哌虫啶在土壤中的降解动态及对土壤微生物的影响

采用实验室模拟方法研究了烟碱类新农药哌虫啶在土壤生态系统中的降解动态及其对土壤微生物的影响。结果表明,哌虫啶的降解过程符合一级反应动力学方程,浓度为1、5和10 mg kg-1的哌虫啶在土壤中的降解半衰期为11.28~7.30 d。哌虫啶对土壤微生物的毒性作用与浓度正相关。施药后哌虫啶对土壤中细菌和放线菌的数量具有激活作用,3 d后,哌虫啶开始抑制土壤中细菌和放线菌的数量,施药后5 d内,哌虫啶促进了真菌的生长繁殖,10 d后表现为抑制真菌数量,有先促进后抑制细菌、真菌和放线菌的趋势。哌虫啶施入土壤后对土壤酶活性具有一定的影响,土壤碱性磷酸酶较酸性磷酸酶更敏感,哌虫啶具有抑制酸性磷酸酶和碱性磷酸酶的作用,这种抑制作用一直延续至试验的第20天;施药处理组对脲酶活性均有显著的抑制作用,并且浓度越大,抑制作用越强烈;哌虫啶对土壤脱氢酶具有显著的激活作用,哌虫啶对土壤过氧化氢酶影响作用较弱。总之哌虫啶在土壤中降解半衰期较短,属于易降解农药,10 mg kg-1浓度的哌虫啶对土壤微生物具有一定的毒性作用。     

乙草胺对土壤微生物数量和酶活性的影响

采用室内瓶培养试验,研究了乙草胺施用对土壤微生物数量及酶活性的影响。结果表明:乙草胺施用初期对土壤细菌和放线菌数量有明显刺激作用,但施用30d时高施用量处理(30mg·kg-1)呈明显抑制作用,之后各处理放线菌恢复到对照水平,而对细菌的抑制作用一直持续到60d;乙草胺对土壤真菌数量呈"抑制-恢复-刺激"的作用趋势。乙草胺施用初期对土壤脱氢酶产生一定刺激作用,45d后高施用量处理呈明显抑制作用,一直持续到60d;土壤过氧化氢酶对乙草胺不敏感,而转化酶和脲酶对乙草胺施入初期较敏感;低施用量处理对转化酶有抑制作用,高施用量处理对转化酶有刺激作用,各处理对脲酶都有抑制作用。     

土壤微生物对除草剂乙草胺污染的响应和指示

采用除草剂乙草胺作为土壤污染因子, 在人工可控制条件下, 研究乙草胺对土壤微生物细菌、真菌和放线菌数量及土壤微生物量碳的影响, 并探讨这些微生物学指标对土壤中乙草胺污染状况的指示.研究结果表明: 在整个试验过程中, 除草剂乙草胺在短时间内对微生物区系能产生明显抑制作用, 但随着时间增加和污染物的分解, 微生物数量逐渐得到恢复.在短时间抑制过程中, 细菌、放线菌数量以及微生物量碳与乙草胺浓度的对数之间有很好的剂量效应关系, 第7 d细菌数量与乙草胺浓度对数的拟合公式为y = -2.97x + 12.36, R2 = 0.999 3; 放线菌数量与乙草胺浓度对数的拟合公式为y = -2.13x + 6.67, R2 = 0.956 4; 微生物量碳在第14 d与乙草胺浓度对数的拟合公式为y = -89.25x + 348.90, R2 = 0.995 4; 其相关性都达到显著水平.而真菌在受到乙草胺污染后, 受抑制现象并不明显, 真菌对乙草胺有较强的抗性.总之在短期污染条件下, 土壤中的细菌、放线菌数量以及微生物量碳可以很好地指示土壤中乙草胺的污染状况.     

苯磺隆和2,4-D胁迫对土壤微生物影响的研究

以盆栽试验研究了除草剂苯磺隆、2,4-D对石灰性褐土中土壤微生物群落的影响。结果表明,在供试浓度下,土壤微生物对两种除草剂的感应存在一定的差异性。苯磺隆高浓度处理在最初3d极显著地抑制细菌生长,之后对土壤细菌具有刺激作用,特别是培养结束时激活率还高达917.6%,低浓度处理呈极显著的刺激作用;苯磺隆对土壤放线菌具有显著的刺激作用,对土壤真菌有强烈的抑制作用,最高抑制率达100%,到培养结束时(60d)真菌数量还未恢复到对照水平。2,4-D处理对土壤放线菌具有明显的抑制、激活的波动性,对土壤细菌、真菌有强烈的抑制作用。     

磷化铝对土壤微生物数量和酶活性的影响

为明确磷化铝对土壤微生物数量和酶活性的影响,采用室内培养的方法,研究了经0.1、1mg.g-1和10mg.g-13个浓度磷化铝熏蒸处理后,供试土壤中微生物数量和土壤酶活性的变化。结果表明,磷化铝处理土壤后,各个浓度的磷化铝对土壤细菌、真菌和放线菌数量具有抑制作用,浓度越高,抑制作用越强,但一段时间后低浓度（0.1mg.g-1）处理对土壤微生物数量的影响恢复至对照水平。磷化铝对土壤脲酶表现为抑制作用,并随浓度升高而增强;低浓度处理对土壤中的蔗糖酶活性抑制作用不明显,而高浓度（10mg.g-1）处理表现为强烈的抑制作用;各浓度处理初期对土壤过氧化氢酶表现为抑制或激活作用,但到第30d,恢复至对照水平。这说明,施入常规剂量的磷化铝对土壤微生物数量和土壤酶活性会产生一定的影响,在经过一定时间后均可恢复至对照水平。     

百草枯对土壤微生物影响的研究

研究了5种不同浓度百草枯对土壤微生物种群数量及土壤中细菌、放线菌和真菌生长速率的影响。结果表明,百草枯对土壤微生物的种群数量及土壤细菌、放线菌和真菌生长速率均具有一定的抑制作用,且随药剂浓度升高逐渐增强。加药后2～7d,对细菌种群抑制率为13.3%～100%,抑菌圈直径达0.07～0.93cm;对放线菌种群抑制率为8.6%～100%,抑菌圈直径达0～3.00cm;对真菌种群抑制率为7.6%～100%,生长速率的抑制率达1.4%～77.3%。抑制作用随加药时间延长又逐渐减弱。     

氟磺胺草醚对大豆根际土壤微生物和酶活性的影响及其在根际的降解

【目的】 本研究旨在探讨不同浓度氟磺胺草醚在大豆根际土壤中的微生态效应,及其在根际土壤中的降解动态,为进一步研究除草剂的残留污染提供科学依据。 【方法】 以中黄13号大豆为材料,采用根箱进行了模拟栽培试验。设施用氟磺胺草醚3.75 mg/kg (低)、7.5 mg/kg (中)、18.75 mg/kg (高) 3个水平,以不添加氟磺胺草醚处理为对照,调查了大豆根际土壤细菌、真菌、放线菌数量,分析了根际土壤中过氧化氢酶、磷酸酶、脲酶、蔗糖酶4种酶活性,以及氟磺胺草醚在大豆根际土壤中的降解规律。 【结果】 低浓度氟磺胺草醚处理的大豆根际土壤细菌数量显著低于对照根际土壤 (P < 0.05),高浓度氟磺胺草醚处理在28 d时显著高于对照 ( P < 0.05);中浓度氟磺胺草醚处理与对照没有显著性差异。不同浓度氟磺胺草醚处理的大豆根际土壤真菌和放线菌数量与对照差异不显著。氟磺胺草醚处理的大豆根际土壤过氧化氢酶活性与对照没有显著差异;磷酸酶活性在取样初期略有降低;低浓度氟磺胺草醚处理的土壤脲酶活性显著降低,中浓度和高浓度处理对脲酶活性表现为先刺激后抑制;高浓度氟磺胺草醚处理的蔗糖酶活性在42 d和56 d时显著低于对照。高浓度氟磺胺草醚降解速率明显高于低浓度和中浓度,并且在试验初期降解迅速;3种浓度氟磺胺草醚在大豆根际土壤中的降解均符合一级动力学方程,降解半衰期由低浓度到高浓度逐渐变短。 【结论】 3种浓度氟磺胺草醚总体上降低大豆根际土壤中细菌的数量,而对大豆根际土壤真菌和放线菌的数量均没有显著影响。氟磺胺草醚对大豆根际土壤过氧化氢酶活性没有显著影响,在短期内对磷酸酶活性有一定程度的抑制作用,低浓度氟磺胺草醚可以显著降低大豆根际土壤脲酶活性,而高浓度氟磺胺草醚在试验后期可以显著抑制大豆根际土壤蔗糖酶活性。大豆根际土壤中氟磺胺草醚初始浓度越高,降解速率越快,半衰期越短。      

NaCl胁迫下苯丙烯酸对黄瓜幼苗根际土壤微生物及产量的影响

实验以耐盐的津绿5号和盐敏感的津优1号黄瓜品种为试材,以NaCl(585 mg kg-1)为盐胁迫条件,研究了盐胁迫下不同浓度的苯丙烯酸(0、25、50、200 mg kg-1)对黄瓜幼苗根际土壤微生物及产量的影响。结果表明,盐胁迫处理降低了黄瓜幼苗土壤根际细菌、真菌、放线菌的数量,而对镰孢菌数量有促进作用,并降低了黄瓜产量。低浓度的苯丙烯酸对黄瓜幼苗土壤根际细菌、真菌、放线菌的数量具有促进作用,对镰孢菌有抑制作用,对盐胁迫有一定的缓解作用,并对黄瓜产量具有促进作用;高浓度苯丙烯酸(200 mg kg-1)则相反,进一步加重了盐害的胁迫程度,抑制了黄瓜产量。盐胁迫对细菌、真菌、放线菌和镰孢菌数量的影响强度大于苯丙烯酸,而苯丙烯酸对细菌群落DGGE条带数和黄瓜产量的影响强度大于盐分胁迫。     

乐果与Cd2＋复合污染对土壤微生物生态效应研究

土壤微生物数量及土壤酶活性是描述土壤的重要生物学指标。在实验室控制条件下,研究了农药乐果、Cd2＋单一污染及乐果与Cd2＋复合污染对土壤3大类群微生物数量和主要土壤酶活性的影响。结果表明,Cd2＋和乐果复合处理对土壤中微生物生长存在着明显的拮抗作用,复合抑制效应顺序为放线菌〉真菌〉细菌;而对土壤酶活性均有明显的协同作用,复合抑制效应顺序为蛋白酶〉蔗糖酶〉脲酶。单一污染时,100mg·kg-1乐果的处理可不同程度地抑制这些生物学指标,其中对土壤微生物数量的抑制效应顺序为真菌〉放线菌〉细菌,对土壤酶活性的抑制效应顺序与乐果和Cd2＋复合污染顺序一致;50mg·kg-1浓度的乐果对这些指标几乎无影响。     

长期轮作与施肥对土壤主要微生物类群的影响

根据长期田间试验,对施肥、作物、种植方式等对土壤细菌、真菌与放线菌含量的影响进行分析.结果显示施肥,特别是施有机肥明显提高土壤微生物数量,玉米、苜蓿与冬小麦连作不同施肥土壤细菌数量相对休闲地变幅在-197.04×105～+187.07×105个/g土,真菌在-6.08×103～+36.57×103个/g土,放线菌在-47.21×104～+301.4×104个/g土.轮作系统不同施肥处理真菌与放线菌数量高于休闲地.在施氮磷化肥条件下不同作物轮作,苜蓿与糜子对细菌有相对抑制作用,对真菌与放线菌有促进作用,红豆草抑制放线菌促进细菌,豌豆对三类微生物均有抑制作用.     

Tebuconazole application decreases soil microbial biomass and activity

A short-term mesocosm experiment was conducted to ascertain the impact of tebuconazole on soil microbial communities. Tebuconazole was applied to soil samples with no previous pesticide history at three rates: 5, 50 and 500 mg kg⁻¹ DW soil. Soil sampling was carried out after 0, 7, 30, 60 and 90 days of incubation to determine tebuconazole concentration and microbial properties with potential as bioindicators of soil health [i.e., basal respiration, substrate-induced respiration, microbial biomass C, enzyme activities (urease, arylsulfatase, β-glucosidase, alkaline phosphatase, dehydrogenase), nitrification rate, and functional community profiling]. Tebuconazole degradation was accurately described by a bi-exponential model (degradation half-lives varied from 9 to 263 days depending on the concentration tested). Basal respiration, substrate-induced respiration, microbial biomass C and enzyme activities were inhibited by tebuconazole. Nitrification rate was also inhibited but only during the first 30 days. Different functional community profiles were observed depending on the tebuconazole concentration used. It was concluded that tebuconazole application decreases soil microbial biomass and activity.     

Effects of a cadmium-contaminated sewage sludge compost on dynamics of organic matter and microbial activity in an arid soil

 An incubation experiment lasting 120 days was carried out to ascertain the effect on the soil microbial activity and organic matter mineralization of adding a sewage sludge compost contaminated with two different levels of Cd to an arid soil. Two composts, with a low (2 mg kg^–1) and high (815 mg kg^–1) Cd content, respectively, were used in this experiment. Both composts increased the total organic C, humic substance and water-soluble C contents, the beneficial effects still being noticeable after 120 days of incubation. The most labile C fraction (water-soluble C) was the most sensitive to the high Cd content. The high Cd concentration decreased soil microbial biomass C and stimulated the metabolic activity of the microbial biomass, the metabolic quotient (qCO₂) revealing itself to be a very sensitive index of the stress that the incorporation of a Cd-contaminated sewage sludge compost causes in a soil. The effect of Cd contamination on enzyme activities (urease, protease that hydrolyse N-α-benzoil-l-arginamide, phosphatase, and β-glucosidase) depended on the enzyme studied. Received: 10 September 1997     

Influence of acetamiprid on soil enzymatic activities and respiration

The effect of a new pesticide, acetamiprid, applied at normal field concentration (0.5 mg kg⁻¹ dried soil) and at high concentration (5 and 50 mg kg⁻¹ dried soil), on soil enzyme activities and soil respiration in upland soil was studied. The results showed that acetamiprid had a strong negative influence on soil respiration and phosphatase activity, and the enzyme activities in soil treated with 5 and 50 mg kg⁻¹ dry soil were significantly (P < 0.05) lower than the CK over the course of incubation. The 7-, 14-, and 35-day EC10 for phosphatase were 11, 15, and 11 mg kg⁻¹ dry soil, respectively. The 21-day EC10 and EC50 for soil respiration was 0.005 and 83 mg kg⁻¹ dry soil. The activity of dehydrogenase was enhanced after acetamiprid application for 2 weeks and the enzyme activities in samples treated with 0.5, 5 and 50 mg kg⁻¹ dry soil was about 2.5-, 1.5- and 2-fold to that of the control on sample day 28. Variance of urease and catalase had no distinct relationship with the application concentration. The activity of proteinase was not significantly affected within the first 2 weeks but inhibited from the fourth week after acetamiprid application and was only 0.45-fold to that of the control on sample day 28. Overall, acetamiprid at normal field dose would not pose a toxicological threat to soil enzymes, but a certain potential threat to soil respiration.     

Effects of Sulfur Fertilization on Soybean Root and Leaf Traits,and Soil Microbial Activity

ABSTRACT

A pot experiment was implemented to study effects of sulfur (S) fertilization on soybean root and leaf traits and soil microbial activity in 2004 and 2005. In this experiment, three different treatments were established: 0 mg· kg^{? 1}(CK), 30 mg· kg^{? 1}(A), and 60 mg· kg^{? 1}(B). The results showed that an application of elemental sulfur significantly increased the number of soybean side roots by 8.6% to 33.2% and dry weight by 6.6% to 34.3%, increased the root nodules number by 2.7% to 35.9%, and dry weight by 13.0% to 75.7%, increased chlorophyll content in leaves by 0.4 to 3.9 unit, and increased soybean yield per plant by 7.3% to 12.8%, compared with the control. The application of elemental sulfur also increased the amount of soil microorganism (bacterium, fungi and actinomycete), activity of catalase, urease, neutral phosphatase, and polyphenoloxidase in the same growth stage significantly. The above results showed sulfur supply could promote the growth of soybean, increase the yield, and enhance soil microbial activity. Thirty mg· kg^{? 1} was the suitable rate of sulfur for achieving the highest yield.     

Enzyme activities in vineyard soils long-term treated with copper-based fungicides

Copper-based fungicides have been applied in vineyard soils for a long time, which has resulted in increasing soil Cu concentration. However, information relating to non-target effects of these fungicides on microorganisms of these soils is scarce. The aim of this study was to determine the potential enzyme activities of vineyard soils in relation to Cu content and evaluate the potential risks of long-term application of Cu-based fungicides. For this purpose, a wide range of soil samples, having different total, exchangeable and bioavailable Cu contents, were collected from six regions of quality wines located in the NW Iberian Peninsula, and the activity of dehydrogenase, β-glucosidase, urease and phosphatase were measured. Overall, the results obtained indicate adverse effects of Cu on dehydrogenase, β-glucosidase and phosphatase activities and an inconsistent effect on urease activity. Threshold Cu concentrations at which changes in the enzyme activities became evident were 150-200 mg total Cu kg⁻¹ and 60-80 mg bioavailable Cu kg⁻¹.     

施磷处理对中性紫色土土壤硝化作用的影响

针对长期定位试验站长期不施化肥的低磷土壤,设置了不同水平的磷素添加共9个处理(P2O5 0~150 mg kg-1土),通过75 d的室内培养实验,探讨磷素处理对土壤硝化细菌及硝化作用的影响。结果表明,适量磷素添加显著刺激了硝化细菌生长,但高浓度磷素添加将抑制硝化细菌数量。进一步通过好氧培养法和悬液法分别测定了土壤硝化潜势,发现不同水平的磷素短期培养后,土壤硝化潜势均出现不同幅度的增加,并且均在P2O5 40~60 mg kg-1土之间最高,但磷素供应水平影响硝化作用的机制仍待进一步研究。     

Microbial and enzyme properties of apple orchard soil as affected by long-term application of copper fungicide

Copper-based fungicides have been applied in apple orchards for a long time, which has resulted in increasing soil Cu concentration. However, the microbial and enzyme properties of the orchard soils remain poorly understood. This study aimed to evaluate the effect of long-term application of Cu-based fungicides on soil microbial (microbial biomass carbon (C_mic), C mineralization, and specific respiration rate) and enzyme (urease, acid phosphatase, and invertase activities) properties in apple orchards. Soil samples studied were collected from apple orchards 5, 15, 20, 30, and 45 years old, and one adjacent forest soil as for reference. The mean Cu concentrations of orchard soils significantly increased with increasing orchard ages ranging from 21.8 to 141 mg kg⁻¹, and the CaCl₂-extractable soil Cu concentrations varied from 0.00 to 4.26 mg kg⁻¹. The soil mean C_mic values varied from 43.6 to 116 mg kg⁻¹ in the orchard soils, and were lower than the value of the reference soil (144 mg kg⁻¹). The ratio of soil C_mic to total organic C (C_org) increased from 8.10 to 18.3 mg C_mic g⁻¹ C_org with decreasing orchard ages, and was 26.1 mg C_mic g⁻¹ C_org for the reference soil. A significant correlation was observed between total- or CaCl₂-extractable soil Cu and soil C_mic or C_mic/C_org, suggesting that the soil Cu was responsible for the significant reductions in C_mic and C_mic/C_org. The three enzyme activity assays also showed the similar phenomena, and declined with the increasing orchard ages. The mean soil C mineralization rates were elevated from 110 to 150 mg CO₂-C kg⁻¹ soil d⁻¹ compared with the reference soil (80 mg CO₂-C kg⁻¹ soil d⁻¹), and the mean specific respiration rate of the reference soil (0.63 mg CO₂-C mg⁻¹ biomass C d⁻¹) was significantly smaller than the orchard soils from 1.19 to 3.55 mg CO₂-C mg⁻¹ biomass C d⁻¹. The soil C mineralization rate and the specific respiration rate can be well explained by the CaCl₂-extractable soil Cu. Thus, the long-term application of copper-based fungicides has shown adverse effects on soil microbial and enzyme properties.     

Changes in soil biological and biochemical characteristics in a long-term field trial on a sub-tropical inceptisol

Soil organic carbon (SOC), microbial biomass carbon (MBC), their ratio (MBC/SOC) which is also known as microbial quotient, soil respiration, dehydrogenase and phosphatase activities were evaluated in a long-term (31 years) field experiment involving fertility treatments (manure and inorganic fertilizers) and a maize (Zea mays L.)-wheat (Triticum aestivum L.)-cowpea (Vigna unguiculata L.) rotation at the Indian Agricultural Research Institute near New Delhi, India. Applying farmyard manure (FYM) plus NPK fertilizer significantly increased SOC (4.5-7.5 g kg⁻¹), microbial biomass (124-291 mg kg⁻¹) and microbial quotient from 2.88 to 3.87. Soil respiration, dehydrogenase and phosphatase activities were also increased by FYM applications. The MBC response to FYM+100% NPK compared to 100% NPK (193 vs. 291 mg kg⁻¹) was much greater than that for soil respiration (6.24 vs. 6.93 μl O₂ g⁻¹ h⁻¹) indicating a considerable portion of MBC in FYM plots was inactive. Dehydrogenase activity increased slightly as NPK rates were increased from 50% to 100%, but excessive fertilization (150% NPK) decreased it. Acid phosphatase activity (31.1 vs. 51.8 μg PNP g⁻¹ h⁻¹) was much lower than alkali phosphatase activity (289 vs. 366 μg PNP g⁻¹ h⁻¹) in all treatments. Phosphatase activity was influenced more by season or crop (e.g. tilling wheat residue) than fertilizer treatment, although both MBC and phosphatase activity were increased with optimum or balanced fertilization. SOC, MBC, soil respiration and acid phosphatase activity in control (no NPK, no manure) treatment was lower than uncultivated reference soil, and soil respiration was limiting at N alone or NP alone treatments.     

Influence of inorganic fertilizers and organic amendments on soil organic matter and soil microbial properties under tropical conditions

 Soil organic matter level, mineralizable C and N, microbial biomass C and dehydrogenase, urease and alkaline phosphatase activities were studied in soils from a field experiment under a pearl millet-wheat cropping sequence receiving inorganic fertilizers and a combination of inorganic fertilizers and organic amendments for the last 11 years. The amounts of soil organic matter and mineralizable C and N increased with the application of inorganic fertilizers. However, there were greater increases of these parameters when farmyard manure, wheat straw or Sesbania bispinosa green manure was applied along with inorganic fertilizers. Microbial biomass C increased from 147 mg kg^–1 soil in unfertilized soil to 423 mg kg^–1 soil in soil amended with wheat straw and inorganic fertilizers. The urease and alkaline phosphatase activities of soils increased significantly with a combination of inorganic fertilizers and organic amendments. The results indicate that soil organic matter level and soil microbial activities, vital for the nutrient turnover and long-term productivity of the soil, are enhanced by use of organic amendments along with inorganic fertilizers. Received: 6 May 1998