黄顶菊（Flaveriabidentis）入侵对土壤微生物功能多样性的影响

外来植物入侵对土壤生物多样性的影响已成为生态学领域的研究热点之一。运用Biolog技术和氯仿熏蒸浸提法研究了黄顶菊入侵对土壤微生物群落功能多样性及土壤微生物量的影响。结果表明,黄顶菊入侵后土壤微生物代谢活性显著升高;土壤微生物群落平均吸光值（4WCD）的变化趋势为：入侵地根际土（RPs）〉入侵地根围土（Bs）〉未入侵地（CK）,且差异显著;而CK的功能多样性指数（日）高于BS,RPS亦高于Bs,差异均显著（P〈O．05）。主成分分析结果表明,黄顶菊入侵使土壤微生物群落的碳源利用方式和代谢功能发生改变。对不同碳源利用的分析结果表明,糖类、氨基酸类、羧酸类和聚合物为土壤微生物利用的主要碳源。入侵样地Bs和RPS的微生物量碳分别比CK高27．05％、121．52％;BS和RPS的微生物量氮分别比CK高37．40％、79．80％。相关性分析表明,AWCD与微生物量碳和微生物量氮均呈极显著正相关（P〈0．01）。由此可知,黄顶菊入侵增强了入侵地土壤微生物代谢活性,降低了土壤微生物群落的功能多样性,增加了土壤微生物量碳、氮水平。     

塔什库尔干县土壤可培养细菌多样性及其胞外酶检测

对新疆塔什库尔干县土壤中可培养细菌多样性进行分析，以期初步阐明该地区土壤可培养细菌群落结构。采用5种琼脂培养基分离纯化可培养细菌，依据其16S rRNA基因序列进行系统发育分析，并运用平板法对纯化菌株的胞外酶产生情况进行检测。序列分析结果表明，33株细菌分别属于放线菌门（96.97%）和厚壁菌门（3.03%）等2个大的系统发育类群，5个属14个种。其中节杆菌属（48.48%）和假节杆菌属（24.24%）为优势菌属。培养基优势度指数结果显示，高氏1号培养基的优势度指数最高，菌株分离效果最好。分离菌株产胞外酶结果显示，33株细菌中含有至少1种胞外酶活性的菌株共19株（57.58%）。总体上，塔什库尔干县土壤中可培养细菌多样性较单一，细菌产单一种类胞外酶活性比例较高，分离菌株可为塔什库尔干县微生物资源的开发和利用提供前期基础。     

豫北地区城乡结合部庭院绿化模式及物种多样性研究

城乡结合部庭院绿化对改善城市生态环境具有重要作用。以豫北城乡结合部为例,通过调查庭院绿化植物群落、种类数目,运用Margalef丰富度指数(R)、香农—威纳多样性指数(Shannon-Weiner index)(H)和Pielou均匀度指数(E)综合评价庭院植物的物种多样性。结果显示,研究区域庭院绿化以单一草本(46.2%)和灌—草复合型配置模式为主(30.4%),其多样性指数表现为灌—草复合型单一灌木型单一草本型乔—草复合型乔—灌复合型单一乔木型乔—灌—草复合型。村庄的植被物种多样性表现为:杨庄南李万史平陵村钦平陵村仇化庄,可见村庄植被物种多样性总体上与其到城市中心区距离呈逆相关,距离越远,城市化水平越低,物种多样性越高。     

活性污泥生物杀虫剂及生物肥料

生物杀虫剂单独使用活性污泥或混加具有杀虫性能的天然植物粉末作培养基 ,培养制备细菌粉末 ,或悬浮剂再加入适当的展着剂、分散剂和防腐剂而成 ,可同步或单独用同样方法培养有机磷细菌、无机磷细菌及钾细菌、固氮菌等一种或几种细菌而制成生物肥料 ,即菌肥。 (ＣＮ 12 2 0 82     

木贼定居对铅锌尾矿砂微生物多样性及重金属迁移转化的影响

为研究根际微生物影响木贼耐受和吸附重金属的机制,为重金属污染植物-微生物协同修复提供参考,应用化学分析方法和Illumina MiSeq高通量测序技术,对木贼定居对铅锌尾矿重金属含量、土壤微生物多样性的影响进行研究。结果表明,子囊菌、未明确分类真菌和担子菌是铅锌尾矿地土壤的优势真菌。木贼定居导致散囊菌纲、座囊菌纲丰度下降,粪壳菌纲丰度增加。Alternaria,Amorphotheca,Aspergillus为尾矿裸地中主要优势真菌,Fusarium,Chaetomiaceae-Unclassified,Calcarisporiella为木贼根际土壤主要优势真菌。变形菌门、厚壁菌门、放线菌门是研究区土壤中的优势细菌类群,Lactococcus,Bacillus,Gemmatimonas,Sulfuricaulis,Dongia,Sulfurifustis,Azoarcus,Nitrospira等是尾矿地优势细菌。有机质、全氮与真菌和细菌ace,shannon指数显著相关,重金属含量与真菌和细菌ace,shannon指数显著或极显著负相关。木贼定居提高了尾矿砂中微生物的种类和多样性,有利于有机和氮素营养成分的积累和降低重金属含量;在尾矿生态修复实践中可多引入木贼等乡土草本先锋植物,同时补充有机质和氮素营养,或引入功能微生物菌剂和接种植物共生菌等,强化生态修复效果。     

设施高肥力蔬菜地氮素调控下磷素特征研究

设施蔬菜种植中存在不合理施肥现象,土壤养分严重失调。为了解设施蔬菜地高氮肥力水平下不同氮素水平对磷素的养分吸收影响,2004—2007年在山东寿光进行不同氮素水平调控和秸秆还田试验,并于2007年冬春季进行裂区淋滤试验。结果表明,不同水平的氮素调控影响磷素含量变化,空白（NN）、有机肥（MN）、有机肥＋秸秆（MN＋S）供氮水平下土壤全磷含量逐年下降,降幅NN〉MN〉MN＋S,全磷增幅传统氮素（cN）〉传统氮素＋秸秆（CN＋S）〉氮素优化＋秸秆（SN＋S）〉氮素优化（sN）。CN、CN＋S供氮水平下土壤速效磷含量达到213．7、225．4mg·kg^-1,增长了17．1％、23．5％,磷素累积明显;其他供氮水平下速效磷含量逐年下降,降幅NN〉MN〉MN＋S〉SN＋S〉SN〉CN〉CN＋S,减少氮素供应有利于减缓磷素累积,促进磷的吸收利用。除NN供氮水平下土壤有机磷含量下降外,其他处理均不同程度增加,CN、CN＋S供氮水平下土壤有机磷含量累积明显（308．4、331Amg·ks。）,分别增长了28．5％、38．2％。SN＋S供氮水平下磷的吸收系数（HO,,rrg·100g。）达到了1571,增长了143．6％;CN、CN＋S供氮水平下磷的吸收系数出现了负增长,CN供氮水平下达到了416（P2O5,mg·100g^-1）,下降了35．5％。添加麦秸秆极大地提高了磷的吸收能力,在一定程度上能减缓土壤速效磷的累积。淋溶液中全磷含量SN〉SN＋S,有机磷含量SN〉SN＋S,秸秆还田对阻控有机磷素淋溶有一定的作用,但整个冬春生长季渗滤液中全磷含量在2．6～12．0mg·L^-1,有机磷含量在OA2～4．1mg·L^-1,淋出液水质仍超过了国家安全水质标准。因此,在高肥力水平下进行氮素调控,优化氮素供应量,促进了磷素的吸收利用,对农民在高肥力水平下施肥具有指导意义。建议农民在以后的种植中减少氮肥供应量及添加高碳源秸秆进行还田,以提高肥料的利用率,减少氮磷对土壤及水体的污染。     

长庆油田石油污染土壤微生物种群多样性研究

以姬塬油田井场石油污染土壤为研究对象,通过高通量测序,分析了细菌群落的类型和结构,结果显示3份土壤样品中共检测到包括变形菌门、放线菌门、厚壁菌门、拟杆菌门、酸杆菌门和疣微菌门等24个门的细菌,土壤微生物结构多样性丰富,揭示了原油污染土壤的微生物种群多样性情况,对石油污染微生物治理技术具有重要的意义。     

气相色谱法测定水中有机磷农药

本方法研究了水样中ＤＤＶＰ、地亚农、乐果、甲基对硫磷、内吸磷、马拉硫磷、水胺硫磷、乙硫磷和乙基谷硫磷等九种有机磷农药的气相色谱分析方法。该方法用三氯甲烷提取水中的有机磷农药,毛细管柱分离,程序升温,ＦＰＤ测定。方法操作简单,测定水中有机磷农药的最低检出浓度在２．８ｎｇ／Ｌ至０．０２９ｍｇ／Ｌ之间,加标回收率在７０．０％～１２０％。方法适用于地表水、地下水和废水中痕量有机磷农药的测定。     

内源磷的释放作用及影响因素研究进展

水体的富营养化已成为目前环境研究中的焦点问题,磷在湖泊中的浓度高低是衡量湖泊富营养化水平的重要指标,是水生态系统基本营养盐之一,并且是淡水湖泊的最主要限制性营养因子。在外源磷得到有效的控制之后,内源磷的污染仍然能够保持湖泊的富营养化状态,此时内源磷的控制就成为了难点和重点。在底泥中的结合态磷,主要是以无机磷和有机磷的形式存在,有机磷与微生物活性密切相关,无机磷则主要与底泥存在的环境联系紧密。湖泊底泥内源磷释放受到一系列物理、化学、生物过程的控制,其影响因素主要包括扰动、氧化还原电位、pH值等,是多种因子综合作用的结果,同时,扰动引起的底泥再悬浮对内源磷有吸附固定作用。故底泥内源磷的释放机理有待进一步探索,在多种影响因素作用下,进一步研究底泥再悬浮对磷的吸附释放作用,从而明确内源磷的主要来源及吸附释放过程,为内源磷的控制提供理论依据,进而控制水体富营养化。     

我国南方典型水稻土中甲烷氧化细菌群落分布研究

甲烷氧化细菌以甲烷为其唯一的碳源和能源,在全球大气甲烷平衡中起着重要的作用。水稻土作为主要的甲烷的源和汇,其中分布大量的甲烷氧化细菌。文章通过利用T-RFLP技术发现我国干杉、广州、重庆、江都及进贤五地的水稻土中的甲烷氧化细菌主要的种群是甲基球菌属(Methylococcus)、甲基微球菌属(Methylomicrobium)、甲基孢囊菌属(Methylocystis)、甲基杆菌属(Methylobacter);五个地区水稻土的土壤中的甲烷氧化细菌分布存在差异,江都水稻土中甲烷氧化细菌种群类型较多,重庆水稻土中甲烷氧化细菌种群多样性指数最大。     

Pyrosequencing reveals bacteria carried in different wind-eroded sediments

Little is known about the microbial communities carried in wind-eroded sediments from various soil types and land management systems. The novel technique of pyrosequencing promises to expand our understanding of the microbial diversity of soils and eroded sediments because it can sequence 10 to 100 times more DNA fragments than previous techniques, providing enhanced exploration into what microbes are being lost from soil due to wind erosion. Our study evaluated the bacterial diversity of two types of wind-eroded sediments collected from three different organic-rich soils in Michigan using a portable field wind tunnel. The wind-eroded sediments evaluated were a coarse sized fraction with 66% of particles >106 μm (coarse eroded sediment) and a finer eroded sediment with 72% of particles <106 μm. Our findings suggested that (i) bacteria carried in the coarser sediment and fine dust were effective fingerprints of the source soil, although their distribution may vary depending on the soil characteristics because certain bacteria may be more protected in soil surfaces than others; (ii) coarser wind-eroded sediment showed higher bacterial diversity than fine dust in two of the three soils evaluated; and (iii) certain bacteria were more predominant in fine dust (, , and ) than coarse sediment ( and ), revealing different locations and niches of bacteria in soil, which, depending on wind erosion processes, can have important implications on the soil sustainability and functioning. Infrared spectroscopy showed that wind erosion preferentially removes particular kinds of C from the soil that are lost via fine dust. Our study shows that eroded sediments remove the active labile organic soil particulates containing key microorganisms involved in soil biogeochemical processes, which can have a negative impact on the quality and functioning of the source soil.     

Wet chemical and phosphorus-31 nuclear magnetic resonance analysis of phosphorus speciation in a sandy soil receiving long-term fertilizer or animal manure applications

In areas under intensive livestock farming and with high application rates of animal manure, inorganic and organic phosphorus (P) may be leached from soils. Since the contribution of these P compounds to P leaching may differ, it is important to determine the speciation of P in these soils. We determined the effect of various fertilization regimes on the P speciation in NaOH-Na2EDTA (ethylenediaminetetraacetic acid) and water extracts of acidic sandy soil samples from the top 5 cm of grassland with wet chemical analysis and 31P nuclear magnetic resonance (NMR) spectroscopy. These soils had been treated for a period of 11 years with no fertilizer (control), N (no P application), N-P-K, or different animal manures. Inorganic P was highly elevated in the NaOH-Na2EDTA extracts of the soils amended with N-P-K or animal manures, while organic P increased only in the soil treated with pig slurry. Water-extractable P showed a similar trend. As indicated by 31P NMR, orthophosphate monoesters were the main organic P compounds in all soils. Our results suggest that long-term applications of large amounts of P fertilizer and animal manures caused an accumulation of inorganic P, resulting in an increase of the potential risk related to mobilization of inorganic P in the top 5 cm of these soils.     

Phosphorus forms in biosolids-amended soils and losses in runoff: effects of wastewater treatment process

Continuous addition of municipal biosolids to soils based on plant nitrogen (N) requirements can cause buildup of soil phosphorus (P) in excess of crop requirements; runoff from these soils can potentially contribute to nonpoint P pollution of surface waters. However, because biosolids are often produced using lime and/or metal salts, the potential for biosolids P to cause runoff P losses can vary with wastewater treatment plant (WWTP) process. This study was conducted to determine the effect of wastewater treatment process on the forms and amounts of P in biosolids, biosolids-amended soils, and in runoff from biosolids-amended soils. We amended two soil types with eight biosolids and a poultry litter (PL) at equal rates of total P (200 kg ha(-1); unamended soils were used as controls. All biosolids and amended soils were analyzed for various types of extractable P, inorganic P fractions, and the degree of P saturation (acid ammonium oxalate method). Amended soils were placed under a simulated rainfall and all runoff was collected and analyzed for dissolved reactive phosphorus (DRP), iron-oxide-coated filter paper strip-extractable phosphorus (FeO-P), and total phosphorus (EPA3050 P). Results showed that biosolids produced with a biological nutrient removal (BNR) process caused the highest increases in extractable soil P and runoff DRP. Alternatively, biosolids produced with iron only consistently had the lowest extractable P and caused the lowest increases in extractable soil P and runoff DRP when added to soils. Differences in soil and biosolids extractable P levels as well as P runoff losses were related to the inorganic P forms of the biosolids.     

Phosphorus movement and speciation in a sandy soil profile after long-term animal manure applications

Long-term application of phosphorus (P) with animal manure in amounts exceeding removal with crops leads to buildup of P in soil and to increasing risk of P loss to surface water and eutrophication. In most manures, the majority of P is held within inorganic forms, but in soil leachates organic P forms often dominate. We investigated the mobility of both inorganic and organic P in profile samples from a noncalcareous sandy soil treated for 11 yr with excessive amounts of pig slurry, poultry manure, or poultry manure mixed with litter. Solution 31P nuclear magnetic resonance spectroscopy was used to characterize NaOH-EDTA-extractable forms of P, corresponding to 64 to 93% of the total P concentration in soil. Orthophosphate and orthophosphate monoesters were the main P forms detected in the NaOH-EDTA extracts. A strong accumulation of orthophosphate monoesters was found in the upper layers of the manure-treated soils. For orthophosphate, however, increased concentrations were found down to the 40- to 50-cm soil layers, indicating a strong downward movement of this P form. This was ascribed to the strong retention of orthophosphate monoesters by the solid phase of the soil, preventing orthophosphate sorption and facilitating downward movement of orthophosphate. Alternatively, mineralization of organic P in the upper layers of the manure-treated soils may have generated orthophosphate, which could have contributed to the downward movement of the latter. Leaching of inorganic P should thus be considered for the assessment and the future management of the long-term risk of P loss from soils receiving large amounts of manure.     

PHOSPHORUS RELEASE AND ASSIMILATORY CAPACITY OF TWO LOWER MISSISSIPPI VALLEY FRESHWATER WETLAND SOILS1

ABSTRACT: Phosphorus fluxes and water quality functions of a bottomland hardwood and freshwater marsh wetland soil were compared. The effect of soil physicochemical conditions, phosphorus loading rate, and diffusive exchange between soils and the overlying food water column on phosphorus release and retention were studied. The predominantly mineral swamp forest soil displayed greater phosphorus sorption potential than the organic freshwater marsh soil. Moreover, due to its low bulk density (0.11 g cm^?3), the freshwater marsh soil surface area required for phosphorus retention is very large compared to the bottomland hardwood wetland soil. For both wetlands, soil redox status affected P release and assimilatory capacity. The more reducing the soils, the smaller their phosphorus retention capacity (greater their release). Phosphorus removal from the overlying water column into the wetland soils followed a first-order kinetic model. Under similar hydrological conditions, phosphorus was found to diffuse 1.2 times faster to the bottom. land hardwood soil than in the freshwater marsh soil. Results indicate that while the bottomland hardwood wetland soil will serve as a sink for phosphorus entering such wetland, phosphorus will be released and exported from the freshwater marsh soil into adjacent ecosystems.     

Organic phosphorus fractions in organically amended paddy soils in continuously and intermittently flooded conditions

Soil organic phosphorus (SOP) can greatly contribute to plant-available P and P nutrition. The study was conducted to determine the effects of organic amendments on organic P fractions and microbiological activities in paddy soils. Samples were collected at the Changshu Agro-ecological Experiment Station in Tahu Lake Basin, China, from an experiment that has been performed from 1999 to 2004, on a paddy soil (Gleysols). Treatments consisted of swine manure (SM), wheat straw (WS), swine manure plus wheat straw (SM + WS), and a control (chemical fertilization alone). Organic amendments markedly increased soil total organic phosphorus (TOP) and total organic carbon (TOC), especially in continuously flooded conditions. Based on the fractionation of SOP, organic amendments significantly increased soil labile organic phosphorus (LOP), moderately labile organic phosphorus (MLOP), and moderately stable organic phosphorus (MSOP) compared with the control. For SM and SM + WS treatments, LOP in continuously flooded soils decreased by 30.1 and 36.4%, respectively, compared to intermittently flooded soils. In organically amended soils, continuous flooding showed significantly lower microbial biomass phosphorus (MBP) and alkaline phosphatase activities (APA) than intermittent flooding. In intermittently flooded conditions, incorporating organic amendments into soil resulted in greater P uptake and biomass yield of rice than the control. In the intermittently flooded soils, APA (P < 0.05) and MBP (P < 0.01) were significantly and positively related to TOP, LOP, MLOP, and MSOP, whereas in continuously flooded soils, there was a significant (P < 0.05) negative relationship between MBP, TOP, and MSOP. Based on soil organic P fractions and soil enzymatic and microbiological activities, continuous flooding applied to paddy soils should be avoided, especially when swine manure is incorporated into paddy soil.     

Relationships between soil physicochemical, microbiological properties, and nutrient release in buffer soils compared to field soils

The retention of nutrients in narrow, vegetated riparian buffer strips (VBS) is uncertain and underlying processes are poorly understood. Evidence suggests that buffer soils are poor at retaining dissolved nutrients, especially phosphorus (P), necessitating management actions if P retention is not to be compromised. We sampled 19 buffer strips and adjacent arable field soils. Differences in nutrient retention between buffer and field soils were determined using a combined assay for release of dissolved P, N, and C forms and particulate P. We then explored these differences in relation to changes in soil bulk density (BD), moisture, organic matter by loss on ignition (OM), and altered microbial diversity using molecular fingerprinting (terminal restriction fragment length polymorphism [TRFLP]). Buffer soils had significantly greater soil OM (89% of sites), moisture content (95%), and water-soluble nutrient concentrations for dissolved organic C (80%), dissolved organic N (80%), dissolved organic P (55%), and soluble reactive P (70%). Buffer soils had consistently smaller bulk densities than field soils. Soil fine particle release was generally greater for field than buffer soils. Significantly smaller soil bulk density in buffer soils than in adjacent fields indicated increased porosity and infiltration in buffers. Bacterial, archaeal, and fungal communities showed altered diversity between the buffer and field soils, with significant relationships with soil BD, moisture, OM, and increased solubility of buffer nutrients. Current soil conditions in VBS appear to be leading to potentially enhanced nutrient leaching via increasing solubility of C, N, and P. Manipulating soil microbial conditions (by management of soil moisture, vegetation type, and cover) may provide options for increasing the buffer storage for key nutrients such as P without increasing leaching to adjacent streams.     

Phosphorus speciation in manure-amended alkaline soils

Two common manure storage practices are stockpiles and lagoons. The manure from stockpiles is applied to soils in solid form, while lagoon manure is applied as a liquid. Soil amendment with manure in any form introduces a significant amount of phosphorus (P) that exists in both organic and inorganic forms. However, little is known about P speciation in manure stored under different conditions, or the subsequent forms when applied to soils. We used solution (31)P nuclear magnetic resonance (NMR) spectroscopy and conventional P fractionation and speciation methods to investigate P forms in dairy manure and liquid lagoon manure, and to study how long-term amendment with these manures influenced surface and subsurface soil P speciation. Our results show that the P forms in solid and lagoon manure are similar. About 30% of the total P was organic, mostly as orthophosphate monoesters. On a dry weight basis, total P was much higher in the solid manure. In the manure-amended soils the total P concentrations of the surface soils were similar, regardless of manure type. Total P in the subsurface soil was greater in the lagoon-manure-amended soil than the solid-manure-amended subsurface soil. However, the fraction of organic P was greater in the subsurface of the solid-manure-amended soil. The NMR results indicate that the majority of organic P in the soils is phytic acid, which is enriched in the surface soils compared with the subsurface soils. These results provide insight into P speciation and dynamics in manure-amended soils that will further increase our understanding on how best to manage manure disposal on soils.     

Adsorption of cadmium on biosolids-amended soils

Debate exists over the biosolid phase (organic or inorganic) responsible for the reduction in phytoavailable Cd in soils amended with biosolids as compared with soils amended with inorganic salts. To test the importance of these two phases, adsorption isotherms were developed for soil samples (nine biosolids-amended soils and their five companion controls) and two biosolids samples from five experimental sites with documented histories of biosolids application. Subsamples were treated with 0.7 M NaClO to remove organic carbon. Cadmium nitrate was added to both moist soil samples and their soil inorganic fractions (SIF) in a 0.01 M Ca(NO3)2 solution at three pH levels (6.5, 5.5, and 4.5), and equilibrated at 22 +/- 1 degrees C for at least 48 h. Isotherms of Cd adsorption for biosolids-amended soil were intermediate to the control soil and biosolids. Decreasing pH did not remove the difference between these isotherms, although adsorption of Cd decreased with decreasing pH level. Organic matter removal reduced Cd adsorption on all soils but had little influence on the observed difference between biosolids-amended and control soils. Thus, increased adsorption associated with biosolids application was not limited to the organic matter addition from biosolids; rather, the biosolids application also altered the adsorptive properties of the SIF. The greater affinity of the inorganic fraction of biosolids-amended soils to adsorb Cd suggests that the increased retention of Cd on biosolids-amended soils is independent of the added organic matter and of a persistent nature.