以及菌群结构的影响。【方法】分别设置不同量葡萄糖(0和1000mg-C/kg干重土壤)和硫化钠(0和150mg-S/kg干重土壤)添加的交叉处理,进行室内微宇宙培养实验,利用自动化培养与实时气体检测系统检测培养过程中NO、N_2O和N_2的积累量,通过反转录定量PCR测定反硝化功能基因表达量,利用MiSeq技术平台基于16S rRNA基因序列的高通量测序分析样品的菌群结构。【结果】硫化钠的添加显著抑制N_2O还原,但是其对于N_2O积累量没有显著影响,却显著降低了NO的积累量。硫化钠的添加短时间内在转录水平上显著抑制N_2O还原酶的活性,并且抑制固氮弧菌属(Azoarcus)、微枝形杆菌属(Microvirga)、剑菌属(Ensifer)、氮氢单胞菌属(Azohydromonas)、芽孢杆菌属(Bacillus)、斯科曼氏球菌属(Skermanella)、申氏杆菌属(Shinella)和西索恩氏菌属(Chthoniobacter)的基因转录,降低它们的转录本丰度,结合Kyoto Encyclopedia of Genes andGenomes(KEGG)数据库的查询结果,发现硫化钠的添加抑制了不产生N_2O的N_2O还原反硝化细菌的生长。【结论】堆肥或其他原因引起的土壤硫化物增加,导致反硝化过程N_2O还原被抑制的原因是由于其对氧化亚氮基因转录的抑制和对不同反硝化菌的选择作用,研究结果有助于认识硫化物对氮代谢影响的微生物机制。     

施肥制度对水稻土壤nosZ型反硝化细菌群落的影响

由含氧化亚氮还原酶(NOS)的反硝化细菌驱动的氧化亚氮(N2O)还原成氮气(N2)的过程是N2O排放的重要调控途径。为探明施肥对稻田土壤nosZ型反硝化细菌群落的影响,采用荧光定量PCR和高通量测序等方法,研究了湖南省宁乡县长达30年的定位试验条件下4种施肥制度[不施肥(CK)、化肥(CF)、70%化肥+30%有机肥(CFM1)和40%化肥+60%有机肥(CFM2)]对水稻土壤nosZ型反硝化细菌数量和群落结构的影响。结果表明:不同施肥处理nosZ基因丰度为2.14×10~8～6.09×10~8copies·g~(-1)干土,施肥处理nosZ基因拷贝数比对照低47.3%～64.8%(P0.05),但不同有机肥配施比例处理间nosZ基因拷贝数差异不显著;变形菌门是优势门水平类群,占总序列的60.2%～77.5%; Bacteria_unclassified、Proteobacteria_unclassified、Betaproteobacteria_unclassified和根瘤菌目为优势目水平类群,占总序列的93.6%～95.9%。施肥显著降低了Proteobacteria_unclassified的相对丰度(P0.01),但显著提高了根瘤菌目、environmental_samples和红环菌目的相对丰度(P0.05);施肥显著改变nosZ型反硝化细菌的群落结构,但有机肥配施比例对其影响较弱;除碳氮比外,其他土壤理化性质均显著影响nosZ型反硝化细菌的数量和群落结构,其中,硝态氮和土壤p H是驱动nosZ型反硝化细菌群落变化的主要因子;施肥显著影响nosZ型反硝化细菌数量和群落结构,有机肥配施比例对nosZ型反硝化细菌群落的影响较弱,研究结果为进一步阐述施肥制度对土壤反硝化微生物的影响提供依据。     

过量施肥对设施菜田土壤菌群结构及N2O产生的影响

【背景】N_2O是一种很强的温室气体,其温室效应强度大约是CO_2的265倍。土壤氮肥施加量是影响N_2O排放的重要因素,而厌氧条件下微生物反硝化则是N_2O产生的重要途径。【目的】研究过量施肥条件下蔬菜大棚土壤菌群结构变化及其对N_2O气体排放的影响。【方法】利用自动化培养与实时气体检测系统(Robot)监测土壤厌氧培养过程中N_2O和N_2排放通量,比较过量施肥和减氮施肥模式下土壤N_2O排放模式的差异。通过Illumina二代测序平台对这2种不同施肥处理的土壤微生物群落进行高通量测序,研究不同施肥量对土壤菌群组成的影响。【结果】过量施肥土壤中硝酸盐的含量大约是减氮施肥土壤的2倍,通过添加硝酸盐使2种土壤的硝酸盐含量均为60 mg/kg或为200 mg/kg时,过量施肥土壤在厌氧培养前期N_2O气体的产生量及产生速度都明显高于减氮施肥土壤。另外,过量施肥导致土壤菌群结构发生显著改变,并且降低了土壤微生物的多样性。相对于减氮施肥,过量施肥方式富集了Rhodanobacter属的微生物。PICRUSt预测结果显示,传统施肥没有显著改变反硝化功能基因相对丰度。【结论】长期过量氮肥施用显著增加了土壤N_2O的排放,可能原因是施肥改变了包括氮转化相关微生物在内的土壤菌群组成,从而影响了土壤N_2O气体的形成与还原过程。     

氮磷添加对草甸草原土壤氮磷转化功能基因丰度的影响

氮添加是提高退化草地生产力的主要养分管理措施,而过量的氮输入会导致土壤酸化、增加硝酸盐淋溶损失和温室气体排放。旨在明确草原割草利用下土壤氮、磷转化功能基因丰度对氮磷添加的响应规律,为定向调控打草场土壤氮、磷转化过程,提高养分利用效率,减少温室气体N₂O排放提供科学依据。2018—2020年在呼伦贝尔草甸草原打草场设置了5个施氮水平(0、1.55、4.65、13.95、27.9 g N m^-2 a^-1)和3个磷水平(0、5.24、10.48 g P m^-2 a^-1),裂区试验设计,在植物不同生长时期测定土壤氨氧化(amoA-AOA和amoA-AOB)、反硝化(narG、nirK、nirS和nosZ)和磷转化(phoD)基因丰度。结果表明,土壤氮转化基因丰度受到氮、磷添加的调控,而氮、磷添加对土壤磷转化功能基因丰度无显著影响(P>0.05)。氮添加可提高amoA-AOB基因丰度,增加氨氧化细菌调控土壤总硝化速率的相对重要性,因此能增加硝酸盐淋溶损失潜势。高氮处理下添加磷可降低...     

干湿交替对生物滞留系统中氮素功能微生物群落的影响

【目的】为探究生物滞留系统干湿交替下环境因子对氮素功能微生物群落的影响。【方法】应用高通量测序技术(Illumina MiSeq PE300),并以amoA和nirS功能基因为分子标记,对无植物型和植物型生物滞留系统在干湿交替下不同土壤空间位置(种植层、淹没层)的硝化和反硝化细菌的多样性和群落结构进行研究,并对微生物群落与环境因子的相互关系进行相关性分析。【结果】微生物种群的功能基因存在显著的空间差异,相比淹没层,种植层的功能细菌更丰富。种植层的OTUs高于淹没层,而进水再湿润促使两种功能基因在种植层和淹没层的OTUs占比差异性增大。群落组成分析表明,amoA型硝化细菌和nirS型反硝化细菌的优势细菌门均为变形菌门(Proteobacteria)。虽然植物根系对氮素功能微生物的多样性指数影响不显著,但在属水平上,植物系统种植层的反硝化菌群种类高于淹没层,而无植物系统则刚好相反。CCA/RDA分析表明,土壤空间位置是影响硝化和反硝化菌群结构的最重要环境因子。【结论】本研究证实干湿交替运行下生物滞留系统中的氮素功能微生物群落受土壤空间位置、水分含量和植物根系的共同调控,其机制有待进一步研究。     

不同放牧强度下土壤氨氧化和反硝化微生物的变化特征

土壤硝化及反硝化功能微生物在氮素可利用性、硝酸盐淋溶和氧化亚氮温室气体排放等方面起着关键作用,在指示不同放牧强度对生态系统的影响及预测草地生态系统退化状况等方面具有重要意义。以内蒙古干旱半干旱草原不同放牧强度(轻度、中度和重度)的长期试验样地为对象,应用定量PCR和限制性末端片段长度多态性(Terminal restriction fragment length polymorphism,T-RFLP)的方法,研究土壤氨氧化古菌(ammonia-oxidizing archaea,AOA)、氨氧化细菌(ammonia-oxidizing bacteria,AOB)和反硝化细菌的丰度、群落结构和多样性对不同放牧强度的响应。结果表明,土壤p H和铵态氮含量分别在7.90—8.18和6.37—35.92 mg/kg之间,中度放牧处理显著增高了土壤pH(P=0.03),而铵态氮含量在重度放牧处理中最高(P=0.02)。不同放牧强度下土壤异养呼吸相比未放牧处理均显著降低(P=0.02)。土壤AOA-amoA和AOB-amoA基因丰度范围分别为每克干土(4.94—7.60)×10~9个拷贝数和(0.68—3.75)×10~6个拷贝数,放牧处理对AOA-amoA基因丰度无显著影响,中度放牧处理显著降低了AOB-amoA基因丰度(P=0.04);反硝化微生物nosZ基因丰度随在轻度放牧处理中最低(P=0.03)。土壤铵态氮含量是影响AOA-amoA和AOB-amoA基因丰度的主要因子,而nosZ基因丰度主要受反硝化底物含量及土壤通气状况的影响。冗余分析表明由放牧所引起的可利用性氮含量的变化是导致氨氧化和反硝化微生物群落结构显著变化的主要因素。     

增温与降水变化对青藏高原高寒草甸土壤nirS反硝化菌群落丰度和群落结构的影响

全球变化已成为国际研究热点。青藏高原属典型生态脆弱带,该地区升温幅度更加明显,已导致大量冰川融化和明显降水变化,进而使该地区水循环和土壤水分发生巨大变化。温度和降水的变化可能会引起土壤微生物丰度和群落结构的改变,进而影响生物地球化学循环。但青藏高原地区土壤微生物群落结构和功能对全球变化响应的研究较少。研究了模拟增温和降水变化对青藏高原高寒草甸土壤nirS反硝化菌群落丰度和群落结构的影响。研究表明,增温1、2、4℃对nirS基因丰度影响不显著;增加降水100%时,增温4℃处理显著增加nirS基因丰度(P0.05)。在未升温与升温2℃背景下增加和减少降水对nirS基因丰度的影响不显著。增温和增减降水均显著影响nirS反硝化菌群落结构,且两个因子具有一定的交互作用。CCA结果显示,增温和降水的共同解释变量中,增温对nirS反硝化菌群落结构变化的影响达极显著(P0.01),解释了其中的54.2%,降水变化解释了45.5%(P0.05)。     

施肥对设施菜地nirK型反硝化细菌群落结构和丰度的影响

采用末端限制性片段多态性分析(T-RFLP)和实时荧光定量PCR(real-time PCR)方法,研究了甘肃武威设施菜地不同施肥条件下0~20 cm、20~40 cm土层中土壤nirK型反硝化细菌群落结构和丰度的变化.结果表明:施肥对土壤中nirK型反硝化细菌的群落结构具有明显影响,且对70、156、190 bp片段所代表设施菜地土壤优势种群影响最显著.施肥对0~20cm土层nirK型反硝化细菌丰度有明显影响,其最大值出现在全有机肥(M)处理、为每克干土2.16×107个拷贝数,分别是对照(CK)和全化肥(NPK)处理的2.04和2.02倍.设施菜地土壤0~20 cm与20~40 cm土层nirK型反硝化细菌的优势种群及其基因丰度均存在显著差异,且设施菜地土壤中nirK型反硝化细菌的群落结构和丰度与大田差异明显.土壤pH值、有机质及硝酸盐含量均影响nirK型反硝化细菌的群落结构和丰度.系统发育分析结果表明,土壤中除存在与厌氧反硝化细菌亲缘相近的nirK型反硝化微生物外,还存在与好氧反硝化菌亲缘关系相近的nirK型反硝化微生物,如根瘤菌属、苍白杆菌属、土壤杆菌属等.     

Symbiotic relationships between soil fungi and plants reduce N2O emissions from soil

N₂O is a potent greenhouse gas involved in the destruction of the protective ozone layer in the stratosphere and contributing to global warming. The ecological processes regulating its emissions from soil are still poorly understood. Here, we show that the presence of arbuscular mycorrhizal fungi (AMF), a dominant group of soil fungi, which form symbiotic associations with the majority of land plants and which influence a range of important ecosystem functions, can induce a reduction in N₂O emissions from soil. To test for a functional relationship between AMF and N₂O emissions, we manipulated the abundance of AMF in two independent greenhouse experiments using two different approaches (sterilized and re-inoculated soil and non-mycorrhizal tomato mutants) and two different soils. N₂O emissions were increased by 42 and 33% in microcosms with reduced AMF abundance compared to microcosms with a well-established AMF community, suggesting that AMF regulate N₂O emissions. This could partly be explained by increased N immobilization into microbial or plant biomass, reduced concentrations of mineral soil N as a substrate for N₂O emission and altered water relations. Moreover, the abundance of key genes responsible for N₂O production (nirK) was negatively and for N₂O consumption (nosZ) positively correlated to AMF abundance, indicating that the regulation of N₂O emissions is transmitted by AMF-induced changes in the soil microbial community. Our results suggest that the disruption of the AMF symbiosis through intensification of agricultural practices may further contribute to increased N₂O emissions.     

The effects of stubble retention and nitrogen application on soil microbial community structure and functional gene abundance under irrigated maize

The effects of agronomic management practices on the soil microbial community were investigated in a maize production system in New South Wales, Australia. The site has been intensively studied to measure the impact of stubble management and N-fertilizer application on greenhouse gas emissions (CO(2) and N(2)O), N-cycling, pathology, soil structure and yield. As all of these endpoints can be regulated by microbial processes, the microbiology of the system was examined. Soil samples were taken after a winter fallow period and the diversity of the bacterial and fungal communities was measured using PCR-denaturing gradient gel electrophoresis. Stubble and N shifted the structure of bacterial and fungal communities with the primary driver being stubble addition on the fungal community structure (P<0.05 for all effects). Changes in C, N (total and NO(3)), K and Na, were correlated (P<0.05) with variation in the microbial community structure. Quantitative PCR showed that nifH (nitrogen fixation) and napA (denitrification) gene abundance increased upon stubble retention, whereas amoA gene numbers were increased by N addition. These results showed that the management of both stubble and N have significant and long-term impacts on the size and structure of the soil microbial community at phylogenetic and functional levels.     

Effects of Biochar Addition on CO2 and N2O Emissions following Fertilizer Application to a Cultivated Grassland Soil

Carbon (C) sequestration potential of biochar should be considered together with emission of greenhouse gases when applied to soils. In this study, we investigated CO₂ and N₂O emissions following the application of rice husk biochars to cultivated grassland soils and related gas emissions tos oil C and nitrogen (N) dynamics. Treatments included biochar addition (CHAR, NO CHAR) and amendment (COMPOST, UREA, NO FERT). The biochar application rate was 0.3% by weight. The temporal pattern of CO₂ emissions differed according to biochar addition and amendments. CO₂ emissions from the COMPOST soils were significantly higher than those from the UREA and NO FERT soils and less CO₂ emission was observed when biochar and compost were applied together during the summer. Overall N₂O emission was significantly influenced by the interaction between biochar and amendments. In UREA soil, biochar addition increased N₂O emission by 49% compared to the control, while in the COMPOST and NO FERT soils, biochar did not have an effect on N₂O emission. Two possible mechanisms were proposed to explain the higher N₂O emissions upon biochar addition to UREA soil than other soils. Labile C in the biochar may have stimulated microbial N mineralization in the C-limited soil used in our study, resulting in an increase in N₂O emission. Biochar may also have provided the soil with the ability to retain mineral N, leading to increased N₂O emission. The overall results imply that biochar addition can increase C sequestration when applied together with compost, and might stimulate N₂O emission when applied to soil amended with urea.     

Soil microorganisms as controllers of atmospheric trace gases (H2, CO, CH4, OCS, N2O, and NO).

Production and consumption processes in soils contribute to the global cycles of many trace gases (CH4, CO, OCS, H2, N2O, and NO) that are relevant for atmospheric chemistry and climate. Soil microbial processes contribute substantially to the budgets of atmospheric trace gases. The flux of trace gases between soil and atmosphere is usually the result of simultaneously operating production and consumption processes in soil: The relevant processes are not yet proven with absolute certainty, but the following are likely for trace gas consumption: H2 oxidation by abiontic soil enzymes; CO cooxidation by the ammonium monooxygenase of nitrifying bacteria; CH4 oxidation by unknown methanotrophic bacteria that utilize CH4 for growth; OCS hydrolysis by bacteria containing carbonic anhydrase; N2O reduction to N2 by denitrifying bacteria; NO consumption by either reduction to N2O in denitrifiers or oxidation to nitrate in heterotrophic bacteria. Wetland soils, in contrast to upland soils are generally anoxic and thus support the production of trace gases (H2, CO, CH4, N2O, and NO) by anaerobic bacteria such as fermenters, methanogens, acetogens, sulfate reducers, and denitrifiers. Methane is the dominant gaseous product of anaerobic degradation of organic matter and is released into the atmosphere, whereas the other trace gases are only intermediates, which are mostly cycled within the anoxic habitat. A significant percentage of the produced methane is oxidized by methanotrophic bacteria at anoxic-oxic interfaces such as the soil surface and the root surface of aquatic plants that serve as conduits for O2 transport into and CH4 transport out of the wetland soils. The dominant production processes in upland soils are different from those in wetland soils and include H2 production by biological N2 fixation, CO production by chemical decomposition of soil organic matter, and NO and N2O production by nitrification and denitrification. The processes responsible for CH4 production in upland soils are completely unclear, as are the OCS production processes in general. A problem for future research is the attribution of trace gas metabolic processes not only to functional groups of microorganisms but also to particular taxa. Thus, it is completely unclear how important microbial diversity is for the control of trace gas flux at the ecosystem level. However, different microbial communities may be part of the reason for differences in trace gas metabolism, e.g., effects of nitrogen fertilizers on CH4 uptake by soil; decrease of CH4 production with decreasing temperature; or different rates and modes of NO and N2O production in different soils and under different conditions.     

Soil anammox community structure in different land use soils treatment with 13 C urea as determined by analysis of phospholipid fatty acids

The anaerobic ammonium oxidation (anammox) process is globally an important nitrogen-cycling process mediated by specialized microbes. However, still little information is documented about anammox microbial community structure under agricultural soils. The anaerobic incubation experiment was conducted to study the impacts of different land use soils fertilized by 13C-urea on the activity and diversity of anammox bacteria using stable isotope to probe the phospholipid fatty acid (PLFA-SIP). The 13C was preferentially incorporated in ratios PLFAs 16:1ω7c, 16:1ω5c, and 16:0. The results revealed that the abundance of the anammox bacteria (both hzs-β and hzo) were observed in vegetable soil V1 and paddy soils (R1 and R2) means that they were positively correlated with 13C-urea but were negatively correlated with NO3 −-N and NH4 +-N concentrations. Thus, 13C-PLFAs 16:1ω7c, 16:1ω5c, and 16:0 could be the biomarker as soil anammox. The anaerobic microbial community composition of soils under different land use systems was diverse, and V1, R1, and R2 had similar microbial diversity and higher microbial biomass. The principal component analysis between soil properties and gene abundance suggested that not only pH but also soil organic matter, available P, and available K were important factors for the anammox process. This study suggested that 13C-Urea-PLFA for anaerobic incubation was a simple method to study anammox microbial community structure through affecting the soil nutrients, and the different land use systems played important roles in determining the microbial composition of soils.     

Regulation of denitrification at the cellular level: a clue to the understanding of N2O emissions from soils

Denitrifying prokaryotes use NO(x) as terminal electron acceptors in response to oxygen depletion. The process emits a mixture of NO, N(2)O and N(2), depending on the relative activity of the enzymes catalysing the stepwise reduction of NO(3)(-) to N(2)O and finally to N(2). Cultured denitrifying prokaryotes show characteristic transient accumulation of NO(2)(-), NO and N(2)O during transition from oxic to anoxic respiration, when tested under standardized conditions, but this character appears unrelated to phylogeny. Thus, although the denitrifying community of soils may differ in their propensity to emit N(2)O, it may be difficult to predict such characteristics by analysis of the community composition. A common feature of strains tested in our laboratory is that the relative amounts of N(2)O produced (N(2)O/(N(2)+N(2)O) product ratio) is correlated with acidity, apparently owing to interference with the assembly of the enzyme N(2)O reductase. The same phenomenon was demonstrated for soils and microbial communities extracted from soils. Liming could be a way to reduce N(2)O emissions, but needs verification by field experiments. More sophisticated ways to reduce emissions may emerge in the future as we learn more about the regulation of denitrification at the cellular level.     

Contributions of Autotrophic and Heterotrophic Nitrifiers to Soil NO and N(2)O Emissions

Soil emission of gaseous N oxides during nitrification of ammonium represents loss of an available plant nutrient and has an important impact on the chemistry of the atmosphere. We used selective inhibitors and a glucose amendment in a factorial design to determine the relative contributions of autotrophic ammonium oxidizers, autotrophic nitrite oxidizers, and heterotrophic nitrifiers to nitric oxide (NO) and nitrous oxide (N(2)O) emissions from aerobically incubated soil following the addition of 160 mg of N as ammonium sulfate kg. Without added C, peak NO emissions of 4 mug of N kg h were increased to 15 mug of N kg h by the addition of sodium chlorate, a nitrite oxidation inhibitor, but were reduced to 0.01 mug of N kg h in the presence of nitrapyrin [2-chloro-6-(trichloromethyl)-pyridine], an inhibitor of autotrophic ammonium oxidation. Carbon-amended soils had somewhat higher NO emission rates from these three treatments (6, 18, and 0.1 mug of N kg h after treatment with glucose, sodium chlorate, or nitrapyrin, respectively) until the glucose was exhausted but lower rates during the remainder of the incubation. Nitrous oxide emission levels exhibited trends similar to those observed for NO but were about 20 times lower. Periodic soil chemical analyses showed no increase in the nitrate concentration of soil treated with sodium chlorate until after the period of peak NO and N(2)O emissions; the nitrate concentration of soil treated with nitrapyrin remained unchanged throughout the incubation. These results suggest that chemoautotrophic ammonium-oxidizing bacteria are the predominant source of NO and N(2)O produced during nitrification in soil.