黑土中乙草胺残留和微生物变化的时间特征研究

通过黑土室外盆栽试验,研究了种植玉米和未种植条件下乙草胺在玉米生长苗期的残留变化规律及土壤微生物量碳的动态特征。研究表明:乙草胺在土壤中半衰期较短,土壤微生物活性是影响其降解的主要因素。但是,由于施用化肥极大地刺激了微生物活性,因而,乙草胺施用对土壤微生物量碳影响并不显著。然而,玉米的种植对土壤微生物量和土壤乙草胺残留数量有着显著的影响。种植玉米条件下土壤微生物量碳显著增加,同时,土壤中乙草胺残留量降低,说明种植玉米有助于微生物活性的提高和乙草胺生物毒害性的降低。     

原位土壤中乙草胺降解迁移规律研究

通过原位试验,研究了乙草胺在海伦农田黑土中残留和迁移的时间特征和微生物对乙草胺的降解作用。结果显示:乙草胺按推荐量施入土壤后,在0-10cm层次微生物降解作用非常明显,使乙草胺残留显著降低,同时由于海伦黑土有机质含量高,保水能力强,因而乙草胺不易向深层移动。但连续降水显著促进乙草胺向下层土壤迁移并有所积累,因此施药初期要尽量避开此种天气,以提高乙草胺持效性并降低其生态环境风险。     

乙草胺对玉米根际和非根际可培养微生物的影响

为探明土壤-植物系统中,田间施用量的乙草胺对玉米根际和非根际微生物数量的影响,采用田间试验及室内测试方法,在玉米苗期不同阶段测定了土壤中微生物量碳的变化,并进一步用平板稀释培养法研究了玉米根际和非根际土壤中细菌和真菌数量的变化。结果表明,乙草胺施用对玉米根际和非根际的土壤微生物群落均具有一定影响。可培养的根际细菌和真菌均呈现先抑制后刺激的变化,但与真菌不同,细菌受到的抑制作用时间较短,刺激作用时间较长;而本体土壤中可培养细菌和真菌则主要受到抑制作用,但是抑制作用的强度和持续时间差别很大。乙草胺对根际土壤微生物量碳可产生一定刺激作用,但影响并不显著;由于乙草胺施用对非根际土壤细菌和真菌的影响不同步并存在群落结构的补偿作用,从而维持了非根际土壤总体微生物生物量碳的基本稳定。     

土壤微生物对紫茎泽兰生长与竞争的反馈: 不同灭菌方法的比较

土壤微生物去除是验证土壤微生物反馈调节入侵植物竞争排斥本地植物群落的重要手段。为了确定土壤微生物反馈效应的最佳土壤微生物去除方法,以及土壤微生物对紫茎泽兰与本地植物竞争中的反馈作用,本试验比较了添加蛭石和未添加蛭石下,3种常见土壤微生物灭菌方式(干热灭菌、湿热灭菌、辐照灭菌)处理的紫茎泽兰单优群落根际土壤对紫茎泽兰与本地植物香茶菜生长的影响。结果表明:与未灭菌处理土壤相比,3种灭菌处理土壤均显著抑制了紫茎泽兰和香茶菜的生长;添加蛭石灭菌的土壤相对于未添加蛭石的灭菌土壤显著促进了2种植物的生长;灭菌土壤添加蛭石的情况下辐照灭菌土壤的两种植物的生物量显著地高于干热灭菌和湿热灭菌土壤两种植物的生物量,其中辐照灭菌下紫茎泽兰的生物量分别比干热灭菌和湿热灭菌条件下增加30.8%和66.5%,香茶菜生物量分别显著增加109.5%和63.4%。辐照灭菌土壤添加蛭石的处理方式最接近真实地反映土壤微生物对植物生长的反馈效应。进一步进行辐照灭菌土壤添加蛭石处理与未灭菌土壤添加蛭石处理的紫茎泽兰与香茶菜混种的盆栽试验,结果显示,土壤微生物显著增强了紫茎泽兰对香茶菜的竞争优势,相对竞争优势度增加16.0%,说明土壤微生物在紫茎泽兰竞争排斥本地植物的入侵过程中具有正反馈偏利调节作用     

两种环境激素类农药及其混合剂在土壤中的降解研究

为了深入了解环境激素类农药在与其它多种农药同时存在条件下在土壤中的降解过程、阐释其机理,用室内培养的方法,研究氯氰菊酯、毒死蜱两种农药及其混合剂在灭菌和未灭菌土壤中的降解特征。结果表明,两种农药及其混合剂在土壤中的降解是微生物主导的过程;灭菌土壤中,混合剂中各农药组分与其单独存在降解过程基本一致,均符合单室模型C=C0e-kt,降解半衰期也与其单独存在相近;但在未灭菌土壤中,混合剂中各农药组分降解特点与其单独存在有所不同。两种农药单独存在时,氯氰菊酯、毒死蜱在未灭菌土壤中的降解方程均符合单室模型,降解半衰期分别为31.5 d和57.8 d;混合剂中各组分农药在未灭菌土壤中的降解过程符合双室模型C=C1e-αt+C2e-βt,不同阶段降解半衰期不同,氯氰菊酯前期和后期半衰期分别为33.0 d和53.3;而毒死蜱前期和后期的半衰期则分别为63.0 d和86.6 d。在未灭菌土壤中多种农药存在时各种农药降解均呈现先快后慢的特点。     

双草醚在稻田土壤中的降解及其影响因子的研究

采用了实验室模拟方法研究了双草醚在不同土壤中的降解动态。结果表明,在未灭菌的土壤中,双草醚三种浓度(2.0、10.0、50.0mg kg-1)处理的半衰期为7.6~10.3d,远远小于在灭菌土壤中3种添加浓度处理的半衰期(43.3~61.9 d);双草醚在偏酸土壤中降解较快,随着土壤含水量的增加和环境温度的增高,双草醚降解速度加快。4种试验因子中土壤微生物是影响双草醚降解的主要因素,有利于土壤中微生物生长的环境因素,如偏酸的土壤、较高的温度和土壤湿度等,也能促进土壤中双草醚的降解。     

氮肥用量对石灰性土壤二氧化碳释放的影响

采用室内培养方法研究了灭菌及未灭菌条件下施用氮肥对石灰性土壤p H值、矿质态氮含量和CO2释放量的影响。结果表明:土壤CO2释放量随施氮量增加而显著增加,培养结束时未灭菌土壤CO2累积释放量比对照增加了21.8%~103.5%,平均增加62.7%,这与施氮促进有机质矿化及降低土壤p H值促进无机碳分解有关。采用哌嗪-1,4-二乙磺酸(PIPES)缓冲的Hg Cl2溶液灭菌后,培养期间不同施氮量下土壤铵态氮与硝态氮含量稳定,说明灭菌处理抑制了硝化作用的进行,灭菌效果良好。灭菌处理显著降低了土壤CO2释放量,但相比对照,施用氮肥也使CO2释放量增加了5.3%~17.8%,说明施用氮肥也促进了培养过程中土壤无机碳的释放。因此,应重视大量施用氮肥对石灰性土壤无机碳释放的影响。     

施用等养分量有机肥和化肥对干旱胁迫下玉米生物量影响的比较

  目的  研究干旱胁迫条件下施用有机肥和与之等氮磷钾养分量化肥对玉米生物量的影响及其机制,为玉米抗旱技术措施的提出提供理论依据。  方法  通过温室盆栽模拟试验研究施肥（不施肥、施用牛粪和施用化肥）、微生物（不灭菌和灭菌）和水分（不干旱即田间持水量的70%和干旱即田间持水量的40%）三因素对苗期（45天后）玉米生长及土壤性质的影响。  结果  （1）与不施肥相比,施肥处理显著提高玉米生物量,其中地上部生物量提高了155% ~ 278%,根系提高了71% ~ 122%,总生物量提高了125% ~ 221%;在灭菌条件下,干旱后玉米生物量显著降低（30% ~ 34%）。（2）施肥后,未显著改变土壤无机氮的含量,显著提高了土壤速效磷和速效钾的含量;与正常水分处理相比,干旱仅在有机肥处理下显著降低了土壤速效钾含量,达43.8%;施肥对土壤微生物总生物量和细菌生物量均无显著影响,显著提高了真菌生物量以及真菌和细菌的比值;干旱后,土壤微生物总生物量、细菌和真菌生物量均未发生显著改变。（3）随土壤速效磷含量的增加,玉米总生物量显著增加。  结论  干旱显著降低了苗期玉米生物量,且这种干旱效应仅在灭菌土壤上出现,说明了土壤微生物能够增强植物对干旱胁迫的抗性;在干旱情况下,有机肥施用后玉米生物量显著高于化肥处理,土壤速效磷是主要的驱动因子。     

六六六在土壤中持留和降解

本研究结果表明:(1)六六六在旱地土壤中的持留性一般比稻田土壤高;(2)土壤中六六六残留量的β/γ比值较大;(3)稻田土壤中六六六残留量很低。这主要是由于六六六在稻田土壤中的降解比旱地土壤快得多,以及β-666在土壤中比γ-666更稳定而造成的。实验表明不同作物对土壤中六六六残留量的吸收不同。稻米中六六六残留量与收割时土壤中残留量相关系数等于0.379,没有明显相关;而花生中残留量与土壤中残留量呈极显著相关。实验观察到六六六的降解速率随土壤水份、温度的增加而增加,适量的有机质能促进六六六在土壤中的降解作用。文章讨论了六六六在土壤中降解的可能历程。     

重复用药对土壤中百菌清的降解影响

<正> 重复使用百菌清可抑制土壤中该农药的降解。于灭菌与未灭菌土壤中进行实验发现,百菌清的降解仅发生在未灭菌土壤中。因此认为,是土壤微生物的活动,导致百菌清发生降解。实验还发现,用易腐熟有机物改良土壤,可活化土壤对百菌清的降解能力,这表     

菌渣还田对设施土壤微生物量碳、氮的影响

[目的]探究设施土壤微生物量碳、氮对菌渣还田的响应,为实现设施瓜菜生产的可持续发展提供理论依据和技术支持。[方法]以草菇菌渣为材料,在山东省莘县进行了田间试验,以常规鸡粪还田为对照(CON),设置5个菌渣(FR)还田量,研究菌渣还田对设施土壤有机碳(SOC)、全氮(TN)和微生量碳(MBC)、氮(MBN)的影响。[结果] 5个菌渣还田处理的菌渣使用量分别为15,30,45,60和75 t/hm~2)相比CON增加了SOC和TN。SOC分别增加了12.0%,11.2%,21.6%,33.1%和31.7%,TN分别增加了3.1%,6.3%,19.9%,29.4%和26.4%。除FR_1以外,其他4个菌渣还田处理相比增加了MBC和MBN,MBC分别增加了16.1%,19.9%,36.8%和50.7%,MBN分别增加了3.3%,37.7%,40.4%和60.9%。相比CON,高量菌渣还田处理增加了MBC/SOC和MBN/TN。相关分析表明,MBC,MBN与SOC和TN均呈极显著正相关。[结论]菌渣还田可以提高土壤有机碳、土壤全氮和土壤微生物碳、氮。土壤微生物碳、氮含量随着菌渣还田量的增加而增加,因此菌渣还田是提高设施土壤微生物活性及土壤肥力的有效措施。     

四环素对芘污染农田土壤微生物修复的影响及响应过程

针对城郊农田土壤中多环芳烃和抗生素复合污染的新特征,通过室内模拟土培实验,研究四环素(Tetracycline,TC)胁迫下,降解菌Sphingobium sp.PHE3对长三角典型农田土壤中芘的降解效果和影响机制。研究表明,接种降解菌处理(B)能明显促进土壤中芘的降解,TC的引入可显著抑制土壤中芘的深度降解过程(P0.05)。经过90天培养后,B处理与接菌+添加TC处理(BTC)的降解率分别为40.1%、25.7%,较对照分别提高了23.0倍、14.1倍。通过土壤微生物群落结构多样性分析发现,降解菌数量在经历90天的土壤环境适应期后逐渐快速增加,其数量变化与污染物芘在土壤中含量消减趋势呈负相关;引入芘和四环素对土壤细菌群落结构多样性和功能稳定性具有显著影响(P0.05),然而对土壤真菌群落影响不显著(P0.05)。此外,B和BTC处理条件下,土壤过氧化氢酶活性、荧光素二乙酸酯酶活性和土壤微生物生物量碳氮值显著高于单独添加芘处理(P)和单独添加TC处理(TC),但P处理与TC处理之间无显著差异(P0.05),说明外源污染物(芘或四环素)对于土壤酶活性和微生物生物量碳氮具有显著抑制作用(P0.05),致使降解菌功能作用受到抑制。综上研究结果表明TC可明显抑制土壤中典型四环多环芳烃的微生物降解过程,针对多环芳烃与抗生素复合有机污染农田土壤的微生物强化修复技术有待深入研究。     

Organic matter and aggregation in a degraded potato soil as affected by raw and composted pulp residue

Soils under intensive potato (Solanum tuberosum L.) production are often low in organic matter content and microbial activity. Pulp fibre residue addition may restore the quality of these soils. An experiment was initiated in which raw or composted pulp fibre waste was added to a Fredericton sandy loam (Orthic Humo-Ferric Podzol) in New Brunswick (Canada). Each material was applied at 45 Mg (dry weight) ha^-1 and 90 Mg (dry weight) ha^-1 before planting. Soil was under continuous potato (cv. Russet Burbank) for 3 years. The raw and the composted pulp greatly increased soil organic matter (SOM) content, the C/N ratio, macroaggregation, C mineralization, microbial biomass C (MBC) and enzyme activities for the whole duration of the experiment but had no effect on its total N. Most of the SOM increase was found in the macroorganic matter fraction. The SOM, C/N ratio, macroaggregation, C mineralization and MBC decreased from the time of application. No major difference was found between materials except for CO₂-C release in the incubation which was higher for the composted than for the raw pulp. This study indicated that pulp fibre, either applied raw or composted, increased SOM and macroaggregation and promoted microbial growth and activity in this potato soil which was low in C content. The beneficial effects on soil physical and biochemical properties were still present after 3 years of continuous cropping.     

巴西东北部地区土地退化对土壤微生物量和活性的影响

Land degradation causes great changes in the soil biological properties.The process of degradation may decrease soil microbial biomass and consequently decrease soil microbial activity.The study was conducted out during 2009 and 2010 at the four sites of land under native vegetation(NV),moderately degraded land(LDL),highly degraded land(HDL) and land under restoration for four years(RL) to evaluate changes in soil microbial biomass and activity in lands with different degradation levels in comparison with both land under native vegetation and land under restoration in Northeast Brazil.Soil samples were collected at 0-10 cm depth.Soil organic carbon(SOC),soil microbial biomass C(MBC) and N(MBN),soil respiration(SR),and hydrolysis of fluorescein diacetate(FDA) and dehydrogenase(DHA) activities were analyzed.After two years of evaluation,soil MBC,MBN,FDA and DHA had higher values in the NV,followed by the RL.The decreases of soil microbial biomass and enzyme activities in the degraded lands were approximately 8-10 times as large as those found in the NV.However,after land restoration,the MBC and MBN increased approximately 5-fold and 2-fold,respectively,compared with the HDL.The results showed that land degradation produced a strong decrease in soil microbial biomass.However,land restoration may promote short-and long-term increases in soil microbial biomass.     

Addition of a clay subsoil to a sandy topsoil changes the response of microbial activity to drying and rewetting after residue addition – a model experiment

The effect of drying and rewetting (DRW) on C mineralization has been studied extensively but mostly in absence of freshly added residues. But in agricultural soils large amounts of residues can be present after harvest; therefore, the impact of DRW in soil after residue addition is of interest. Further, sandy soils may be ameliorated by adding clay‐rich subsoil which could change the response of microbes to DRW. The aim of this study was to investigate the effect of DRW on microbial activity and growth in soils that were modified by mixing clay subsoil into sandy top soil and wheat residues were added. We conducted an incubation experiment by mixing finely ground wheat residue (20 g kg^–1) into top loamy sand soil with clay‐rich subsoil at 0, 5, 10, 20, 30, and 40% (w/w). At each clay addition rate, two moisture treatments were imposed: constantly moist control (CM) at 75% WHC or dry and rewet. Soil respiration was measured continuously, and microbial biomass C (MBC) was determined on day 5 (before drying), when the soil was dried, after 5 d dry, and 5 d after rewetting. In the constantly moist treatment, increasing addition rate of clay subsoil decreased cumulative respiration per g soil, but had no effect on cumulative respiration per g total organic C (TOC), indicating that the lower respiration with clay subsoil was due to the low TOC content of the sand‐clay mixes. Clay subsoil addition did not affect the MBC concentration per g TOC but reduced the concentration of K₂SO₄ extractable C per g TOC. In the DRW treatment, cumulative respiration per g TOC during the dry phase increased with increasing clay subsoil addition rate. Rewetting of dry soil caused a flush of respiration in all soils but cumulative respiration at the end of the experiment remained lower than in the constantly moist soils. Respiration rates after rewetting were higher than at the corresponding days in constantly moist soils only at clay subsoil addition rates of 20 to 40%. We conclude that in presence of residues, addition of clay subsoil to a sandy top soil improves microbial activity during the dry phase and upon rewetting but has little effect on microbial biomass.     

添加黏土及植物残体混合物对沙质土壤中呼吸作用和微生物量碳、氮有效性的影响

Crop yields in sandy soils can be increased by addition of clay-rich soil, but little is known about the effect of clay addition on nutrient availability after addition of plant residues with different C/N ratios. A loamy sandy soil(7% clay) was amended with a clay-rich subsoil(73% clay) at low to high rates to achieve soil mixtures of 12%, 22%, and 30% clay, as compared to a control(sandy soil alone) with no clay addition. The sandy-clay soil mixtures were amended with finely ground plant residues at 10 g kg~(-1): mature wheat(Triticum aestivum L.) straw with a C/N ratio of 68, mature faba bean(Vicia faba L.) straw with a C/N ratio of 39, or their mixtures with different proportions(0%–100%, weight percentage) of each straw. Soil respiration was measured over days 0–45 and microbial biomass C(MBC), available N, and p H on days 0, 15, 30, and 45. Cumulative respiration was not clearly related to the C/N ratio of the residues or their mixtures, but C use efficiency(cumulative respiration per unit of MBC on day 15) was greater with faba bean than with wheat and the differences among the residue mixtures were smaller at the highest clay addition rate. The MBC concentration was lowest in sole wheat and higher in residue mixtures with 50% of wheat and faba bean in the mixture or more faba bean. Soil N availability and soil p H were lower for the soil mixtures of 22% and 30% clay compared to the sandy soil alone. It could be concluded that soil cumulative respiration and MBC concentration were mainly influenced by residue addition, whereas available N and p H were influenced by clay addition to the sandy soil studied.     

玉米秸秆不同构件混合分解的非加和效应及其对土壤有机碳矿化的影响

[目的]研究玉米秸秆不同构件混合分解的非加和效应及其对黄绵土土壤有机碳矿化的影响,为秸秆还田背景下坡地土壤CO2排放提供理论支撑。[方法]采用室内模拟试验,试验设置无玉米秸秆土壤对照(CK)及4种玉米秸秆添加处理:茎+土壤(CKS)、叶+土壤(CKL)、鞘+土壤(CKLS)、混合玉米秸秆+土壤(CKM)。[结果]培养结束土壤有机碳矿化累积排放量实测值显著高于预测值,且促进作用主要是由培养初期快速分解阶段(1~28d)导致的。培养结束后混合玉米秸秆剩余质量预测值明显高于实测值,且元素含量发生明显改变,其中全氮含量预测值明显低于实测值,C/N预测值明显高于实测值。培养结束后CKS处理土壤微生物碳含量明显高于其他几种处理,其他几种处理差异不显著;添加玉米秸秆处理土壤微生物量氮明显降低,相应的土壤微生物量C/N增大,CKS,CKL和CKM处理与CK处理差异达到显著水平。土壤可溶性有机碳(DOC)含量CKLS和CKM处理明显高于其他3种处理,CKS与CKL处理与对照差异不显著。[结论]玉米秸秆不同构件按比例混合对玉米秸秆分解产生协同促进作用,混合分解过程促进氮累积。     

Influence of land management on soil nutrients and microbial biomass in the central loess plateau,northwest China

Loss of soil organic matter under cropping systems is often considered one of the most serious forms of agriculturally induced soil degradation. Therefore, understanding how to improve or maintain soil fertility is of importance for sustainable systems of agriculture. This study deals with the effects of succession fallow and fertilization combined with crop rotation on the chemical properties and microbial biomass of soil in the central Loess Plateau, China. In order to create a more uniform experimental environment and avoid the influence of different crop residues, wheat/potato (W/P) rotation was selected as a fertilization treatment. The results showed that with increasing fallow time organic carbon (Corg) and total nitrogen (TN) slightly increased, microbial biomass carbon (MBC) and MBC/Corg gradually decreased, and microbial biomass nitrogen (MBN) remained unchanged. However, only MBC/Corg among all the microbial parameters measured showed significant differences at various stages of fallow. Although there was a decrease in organic carbon and total nitrogen in the fertilized plots, MBC was not significantly different in the various fallow and fertilized plots except for one‐year‐old fallows, which had the highest MBC. MBN, MBC/Corg and MBN/TN in fertilized plots were higher than for plots at different stages of fallow. Fertilization can increase organic carbon, total nitrogen, MBC and MBN content (compared to the control). It was concluded that appropriate land management, such as fertilization combined with crop rotation and reducing one‐year‐old fallow, would be useful ways to improve or maintain soil fertility. Copyright © 2005 John Wiley & Sons, Ltd.