乐果对土壤微生物种群的影响

农药对土壤微生物的影响已成为评价农药对土壤生态安全的一个重要指标。采用室内培养法研究了乐果在3种不同质量分数下对土壤微生物种群数量以及土壤中占优势的细菌、真菌和放线菌生长速率的影响。结果表明,以真菌种群受抑制最大,放线菌次之,细菌最小。在供试质量分数下,该杀虫剂对土壤细菌种群数量的影响较复杂,没有明显规律;对土壤真菌和放线菌种群数量的影响均表现为明显的抑制作用,且随药剂质量分数的提高和加药时间的延长抑制趋势越明显。因此,可以选择真菌和放线菌作为土壤受乐果污染的敏感指示菌。结果同时表明,50～500mg·kg-1的乐果不影响细菌的生长速率,而5000mg·kg-1的乐果在加药后2～5d明显抑制其生长速率,加药后6～7d,又恢复到正常水平;3种不同质量分数的乐果在加药后2～7d对真菌和放线菌的生长速率均表现明显的抑制作用,且随药剂质量分数的提高而逐渐增强,但随加药时间的延长又逐渐恢复。     

皇竹草对土壤阿特拉津的降解特性

为了探明种植皇竹草(Pennisetum hydridum)对土壤阿特拉津降解的促进作用,通过盆栽试验研究了皇竹草对土壤阿特拉津的降解动态、转移特征以及土壤阿特拉津残留浓度与土壤相关酶活性的关系。结果表明:与未种植皇竹草相比,种植皇竹草土壤阿特拉津降解率明显提高,皇竹草对未灭菌和灭菌土壤阿特拉津的降解率分别提高52.84和42.38百分点;与未种植皇竹草处理相比,灭菌和未灭菌条件下种植皇竹草处理阿特拉津在土壤中的半衰期可分别缩短64.35和53.21 d;土壤中阿特拉津被皇竹草吸收后逐步由地下部分向地上部分转移,随着培养时间的延长,转移系数变大;土壤中阿特拉津残留浓度与土壤过氧化氢酶、过氧化物酶、转化酶和多酚氧化酶活性呈显著负相关(P0.05或P0.01)。认为种植皇竹草有助于阿特拉津的降解。     

呋喃丹对海南花岗岩砖红壤微生物种群的影响

在室温下培养土样并采用梯度稀释涂布的方法研究了不同质量分数的呋喃丹对砖红壤中细菌、真菌和放线菌3大主要土壤微生物种群数量变化的影响。结果表明,细菌、真菌和放线菌种群对呋喃丹的反应随其施加质量分数的不同而有所差别。培养初期,5mg·kg-1呋喃丹处理土壤的细菌、真菌、放线菌数量相对最少。而在整个培养周期内随着培养时间的增加,各处理细菌和放线菌数量均能恢复并接近对照水平,但真菌的生长一直受到抑制且呋喃丹质量分数越大其受抑制程度也越大,表明呋喃丹对细菌和放线菌无明显的影响,而抑制真菌的趋势明显。因此,真菌可以被作为海南砖红壤受呋喃丹污染的敏感指示菌。     

土壤中乐果与微生物的相互作用研究

采用室内模拟实验,研究了土壤中乐果与微生物的相互作用.结果表明:(1)50、500、5 000 mg·kg-1的乐果在灭菌土中的降解速度十分缓慢,加药后15d,50 mg·kg-1的降解率为69.3%,500 mg·kg-1的降解率为26.7%,5 000 mg·kg-1的降解率为19.6%.在施过乐果的土壤中的降解速度非常迅速,加药后15d,50 mg·kg-1的降解率为99.7%,500 mg·kg-1的降解率为78.4%,5 000 mg·kg-1的降解率为54.6%.在未施过乐果的土壤中的降解速度则介于二者之间.说明微生物在乐果的降解中起着非常重要的作用,同时,施药可以诱发乐果降解菌的生成从而加速乐果的降解.(2)在各处理的土壤中,50 mg·k-1的乐果对细菌数星有一定的刺激作用,500、5 000 mg·kg-1的乐果抑制细菌的生长.且随质量浓度的升高,抑制作用增强.但随加药时间的延长,又有所恢复.3种不同质量浓度的乐果对土壤真菌和放线菌种群数量的影响均表现为明显的抑制作用,且随药剂质量浓度的提高和加药时间的延长抑制趋势越明显.因此,可以选择真菌和放线菌作为土壤受乐果污染的敏感指示菌.(3)在同样处理条件下,施过乐果土壤中的微生物种群数量并不比未施过乐果土壤中的占优势,表明乐果在施过药的土壤中降解速度的加快并不是由微生物的数量决定的,而是由它们的降解能力决定的.     

超积累植物和化学改良剂联合修复锌镉污染土壤后的微生物特征

通过盆栽试验,观察分析不同的土壤改良配方对重金属超积累植物东南景天盆栽土壤中细菌、真菌和放线菌数量、Cmic及Nmic的影响,以此来筛选出最优的促进东南景天修复锌镉污染土壤的改良剂配方。结果显示:细菌、真菌和放线菌数量,与土壤Zn、Cd的去除率、东南景天植株干质量、Cmic及Cmic/Nmic两两之间都呈现极显著正相关关系(但Cmic/Nmic与真菌数量仅呈显著相关)。添加了土壤改良剂后,细菌、放线菌、真菌的数量都有不同程度的增加,其中以细菌数量的增加最为显著,放线菌次之,真菌则对各种土壤处理相对较不敏感;在各种土壤配方中,添加了6 g赤泥、15 g污泥和15 g沸石的T7处理最有利于各类土壤微生物的生长,微生物量碳达到345.64 mg.kg-1,与其它处理之间都达到显著差异。因此,可以利用土壤微生物作为污染土壤改良情况的生物指标。该研究为下阶段研究化学改良剂-植物-微生物修复技术奠定了基础。     

返青前后草地早熟禾草坪根际微生物区系动态

根际是土壤-植物生态系统物质及能量交换的活跃界面,根际微生物不仅直接影响植物对水分、养分的吸收,而且也同时影响植物对不良环境的抵抗能力。利用选择性培养基对草地早熟禾(PoapratensisL.)返青前后根际与非根际的细菌、真菌以及放线菌类群进行分离测数,拟从根际及非根际土壤微生物区系动态变化方面来阐述草地早熟禾返青前后其根际微生态的变化规律。结果表明:(1)草地早熟禾草坪的返青后,根际及非根际细菌、真菌数量明显增加,但放线菌数量呈减少趋势;(2)无论返青前后或者根际以及非根际,细菌的数量都占整个土壤微生物量的绝大部分,细菌数量的变化代表了整个微生物类群数量的变化趋势,使得草地早熟禾返青后根际土壤由"真菌型"向"细菌型"转化;(3)返青前后,各微生物类群都表现出明显的根际效应。     

模拟酸雨与重金属复合胁迫对绞股蓝生长及根际微生物的影响

通过盆栽试验研究了不同pH值的模拟酸雨与Zn(30和400 mg.kg-1)、Cd(1和15 mg.kg-1)单独或复合胁迫对绞股蓝(Gynostemma pentaphyllum)药用成分——总皂甙含量以及根际土壤微生物数量和组成的影响。结果表明:不同pH值的模拟酸雨均能抑制细菌、放线菌、氮素生理类群的生长,其数量随酸雨pH值的降低而不断减少;真菌、纤维素分解菌数量随酸雨pH值的降低呈先升高后降低的变化趋势;绞股蓝茎叶总皂甙含量随酸雨pH值的降低而降低。酸雨影响下,单施低浓度的Zn(30 mg.kg-1)或Cd(1 mg.kg-1)时,根际3大类群微生物、氮素生理类群、纤维素分解菌、绞股蓝总皂甙含量均高于无重金属处理;但当Zn(400 mg.kg-1)或Cd(15 mg.kg-1)处于高浓度时,它们又明显低于无重金属处理。酸雨影响下,Zn(30 mg.kg-1)或Cd(1 mg.kg-1)为低浓度水平时,Zn-Cd复合污染对根际3大类群微生物、氮素生理类群、纤维素分解菌、绞股蓝茎叶总皂甙含量影响表现为拮抗效应;Zn(400 mg.kg-1)或Cd(15 mg.kg-1)为高浓度水平时,Zn-Cd复合污染对根...     

Arthrobacter sp.AD30和Pseudomonas sp.AD39在阿特拉津工业废水生物处理及污染土壤生物修复中的应用

将分类地位和降解特性不同的两个高效降解除草剂阿特拉津的菌株Arthrobacter sp.AD30和Pseudo-monas sp.AD39,用于阿特拉津工业废水的生物处理和污染土壤的生物修复试验.填充聚氨酯泡沫的小型生物反应器阿特拉津降解实验表明,在进水的CODCr为1702 mg·1-1、阿特拉津浓度为133 mg·1-1和水力停留时间(HRT)为24 h的条件下,出水的CODCr稳定在100 mg·1-1以下,阿特拉津浓度在0.2 mg·1-1以下,均达到国家工业水污染物排放标准(GB 21523-2008).土壤的生物修复实验表明,含有200 mg·kg-1阿特拉津的土壤接种上述两个菌株,在30℃处理20 d以后,土壤中99.1%的阿特拉津被去除.这些结果表明,由AD30和AD39组成的混合菌株在工业废水的生物处理和污染土壤的生物修复中具有很好的应用潜力.     

青海省保护地辣椒根际土壤和根表放线菌研究

采用常规方法研究了青海省大棚和温室中辣椒健株、病株根际土壤和根表的微生物数量、放线菌组成及拮抗性放线菌的分布。结果表明：（1）青海保护地辣椒根际土壤和根表微生物以细菌为主，放线菌次之，真菌最少，三者数量之比为10^5：1：1(根表）；（20根际微生物数量和土壤速效N、P、K含量密切相关，速效养分含量高的土壤中微生物数量大。辣椒病株根际土坟和根表细菌、放线菌及真菌三大类微生物数量显著高于健株。（3）保护地辣椒根际土壤和根表放线菌组成较复杂，共分离到了7个属的放线菌，但仍以链霉菌为主，其次为小单孢菌和马杜拉放线菌。链霉菌可分为10个类群，金色类群占优势。健株根际土壤和根表放线菌组成较病株复杂，而链霉菌组成较病株简单。（4）供试放线菌菌株中9.0%对G^ 细菌有拮抗活性，6.7%对真菌有拮抗活性，对G^-细菌均无拮抗作用，健株根际土壤拮抗性放线放菌数量及其占放线菌总数的比例均高于病株，健株根表拮抗笥放线菌占放线菌总数的比例亦高于病株，表明根际土壤中拮抗性放线菌的数量及根际和根表拮抗性放线菌占放线菌总数的比例是决定辣椒是否染病的关键因素之一。表4参11。^^^^^^^^^     

抗虫-耐除草剂转基因玉米种植对根际土壤细菌和真菌群落的影响

全生育期种植抗虫基因cry1Ab/cry2Aj和耐除草剂基因G10evo-spsps的转基因玉米及其亲本非转基因玉米,采用定量聚合酶链式反应(PCR)和高通量测序技术,测定玉米拔节期和成熟期根际土壤细菌和真菌群落数量、组成及多样性,研究种植抗虫耐除草剂转基因玉米对根际土壤微生物的影响。结果表明,种植转基因玉米未显著影响根际土壤理化性质、土壤荧光素二乙酸酯水解酶活性、微生物群落丰度及多样性;在门水平上,种植转基因玉米仅显著提高2个生长时期根际土壤细菌放线菌门(Actinobacteria)相对丰度;在属水平上,种植转基因玉米均显著降低2个生长时期根际土壤细菌Candidatus_Nitrososphaera相对丰度;种植转基因玉米未影响真菌门水平相对丰度,但影响根际土壤真菌Fusarium、Staphylotrichum和Lophiostoma属相对丰度。另外,生长时期显著影响根际土壤可溶性有机碳和全氮含量,也显著影响根际土壤细菌群落组成和多样性,但未显著影响根际土壤真菌群落组成和多样性。该研究旨在为转基因作物产业化的自然生态风险管理和控制提供基础数据和理论支撑。     

阿特拉津在土壤中的降解途径及其对持留性的影响

通过田间和实验室试验，研究了除草剂阿特拉津在土壤中的降解代谢规律及其与土壤特性的关系。试验表明，阿特拉津施用后、在作物生长期内可降解９０％以上，土壤酸碱度对阿特拉津在土壤中的代谢有显著影响。在碱性土壤中阿特拉津主要经过微生物代谢而被降解；在酸性土壤中化学水解占优势地位。阿特拉津在强酸性土壤中的持留性（半衰期为６３ｄ）低于弱酸性土壤中的持留性（半衰期为８４ｄ），而在碱性土壤中由于较强的微生物降解作用，其持留性（半衰期为５１ｄ）最低。     

Investigation of the effects of humic acid and H 2 O 2 on the photocatalytic degradation of atrazine assisted by microwave

A solution of atrazine in a TiO₂ suspension, an endocrine disruptor in natural water, was tentatively treated by microwave-assisted photocatalytic technique. The effects of mannitol, oxygen, humic acid, and hydrogen dioxide on the photodegradation rate were explored. The results could be deduced as follows: the photocatalytic degradation of atrazine fits the pseudo-first-order kinetic well with k = 0.0328 s⁻¹, and ·OH was identified as the dominant reactant. Photodegradation of atrazine was hindered in the presence of humic acid, and the retardation effect increased as the concentration of humic acid increased. H₂O₂ displayed a significant negative influence on atrazine photocatalysis efficiency. Based on intermediates identified with gas chromatography-mass spectrometry (GC-MS) and Liquid chromatography-mass spectrometry (LC-MS/MS) techniques, the main degradation routes of atrazine are proposed.     

Investigation of the effects of humic acid and H<Subscript>2</Subscript>O<Subscript>2</Subscript> on the photocatalytic degradation of atrazine assisted by microwave

A solution of atrazine in a TiO₂ suspension, an endocrine disruptor in natural water, was tentatively treated by microwave-assisted photocatalytic technique. The effects of mannitol, oxygen, humic acid, and hydrogen dioxide on the photodegradation rate were explored. The results could be deduced as follows: the photocatalytic degradation of atrazine fits the pseudo-first-order kinetic well with k = 0.0328 s^?1, and ·OH was identified as the dominant reactant. Photodegradation of atrazine was hindered in the presence of humic acid, and the retardation effect increased as the concentration of humic acid increased. H₂O₂ displayed a significant negative influence on atrazine photocatalysis efficiency. Based on intermediates identified with gas chromatography-mass spectrometry (GC-MS) and Liquid chromatography-mass spectrometry (LC-MS/MS) techniques, the main degradation routes of atrazine are proposed.     

阿特拉津对不同肥力土壤磷酸酶的影响

通过室内恒温培养法，研究除草剂阿特拉津对4种长期定位施肥处理下的土壤的磷酸酶活性的影响。试验结果表明，在阿特拉津质量分数不同和处理时间长短不同的情况下，阿特拉津对土壤磷酸酶的活性既有激活作用又有抑制作用。在试验过程中，4种不同肥力的土壤其磷酸酶活性随着处理时间的延续而呈现出“降低→升高→降低→升高”的消长趋势。不同阿特拉津质量分数对磷酸酶的影响没有规律，同一质量分数处理既有激活作用，也有抑制作用。在4种不同肥力的土壤中，磷酸酶活性最高的是以氮、磷、钾无机肥配合有机肥施用的土壤。     

狼尾草根系对阿特拉津长期胁迫的氧化应激响应

通过盆栽实验研究了抗性植物狼尾草根部丙二醛(MDA)、脯氨酸(Pro)、抗坏血酸(As A)含量及超氧化物歧化酶(SOD)、谷胱甘肽还原酶(GR)等氧化应激生理指标对不同浓度阿特拉津长期(48 d)胁迫的响应规律。结果表明:当阿特拉津胁迫浓度分别高于20 mg·kg~(-1)和50 mg·kg~(-1)时,狼尾草根系的MDA与Pro含量较对照组显著升高(P0.05);随着阿特拉津胁迫浓度的增加,狼尾草根部SOD和GR活性呈先升高后降低的趋势,其中当阿特拉津胁迫浓度为20 mg·kg~(-1)时,SOD和GR活性达到最大值;供试植物根系中As A含量与阿特拉津胁迫浓度呈正相关。综上,中低浓度(≤20 mg·kg~(-1))阿特拉津处理没有对狼尾草的根系产生明显的氧化胁迫效应,狼尾草根系的上述抗氧化应激生理指标对于发挥阿特拉津抗性起着重要的作用。     

Extractable atrazine and its metabolites in agricultural soils from the temperate humid zone

Extractable atrazine and its metabolites (hydroxyatrazine, deethylatrazine and deisopropylatrazine) were evaluated in agricultural soils from the temperate humid zone (Galicia, NW Spain) under laboratory conditions. The experiment was performed with five soils with different properties (organic C, soil texture and atrazine application history), both unamended and treated with atrazine at field application rate. Measurements of the atrazine compounds were made at different time intervals (1, 3, 6, 9 and 12 weeks) during a 3-month incubation period. Results showed that only hydroxyatrazine was detected in the extractable fraction of the unamended soils, with values remaining relatively constant throughout the incubation period. Atrazine addition notably increased the concentration of the parent compound and its degradation products; deisopropylatrazine and hydroxyatrazine were the main metabolites detected in the extractable fraction of the treated soils, whereas deethylatrazine was not detected. After 7 days incubation, values of total extractable residues, expressed as percentage of initially added atrazine, ranged from 75 to 86% (25–68% of atrazine, 7–11% of hydroxyatrazine and 9–57% of deisopropylatrazine). The values decreased rapidly during the first 3 weeks of incubation, showing values of 2–8% in soils with higher atrazine application and from 28 to 30% in soils with lower application history. At the end of the incubation, 2–8% of total extractable residues were still detected (0–4% of atrazine, 2–3% of hydroxyatrazine and 0–2% of deisopropylatrazine), indicating a residual effect of atrazine addition. These variations in the extractable fraction indicated that most added atrazine was rapidly degraded, especially in soils with higher application history.     

Study of atrazine degradation in soil from Kenyan sugarcane-cultivated fields in controlled laboratory conditions

A study to compare the extent of atrazine mineralization in soils from Kenyan sugarcane-cultivated fields with and without history of atrazine use was carried out in the laboratory under controlled conditions. The study was testing the hypothesis that repeated atrazine application to soil will not result in enhanced atrazine mineralization. The study was carried out with ¹⁴C-uniformly ring-labeled atrazine in a laboratory under controlled conditions. Atrazine mineralization to ¹⁴CO₂ in soil with no history of atrazine use was negligible (0.16%) after 163 days of soil incubation. The three metabolites hydroxyatrazine, desisopropylatrazine, and desethylatrazine in the proportion of 17.7%, 1.3%, and 2.6%, respectively, were in the soil after 75 days. In the soil from the sugarcane-cultivated field with history of atrazine use, atrazine mineralization was 89.9% after 98 days. The same soil, amended with mature compost, showed a lag phase of eight days before rapid atrazine mineralization was observed.     

Toxicity,degradation and analysis of the herbicide atrazine

Excessive use of pesticides and herbicides is a major environmental and health concern worldwide. Atrazine, a synthetic triazine herbicide commonly used to control grassy and broadleaf weeds in crops, is a major pollutant of soil and water ecosystems. Atrazine modifies the growth, enzymatic processes and photosynthesis in plants. Atrazine exerts mutagenicity, genotoxicity, defective cell division, erroneous lipid synthesis and hormonal imbalance in aquatic fauna and nontarget animals. It has threatened the sustainability of agricultural soils due to detrimental effects on resident soil microbial communities. The detection of atrazine in soil and reservoir sites is usually made by IR spectroscopy, ELISA, HPLC, UPLC, LC–MS and GC–MS techniques. HPLC/LC–MS and GC–MS techniques are considered the most effective tools, having detection limits up to ppb levels in different matrices. Biodegradation of atrazine by microbial species is increasingly being recognized as an eco-friendly, economically feasible and sustainable bioremediation strategy. This review presents the toxicity, analytical techniques, abiotic degradation and microbial metabolism of atrazine.     

乙草胺和莠去津对土壤微生物的影响及安全性评价

采用密闭法测定了乙草胺和莠去津对土壤微生物呼吸作用的影响，并对其使用的环境安全性进行了评价。结果表明，乙草胺和莠去津对土壤微生物基本无影响；它们对土壤微生物的安全性属于低毒级或无实际危害级农药。     

吸附反应时间对除草剂阿特拉津吸附行为的影响

采用批量动态实验方法,对潮土中阿特拉津吸附特征随吸附反应时间变化进行了研究。结果表明,土壤吸附的阿特拉津量随反应时间的变化符合双曲线函数关系。在50μg·L-1～2000μg·L-1浓度系列下,在48h内,土壤颗粒对阿特拉津的吸附属于快反应,土壤吸附的阿特拉津量随吸附反应时间呈指数上升,为吸附实验结束(168h)时土壤吸附阿特拉津总量的58%到90%。当吸附反应时间超过48h后,随反应时间增加,土壤吸附阿特拉津量差异变化不显著。阿特拉津在潮土颗粒和土壤溶液中的相分配可用Freundlich方程描述。吸附容量因子Kf与吸附反应时间之间有极显著的线性正关系(r2=0.9063**,p<0.0001)。无量纲的非线性因子n与吸附反应时间之间也具有显著的线性负关系(r2=0.5666*,p=0.0192)。