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1.
Ammonia oxidation, the first step of nitrification, is mediated by both ammonia-oxidizing archaea (AOA) and bacteria (AOB); however, the relative contributions of AOA and AOB to soil nitrification are not well understood. In this study we used 1-octyne to discriminate between AOA- and AOB-supported nitrification determined both in soil-water slurries and in unsaturated whole soil at field moisture. Soils were collected from stands of red alder (Alnus rubra Bong.) and Douglas-fir (Pseudotsuga menziesii Mirb. Franco) at three sites (Cascade Head, the H.J. Andrews, and McDonald Forest) on acidic soils (pH 3.9–5.7) in Oregon, USA. The abundances of AOA and AOB were measured using quantitative PCR by targeting the amoA gene, which encodes subunit A of ammonia monooxygenase. Total and AOA-specific (octyne-resistant) nitrification activities in soil slurries were significantly higher at Cascade Head (the most acidic soils, pH < 5) than at either the H.J. Andrews or McDonald Forest, and greater in red alder compared with Douglas-fir soils. The fraction of octyne-resistant nitrification varied among sites (21–74%) and was highest at Cascade Head than at the other two locations. Net nitrification rates of whole soil without NH4+ amendment ranged from 0.4 to 3.3 mg N kg−1 soil d−1. Overall, net nitrification rates of whole soil were stimulated 2- to 8-fold by addition of 140 mg NH4+-N kg−1 soil; this was significant for red alder at Cascade Head and the H.J. Andrews. Red alder at Cascade Head was unique in that the majority of NH4+-stimulated nitrifying activity was octyne-resistant (73%). At all other sites, NH4+-stimulated nitrification was octyne-sensitive (68–90%). The octyne-sensitive activity—presumably AOB—was affected more by soil pH whereas the octyne-resistant (AOA) activity was more strongly related to N availability.  相似文献   
2.
Nitrification plays a central role in global nitrogen cycle, which is affected by biological interaction between soil microfauna and microorganisms. However, the complexity of soil biotic communities made it difficult to reveal organizational principles of the community and the interactions among species. Here, we used the network analysis to decipher the interactions between nematodes and ammonia oxidizers within aggregate fractions under 10-year manure application, and examine their associations with soil variables and potential nitrification activity (PNA). Three aggregate fractions included large macroaggregates (>2000 μm, LA), small macroaggregates (250–2000 μm, SA), and inter-aggregate soil and space (<250 μm, IA). Aggregate factions showed a remarkable effect on association networks of nematodes and ammonia oxidizers. The average connectivity (avgK) and the number of edges in overall networks increased with increasing aggregate sizes, while the average geodesic distance (GD) followed the opposite trend. The LA network could be viewed as a better organized or a better operational soil food web with more functional interrelated members than the SA and IA networks. The modules related to PNA were significantly correlated and clustered together as meta-modules in networks of aggregate fractions. The role-shifts prevailed among the network members such as significant module memberships (MMs) and generalist/specialist operational taxonomic units (OTUs). A half of shared nodes were further identified as shared MMs, dominated by ammonia-oxidizing bacteria (AOB) especially for Nitrosospira cluster 3a and 10. Soil pH could explain partly the shift of module hubs in different networks, while grazing by bacterivores might account for three exclusively connecters related to Nitrososphaera clusters 1.1. The strongly coupled modules correlated positively to pH and total carbon (TC), regardless of aggregate fractions. The network analysis approach provided new insights into potential importance of network interactions between nematodes and ammonia oxidizers in soil nitrogen cycling.  相似文献   
3.
The environmental impact of crop production is mainly related to fossil fuels consumption and to fertilisers application. Emissions arising from the spreading of organic and mineral fertilisers are important contributors for impact categories such as eutrophication and acidification. The choice of the fertilisers and of the spreading techniques as well as the crop residues management can deeply affect the environmental impact related to crop cultivation.In this study, seven scenarios describing fertilising schemes characterised by different organic and mineral fertilisers and by different mechanisation were compared. The aim is to evaluate, using the Life Cycle Assessment (LCA) method, how the environmental performances of grain maize production were affected by these different fertilisers schemes. The study was carried out considering a cradle to farm gate perspective and 1 t grain maize was selected as functional unit. Inventory data were collected on a farm located in Po Valley (Northern Italy) during year 2013 and were processed using the composite method recommended by the International Reference Life Cycle Data System (ILCD). The compared scenarios involved organic and mineral fertiliser distribution and were: pig slurry incorporation after >3 days after spreading (BS), fast pig slurry incorporation within 2 h from spreading (AS1), direct soil injection of pig slurry (AS2), pig slurry incorporation (after >3 days) with straw collection (AS3), digestate spreading instead of pig slurry (after >3 days) (AS4), only mineral fertilisers (i.e. urea and superphosphate) distribution (AS5) and only mineral fertilisers (i.e. calcium ammonium nitrate and superphosphate) distribution (AS6).The results were not univocal, since climate and soil conditions as well as physical and chemical fertiliser characteristics differently affected the environmental load, especially for particulate matter formation, terrestrial acidification and terrestrial eutrophication impact categories. AS1 and AS2 showed the most beneficial results for these impact categories (between ↙67% and ↙73% respect to worst scenario). AS6, on the opposite, showed the highest environmental impact for those impact categories mainly affected by energy and fossil fuel consumption (climate change, ozone depletion, human toxicity with carcinogenic effect, particulate matter, freshwater eutrophication, freshwater ecotoxicity and mineral, fossil and renewable resources depletion), categories on which AS3 and AS4 were the best solutions. AS3 was the most impacting for terrestrial acidification and eutrophicationA sensitivity analysis was carried out varying grain maize yield (mostly affected: marine eutrophication) and ammonia volatilisation losses due to organic fertilisers (mainly affected: terrestrial acidification and eutrophication).The achieved results can be useful for the development of ⬓spreading rules⬽ that drive the application of organic fertilisers in agricultural areas where there is an intense livestock activity.  相似文献   
4.
综述了植物氨同化以及烟草中苯丙氨酸代谢、脯氨酸代谢、美拉德反应及其与烟叶风味和品质关系的研究进展,并分析了环境因素对烟草氨基酸代谢的影响,为深入研究氨基酸对烟叶品质和风味影响的机制奠定了基础。  相似文献   
5.
氨氧化过程对氧化亚氮(N2O)排放具有重要贡献。在不同土壤类型和农田管理下,氨氧化微生物类群对N2O排放的相对贡献组成规律还缺乏系统的研究。本研究选取典型农田耕层土壤(潮土、黑土、砖红壤),以及有机肥改良的砖红壤剖面土壤,采用选择性抑制法(乙炔和辛炔)研究氨氧化细菌(AOB)、氨氧化古菌和全程硝化菌(AOA+comammox)以及异养硝化菌对土壤硝化潜势、净硝化速率及N2O排放的相对贡献。结果表明,在耕层土壤中,潮土、黑土和砖红壤的pH分别是8.0、6.7和5.7,硝化潜势分别是N 32.5、6.6和4.8 mg?kg-1?d-1,净硝化速率分别是N 7.1、3.0和0.5 mg?kg-1?d-1,7天N2O累积排放量分别是N 38.0、35.4和8.7 μg?kg-1。AOB主导耕层土壤的硝化潜势,对硝化潜势的贡献分别是82%、58%和100%。对于净硝化速率,在潮土和砖红壤中,AOB和AOA+comammox贡献相当(均在30%~40%),而黑土中由AOB主导(72%)。AOB主导耕层土壤的N2O排放,对N2O排放的贡献分别是72%、92%和58%。在改良的砖红壤剖面土壤中,在0~20 cm、20~40 cm和40~60 cm,pH分别是7.0、5.5和4.9,硝化潜势分别是N 6.6、2.0和1.1 mg?kg-1?d-1,净硝化速率分别是N 4.1、0.9和0.2 mg?kg-1?d-1,N2O排放分别是N 16.3、6.5和2.8 mg?kg-1?d-1。随土壤由深层至表层,硝化潜势、净硝化速率及N2O排放显著提高。AOA+comammox主导表层硝化潜势及净硝化速率的提高(分别贡献63%和54%),AOB主导N2O排放的增加(贡献54%)。本研究为制定与土壤氨氧化特性及土壤性质相匹配的N2O减排措施提供了新的科学依据。  相似文献   
6.
C/N比对好氧堆肥中NH3挥发损失和含氮有机物转化的影响   总被引:3,自引:0,他引:3  
利用牛粪和不同比例玉米秸秆的混合,设置5个不同C/N比处理(T1=15、T2=20、T3=25、T4=30、T5=35),研究其对条垛式好氧堆肥过程中的NH_3挥发损失和含氮有机物转化的影响。结果表明:在肥堆前24 d有11.1%~23.1%的总氮损失,堆体C/N比越低,总氮损失率越高。堆肥结束时,T1~T5处理的总氮损失率为10.1%~24.1%,其中由NH_3挥发造成的氮损失占总氮损失的30.9%~40.5%。堆肥过程的NH_3挥发主要发生在升温期和高温期,此期的NH_3挥发量占总挥发量的95%以上,是总氮损失的主要途径。堆肥前6 d各处理堆体铵态氮积累并达到最高值,导致pH值迅速升高,是造成堆肥NH_3挥发的直接原因。堆体C/N比越低,pH值越高,NH_3挥发量越大,由此造成的氮损失占总氮损失的比例越大。堆肥材料总氮的90%以上为有机氮,其降解主要发生在堆肥前24 d,堆体初始C/N比越低,有机氮矿化越快。不同有机氮组分的降解速率不同,以氨基酸态氮和酰胺态氮的降解为主。当堆体初始C/N比低于25时,堆肥材料中氨基酸态氮和酰胺态氮等有机态氮快速降解产生大量的铵态氮,由此导致堆体pH值的迅速升高,是导致堆肥过程中大量NH_3挥发和氮素损失的主要原因。  相似文献   
7.
辽河平原玉米田不同施肥下的土壤氨挥发特征   总被引:1,自引:0,他引:1  
【目的】通过不同施肥措施对氨气排放贡献的研究,获得辽河平原化肥施用本地化的氨排放因子,为大气环境和生态等领域的相关研究提供参考借鉴。【方法】于2018年5—10月在沈阳农业大学试验基地开展不同施肥措施下的氨气排放的大田试验,以基肥施树脂包衣缓释化肥、拔节期追施尿素为常规施肥方式,设置无氮处理(T0)、常规施肥减半(T1)、常规施肥+生物炭(T2)、常规施肥一次性施入(T3)、常规施肥(T4)5个处理。采用通气法在玉米全生育期内定时收集氨气,利用流动分析仪检测计算氨排放通量,同时测定土壤铵态氮含量。【结果】施基肥后氨挥发速率呈现双峰趋势,各处理分别于施基肥后第1—2天或第5—7天达到氨挥发速率最大值,施基肥后各处理氨挥发速率最大值表现为:常规施肥减半(T1)>常规施肥+生物炭(T2)>常规施肥一次性施入(T3)>常规施肥(T4)>无氮处理(T0);施追肥后各处理均于第1—2天达到氨挥发速率最大值,追肥后各处理氨挥发速率最大值表现为:常规施肥(T4)>常规施肥+生物炭(T2)>常规施肥减半(T1)>常规施肥一次性施入(T3)>无氮处理(T0)。氨挥发损失累积量表现为常规施肥+生物炭(T2)>常规施肥(T4)>常规施肥一次性施入(T3)>常规施肥减半(T1)>无氮处理(T0)。各时期各处理间的土壤铵态氮含量差异并不显著,但土壤铵态氮含量和同时期土壤氨挥发速率呈现出相似的变化趋势,施追肥后两者的变化趋势比施基肥后更加相似。由于T1、T2、T4追肥期施尿素,尿素释放铵态氮比缓释化肥更加迅速,同时氨挥发也相对较快。整体来看,减少50%施氮量,氨挥发损失累积量只减少20%。各处理间生长季内氨挥发损失累积量差异显著,常规施肥+生物炭(T2)的氨挥发损失累积量最多,在施氮量相同的情况下,加施生物炭氨挥发损失累积量增加22%。全生长季施氮量相同的情况下,一次性施入缓释化肥而不采取尿素追肥的措施比以尿素作为追肥的措施的氨挥发累积量减少12%。【结论】氨挥发随着施氮量增加呈现边际递减效应。生物炭促进了农田氨挥发,玉米秸秆生物炭呈碱性,导致了氨挥发累积量的增加,但其具有孔隙度和比表面积大、吸附效果强的特点,可改良土壤和减少其他温室气体。一次性施入缓释化肥而不采取尿素追肥显著降低了氨挥发。  相似文献   
8.
为研究减少在番茄茎秆好氧堆肥过程中氮素损失的途径,提高堆肥品质,以粉碎的番茄茎秆为原料,按物料干重分别加入5%的腐殖酸(T1)、氯化钙(T2)和过磷酸钙(T3),同时以不进行任何添加的堆体作为对照(CK),进行45 d的好氧堆肥试验。结果表明:3种添加剂均可降低堆肥过程中的氮素损失,同时减少了NH3的挥发量;堆肥结束时,CK、T1、T2和T3处理的氮素损失率分别为18.04%、15.00%、12.65%和14.05%,累计NH3挥发量为CK(1 648.11 mg/kg)>T1(1 330.35 mg/kg)>T3(995.35 mg/kg)>T2(528.11 mg/kg)。其中,添加氯化钙的处理保氮效果最好,与对照相比,氮素损失率低至12.65%,NH3挥发量减少67.96%;各处理高温期均≥3 d,发芽指数≥80%,表明堆体已经腐熟,无植物毒性。综上,番茄茎秆好氧堆肥中添加氯化钙,对于减少堆肥过程中的氮素损失较为理想。本研究可为番茄茎秆好氧堆肥保氮工艺优化提供理论依据。  相似文献   
9.
In previous proof-of-concept work, it was shown that the use of treated coal mine water for rainbow trout (Oncorhynchus mykiss) culture in a cage was technically feasible, though only a 50-fish bioassay was grown and no work on production-related issues was conducted. To further advance the use of treated mine water, an under-utilized water resource throughout Mid Appalachia, work was conducted to assess the effects of using treated coal mine water for the intensive production of rainbow trout in a flow-through system. During this study, comprehensive water quality data were collected to supplement fish weight and length data taken during routine monthly sampling events. The 8000 fish grew well in the raceway system over the 9 months of production, where a feed conversion ratio of 1.4 and a condition factor of 5.1 × 10−4 were measured with stocking and harvest densities of 26.4 and 50.2 kg/m3, respectively. Further, total net production was 3275 kg (7220 lb) with 98.6% survival. Throughout the study, dissolved ion concentrations (Fe, Al, Mg, Ca, and SO4) often exceeded recommended tolerance limits. Further, elevated ammonia nitrogen concentrations generated from a component of the mine water-treatment process were identified as a potential limiting factor for aquaculture development. However, when the non-ideal effects of high ionic strength and the speciation of dissolved metal–ligand complexes were taken into account, the concentrations of free metal ions were within recommended tolerance limits.  相似文献   
10.
Total ammonia nitrogen (TAN) concentration is often a key limiting water quality parameter in intensive aquaculture systems. Removing ammonia through biological filtration is thus the first objective in recirculating aquaculture system design. In this study, the performance characteristics of a steady-state nitrification biofilm were explored using a series of reactors. Four nitrification kinetics parameters were estimated using the data collected from the experimental system, including minimum TAN concentration, half saturation constant, maximum TAN removal rate and maximum specific bacterial growth rate. Experimental data showed that a minimum TAN concentration was needed to support a steady-state nitrification biofilm. For the temperature of 27.2°C, the mean minimum TAN concentration was 0.07 mg/l. For a single substrate-limiting factor, the relationship between TAN removal rate (R) and TAN concentration (S) was represented by an empirical equation [R=1859(S−0.07)/(S+1.93)]. The characteristics of nitrite oxidation were also demonstrated by the experiment system. The results of this study will help to better understand the characteristics of nitrification biofilters applied in recirculating aquaculture systems.  相似文献   
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