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1.
青藏公路沿线土壤微生物数量变化及其影响因素研究   总被引:4,自引:3,他引:1  
以青藏公路沿线土壤为研究对象, 研究了土壤可培养微生物数量的变化特征及影响因子. 结果表明: 青藏公路沿线土壤可培养微生物数量为0.77×106~2.44×107CFU·g-1dw; 沿青藏公路从南(申格里贡山)到北(西大滩), 土壤可培养细菌与真菌数量表现为先迅速减少, 然后渐趋平缓; 可培养放线菌数量先减少后增加; 土壤总氮、 有机碳和含水量逐渐降低, 而pH值逐渐升高. C/N比率与真菌/细菌比率变化趋势相似, 均为先增加后减少. 土壤可培养微生物数量与理化因子的相关性分析结果表明: 青藏公路沿线土壤微生物数量主要受纬度和土壤理化性质的影响, 表现为微生物数量与纬度和pH值显著负相关, 而与总氮、 有机碳和含水量极显著正相关.  相似文献   

2.
以疏勒河上游不同海拔芨芨草根际土壤样品为研究对象,研究了不同海拔土样中细菌分布特征及其影响因素. 结果表明:研究区域芨芨草根际土壤可培养细菌种群密度变化范围为1.7×107~10.8×107 CFU·g-1,平均值为6.4×107 CFU·g-1,随海拔的升高呈先下降后上升的趋势;可培养细菌数量与土壤全氮、脲酶、蔗糖酶含量呈极显著正相关关系,与有机碳、磷酸酶含量呈显著正相关关系;同时,pH值也是影响细菌数量与多样性的一个重要因素. 通过16S rDNA基因测序及构建系统发育树,研究区域可培养细菌归类为15个属,其中芽孢杆菌属和假单胞菌属为优势菌属.  相似文献   

3.
以青藏高原腹地不同植被类型多年冻土区土壤细菌为研究对象, 分析了可培养菌群数量、 多样性和生理代谢功能的变化及其与环境因子间的关系. 结果显示: 从沼泽草甸到高寒荒漠, 土壤水分、 总碳、 总氮含量逐渐降低, pH值升高, 可培养细菌数量在2.97×106~2.88×107 CFU·g-1, 与含水量、 总碳、 总氮显著正相关; Actinobacteria(51.4%)和γ-Proteobacteria(31.7%)为优势菌群, α-protebacteria仅在沼泽草甸中有分布, β-protebacteria、 Bacterioidetes丰度与含水量、 总碳、 总氮间显著正相关; 自沼泽到荒漠, 菌群代谢活性和Shannon功能多样性指数降低, pH与Shannon指数显著负相关, 继氨基酸类碳源之后, 多聚物逐渐成为被细菌群落主要利用的碳源种类. 研究表明, 伴随冻土退化地上植被逆向演替的过程, 青藏高原多年冻土地下土壤微生物群落丰度、 遗传和代谢功能多样性均发生了不同程度的响应.  相似文献   

4.
以山东昌邑国家级海洋生态特别保护区内柽柳林下土壤微生物为研究对象, 测定了其微生物量变化. 结果表明: 研究区细菌、真菌及古菌基因平均拷贝数分别为8.24×106 copies·g-1、1.51×104 copies·g-1和2.85×104 copies·g-1, 微生物量碳、氮平均值分别为140.54 mg·kg-1和29.19 mg·kg-1. 自密集区经稀疏区到边缘区, 随植被盖度的降低, 微生物量呈现降低的趋势. 相关分析表明, 不同植被盖度所造成的有机质输入的差异是造成这种变化规律的主要因素.  相似文献   

5.
基于辽河流域多目标地球化学调查取得的土壤表层和深层有机碳和全碳数据,探讨辽河流域土壤碳储量计算方法,分析辽河流域碳密度的分布特征.对辽河流域5.23×104 km2土壤碳储量计算表明,深层(0~1.8 m)土壤碳储量为860.50×106 t,中层(0~1.0 m)为538.30×106 t,表层(0~0.2 m)为138.76×106 t;辽河流域土壤深层碳密度为16.45×103 t/km2,中层为10.28×103 t/km2,表层为2.65×103 t/km2.分别根据土壤类型、地质单元、生态系统和土地利用类型的划分方式计算土壤的碳储量,为土壤碳循环研究与环境效应评价提供了科学依据.  相似文献   

6.
对青藏高原海北站区的自然土壤和扰动土壤进行高分辨率采样,测定土壤根系、有机碳及其14C含量;用14C示踪技术探讨土地利用变化对高寒草甸土壤有机质更新的影响.研究表明,土地利用变化对高寒草甸土壤碳循环影响显著.耕作活动导致扰动土壤有机碳储量比自然土壤增加29.35%;扰动土壤剖面10~50 cm深土壤有机质的14C含量相对富集;自然土壤大多数有机碳储存在土壤表层,更新时间<50 a,同一深度扰动土壤有机碳储量显著少,更新时间长(171~294 a);自然土壤10 cm以下有机碳主要为更新时间>1 000 a的稳定碳所控制,扰动土壤的相应值出现在40 cm以下;自然土壤有机质更新产生的CO2通量为114 gC·m-2·a-1,扰动土壤为48.7 gC·m-2·a-1.  相似文献   

7.
青藏高原草地土壤有机碳库及其全球意义   总被引:55,自引:5,他引:50  
定量分析了青藏高原各类草地0~0.65m深度范围内有机碳储量,结果表明:青藏高原总面积为1.6027×10hm2的草地有机碳量达到335.1973×108tC,其中以高原草甸土和高原草原土有机碳积累量为主,两者之和达到232.36×108tC,占全国土壤有机碳量的23.44%,是全球土壤碳库的2.4%.在有机碳储量分析的基础上,按土壤碳释放的两种主要途径:土壤呼吸作用和土地利用方式变化与草地退化,对草地土壤碳排放进行了估算,揭示出青藏高原草地土壤通过呼吸每年排放的CO2达到11.7×108tC·a-1,约占中国土壤呼吸总量的2.3%,明显高于全国乃至全球平均值;近30a来,青藏高原草地土壤由于土地利用变化和草地退化所释放的CO2估计约有30.23×108tC.保护青藏高原草地对于全球变化意义重大.定量分析了青藏高原各类草地0~0.65m深度范围内有机碳储量,结果表明:青藏高原总面积为1.6027×10hm2的草地有机碳量达到335.1973×108tC,其中以高原草甸土和高原草原土有机碳积累量为主,两者之和达到232.36×108tC,占全国土壤有机碳量的23.44%,是全球土壤碳库的2.4%.在有机碳储量分析的基础上,按土壤碳释放的两种主要途径:土壤呼吸作用和土地利用方式变化与草地退化,对草地土壤碳排放进行了估算,揭示出青藏高原草地土壤通过呼吸每年排放的CO2达到11.7×108tC·a-1,约占中国土壤呼吸总量的2.3%,明显高于全国乃至全球平均值;近30a来,青藏高原草地土壤由于土地利用变化和草地退化所释放的CO2估计约有30.23×108tC.保护青藏高原草地对于全球变化意义重大.  相似文献   

8.
封育是推广范围最广的草地恢复措施之一. 为研究不同封育年限高寒草甸植被、土壤碳密度变化, 对1 a、6 a和16 a不同封育年限样地监测结果进行分析.结果表明: 不同封育年限高寒草甸植被现存碳密度表现出封育16 a>封育1 a>封育6 a, 分别为1 522.57 gC·m-2、1 323.12 gC·m-2和1 148.17 gC·m-2, 但不同封育年限之间植被现存碳密度差异不显著(P>0.05). 土壤碳密度垂直分布明显, 0~5 cm和5~10 cm土层有机碳密度较高, 随土层深度增加土壤有机碳密度明显下降, 土壤容重上升;不同封育年限之间0~40 cm层次土壤碳密度和土壤容重差异性均不显著, 但仍可表现出土壤碳密度封育1 a>封育6 a>封育16 a, 分别为28 636.32 gC·m-2、26 570.92 gC·m-2和26 060.71 gC·m-2;同时, 土壤容重随封育时间延长而下降. 对7月下旬到10月上旬净生态系统CO2交换率(NEE)监测来看, 封育1 a植被土壤碳吸收速率显著高于封育16 a(P<0.05);而排放率与封育16 a样地接近, 差异不显著(P>0.05).  相似文献   

9.
对祁连山高寒草原碱性土壤可培养固氮菌数量、 固氮基因(nifH)群落结构及其理化性质进行了研究. 结果表明: 固氮菌数量在土层0~40 cm处于3.6×105~0.21×105CFUs·g-1之间, 除了海拔3 001 m的土样AQ4外, 其他3个土样固氮菌数量随着土壤深度的加深而减小. 固氮菌数量与地下生物量呈显著正相关性, 与有机碳、 可溶有机氮、 速效磷和速效钾呈正相关性, 而与pH值和全盐呈负相关性. 通过基因测序得到的37个固氮基因nifH克隆中, 蓝藻门占41%, 变形菌门占8%, 厚壁菌门占14%, 未知菌株占37%; 蓝藻门在除了AQ4外的土样中普遍存在, 并且是AQ1的优势固氮菌群. 此外, 还发现了4个新的nifH基因, 分别是AQ1-12(KC412109)、 AQ4-3(KC412133)、 AQ4-4(KC412133)、 AQ4-5(KC412133), 其中后三者是土样AQ4的优势种群.  相似文献   

10.
高寒草甸是青藏高原面积最大的草地类型, 对全球生态环境的影响十分巨大。然而在外界干扰下, 使得本身就很脆弱的高寒草甸发生了不同程度的退化。为探究翻耕补播对土壤微生物的影响, 以疏勒河上游不同季节(4月、 6月、 9月)原生高寒草甸、 退化草甸和翻耕补播草甸土壤为对象, 研究了土壤可培养细菌数量的季节变化及其影响因素。结果表明: 研究区域可培养细菌数量介于4.3×106 ~ 4.5×107 CFU·g-1之间, 不同季节退化草甸与翻耕补播草甸土壤细菌数量均显著低于原生高寒草甸, 且不同类型高寒草甸生态系统下可培养细菌具有明显的季节差异: 原生高寒草甸生态系统下土壤细菌在6月生物量最高, 4月最低; 而退化草甸与翻耕补播草甸土壤细菌生物量并没有表现出明显的季节波动; 相关分析表明, 可培养细菌数量与土壤全氮、 植被盖度及土壤含水量存在极显著正相关关系。研究发现, 翻耕补播措施并没有恢复该区域微生物数量, 研究结果对于认识高寒草甸生态系统的退化成因, 判断恢复措施的有效性和合理性具有重要意义。  相似文献   

11.
杭州市土壤铅污染的铅同位素示踪研究   总被引:27,自引:0,他引:27       下载免费PDF全文
根据杭州市40个土壤全铅和38个可溶相铅的统计分析,土壤中全铅平均含量为49.6×10-6,可溶相铅平均为21.4×10-6,城区表土的全铅高达76.1×10-6,显著高于全国土壤平均值。分析结果还显示,从农村→远郊→近郊→公路旁,土壤可溶相铅含量逐渐增加,且土壤的可溶相铅含量与深度具明显的负相关关系。表明杭州市土壤受到了不同程度的铅污染,污染程度由农村→远郊→近郊→公路旁→城区有明显的增高趋势。通过对茶园土壤中可溶相铅、残渣态铅及城区表土全铅的同位素组成对比分析发现,从土壤残渣态(代表土壤背景)→土壤可溶相→城区表层土壤全铅206Pb/207Pb比值有明显的降低。208Pb/(206Pb+207Pb)也有类似的变化趋势。将土壤与杭州市的汽车尾气、大气等环境样品进行对比发现,随着土壤受污染程度的增加,铅同位素组成逐渐向汽车尾气铅漂移,表明汽车尾气排放的铅为其主要污染源。  相似文献   

12.
利用PYGV、 R2A、 NB和Czapek 4种培养基, 研究了不同海拔下黑河上游祁连山区土壤细菌群落结构的变化规律.结果表明: 可培养细菌数量为4.6×106~37.0×106CFU·g-1, 随海拔升高明显减少; 基于16S rRNA基因序列分析共发现了7个门、 19个属、 26种细菌, 其中Agreia pratensis, Mucilaginibacter ximonensis, 嗜冷冷杆菌(Cryobacterium psychrophilum)和氧化节杆菌(Arthrobacter oxydans)四种细菌是优势种; 嗜冷冷杆菌的相对丰度在高海拔地区明显增加, Agreia pratensis的相对丰度随海拔升高而降低; 细菌的多样性随海拔升高呈现出先升高后降低的趋势. 冗余分析(RDA)显示, 可培养细菌数量与海拔呈显著负相关, 细菌的多样性与植被指数和土壤理化性质均存在明显的相关关系, 说明可培养细菌数量主要受海拔的影响, 而植被和土壤理化性质是影响细菌群落多样性的主要因素.  相似文献   

13.
Bacterial abundance and production, numbers, sizes and concentrations of transparent exopolymer particles (TEP) and total organic carbon (TOC) were measured during the 1996 summer monsoon to understand the relationship between TEP, the most labile particulate organic carbon, and bacteria. While high regional variability in the vertical distribution of TOC was discernible, TEP concentrations were high in surface waters at 18–20°N along 64°E with concentrations well over 25 mg alginic acid equivalents I−1 due to upwelling induced productivity. Their concentrations decreased with depth and were lower between 200 and 500 m. Bacterial concentrations were up to 1.99 × 108 I–1 in the surface waters and decreased by an order of magnitude or more at depths below 500 m. A better relationship has been found between bacterial abundance and concentrations of TEP than between bacteria and TOC, indicating that bacterial metabolism is fueled by availability of TEP in the Arabian Sea. Assuming a carbon assimilation of 33%, bacterial carbon demand (BCD) is estimated to be 1.017 to 4.035 g C m–2 d–1 in the surface waters. The observed TEP concentrations appear to be sufficient in meeting the surface and subsurface BCD in the northern Arabian Sea.  相似文献   

14.
This investigation represented the preliminary study to characterize Pt and Pd concentrations and enrichment ratios in urban roadside soils. Roadside soil samples were analyzed by ICP-MS. Data from 21 roadside topsoil samples show medians of Pt and Pd concentrations are 2.9 and 2.8 ng g−1, respectively. These values are higher than those of upper crust that average 0.4 and 0.4 ng g−1, respectively. The relatively lower Pt and Pd concentrations are expected due to recent introduction of catalysts to China compared to the prolonged use of catalysts in Europe. Hierarchical clustering analysis indicates that Pt and Pd in Xuzhou urban roadside soils were mainly from the traffic emissions. Computation of enrichment ratios using the upper crust values as background levels suggests that the roadside soils had enrichment medians of 6.4 for Pt (range 2.5–11.75) and of 6.75 for Pd (range 2.75–9.25). Lower Pt/Pd ratios (range 0.35–2.86) in relation to similar studies in other countries were observed due to the different automobile catalytic converters. In general, fine fraction (<250 μm) contains higher Pt and Pd concentrations compared to the coarse fraction (250–500 μm).  相似文献   

15.
The present study fills a gap in the knowledge in regards to the occurrence of banned pesticides at both coastal and inland locations at the Southwest Buenos Aires region, Argentina. Superficial sediment and soil samples were collected from different sites along the Bahia Blanca Estuary and surrounding sites to assess the concentration levels and spatial distribution of 12 selected organochlorine pesticides (OCs); 13 spatial locations including inland and shore-coast were sampled to evaluate occurrence and concentration levels of hexachlorocyclohexanes α-HCH, β-HCH, δ-HCH, γ-HCH, dichlorodiphenyltrichloroethane and its degradation products (DDXs: p,p′-DDT, o,p′-DDT, p,p′-DDE, o,p′-DDE, p,p′-DDD, o,p′-DDD) and the polychlorobenzenes PeCB (pentachlorobenzene) and HCB (hexachlorobenzene). After cleaning and extractions steps, samples were analyzed by means of gas chromatography/mass spectrometry. ∑OCs (sum of all studied compounds) ranged between 0.206 and 1040 ng g?1 dw (mean?=?82.4 and SD?=?277 ng g?1 dw). Total HCHs (sum of α-HCH, β-HCH, γ-HCH and δ-HCH) ranged from 0.0858 to 0.876 ng g?1 dw (mean?=?0.43 and SD?=?0.23 ng g?1 dw), DDXs (sum of p,p′and o,p′ isomers) from 0.080 to 1040 ng g?1 dw (mean?=?81.3 and SD?=?277 ng g?1 dw). Lower concentrations were found for PeCB (mean?=?0.095 and SD 0.17 ng g?1 dw) and HCB (mean?=?0.56 and SD 1.7 ng g?1 dw). Principal component analysis (PCA) permitted the extraction of underlying information about common factors, providing an overview of the distribution of pesticides and allowing the characterization of sites in regards to the major pesticide signature.  相似文献   

16.
High concentrations of ammonium nitrogen released from tannery sludge during storage in open air may cause nitrogen pollution to soil and groundwater. To study the transformation mechanism of NH4+-N by nitrifying functional bacteria in tannery sludge contaminated soils, a series of contaminated soil culture experiments were conducted in this study. The contents of ammonium nitrogen (as NH4+-N), nitrite nitrogen (as NO2?-N) and nitrate nitrogen (as NO3?-N) were analyzed during the culture period under different conditions of pollution load, soil particle and redox environment. Sigmodial equation was used to interpret the change of NO3?-N with time in contaminated soils. The abundance variations of nitrifying functional genes (amoA and nxrA) were also detected using the real-time quantitative fluorescence PCR method. The results show that the nitrification of NH4+-N was aggravated in the contaminated silt soil and fine sand under the condition of lower pollution load, finer particle size and more oxidizing environment. The sigmodial equation well fitted the dynamic accumulation curve of the NO3?-N content in the tannery sludge contaminated soils. The Cr(III) content increased with increasing pollution load, which inhibited the reproduction and activity of nitrifying bacteria in the soils, especially in coarse-grained soil. The accumulation of NO2?-N contents became more obvious with the increase of pollution load in the fine sand, and only 41.5% of the NH4+-N was transformed to NO3?-N. The redox environment was the main factor affecting nitrification process in the soil. Compared to the aerobic soil environment, the transformation of NH4+-N was significantly inhibited under anaerobic incubation condition, and the NO3?-N contents decreased by 37.2%, 61.9% and 91.9% under low, medium and high pollution loads, respectively. Nitrification was stronger in the silt soil since its copy number of amoA and nxrA genes was two times larger than that of fine sand. Moreover, the copy numbers of amoA and nxrA genes in the silt soil under the aerobic environment were 2.7 times and 2.2 times larger than those in the anaerobic environment. The abundance changes of the amoA and nxrA functional genes have a positive correlation with the nitrification intensity in the tannery sludge-contaminated soil.  相似文献   

17.
The aim of this interdisciplinary study is to examine a component of the hydrological cycle in Galapagos by characterizing soil properties. Nine soil profiles were sampled on two islands. Their physical and hydrodynamic properties were analyzed, along with their mineralogical composition. Two groups of soils were identified, with major differences between them. The first group consists of soils located in the highlands (>350 m a.s.l.), characterized by low hydraulic conductivity (<10−5 m s−1) and low porosity (<25%). These soils are thick (several meters) and homogeneous without coarse components. Their clay fraction is considerable and dominated by gibbsite. The second group includes soils located in the low parts of the islands (<300 m a.s.l.). These soils are characterized by high hydraulic conductivity (>10−3 m s−1) and high porosity (>35%). The structure of these soils is heterogeneous and includes coarse materials. The physical properties of the soils are in good agreement with the variations of the rainfall according to the elevation, which appears as the main factor controlling the soil development. The clayey alteration products constrain soils physical and hydrodynamic properties by reducing the porosity and consequently the permeability and also by increasing water retention.  相似文献   

18.
《China Geology》2021,4(3):463-475
Ammonia-oxidizing archaea (AOA), ammonia-oxidizing bacteria (AOB), and anaerobic ammoniaoxidation (anammox) bacteria are very important contributors to nitrogen cycling in natural environments. Functional gene abundances of these microbes were believed to be well relevant to N-cycling in groundwater systems, especially in the Pearl River Delta (PRD) groundwater with unique high intrinsic ammonia concentrations. In this research, 20 sediment samples from two in the PRD were collected for porewater chemistry analysis and quantification of N-cycling related genes, including archaeal and bacterial amoA gene and anammox 16S ribosomal Ribonucleic Acid (rRNA) gene. Quantitative Polymerase Chain Reaction (qPCR) results showed that gene abundances of AOA, AOB, and anammox bacteria ranged from 3.13×105 to 3.21×107, 1.83×104 to 2.74×106, and 9.27×104 to 8.96×106 copies/g in the sediment of the groundwater system, respectively. Anammox bacteria and AOA dominated in aquitards and aquifers, respectively, meanwhile, the aquitard-aquifer interfaces were demonstrated as ammonium-oxidizing hotspots in the aspect of gene numbers. Gene abundances of nitrifiers were analyzed with geochemistry profiles. Correlations between gene numbers and environmental variables indicated that the gene abundances were impacted by hydrogeological conditions, and microbial-derived ammonium loss was dominated by AOA in the northwest PRD and by anammox bacteria in the southeast PRD.© 2021 China Geology Editorial Office.  相似文献   

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