阿特拉津降解菌ATR3的分离鉴定与土壤修复

阿特拉津因效率高、价格低廉,是我国玉米田施用最广泛的除草剂之一,但其结构稳定,残留时间长,因此对生态环境和人类健康造成了一定的危害。从长期受阿特拉津污染的玉米田土壤中筛选并鉴定阿特拉津降解菌,明确其在不同类型土壤中的去除能力。对分离出的阿特拉津降解菌ATR3进行生理生化分析和16S rRNA序列鉴定,确定菌株ATR3为节杆菌属（Arthrobacter sp.）。该菌株以阿特拉津为唯一氮源,培养48 h后对1 000 mg/L阿特拉津的去除率达到97%以上。敏感作物盆栽试验结果表明,阿特拉津在棕壤上去除最快,褐土次之,黑土最慢,说明阿特拉津在土壤中的去除过程与土壤本身的理化性质呈相关关系。同时,该菌株处理14 d后,能明显恢复玉米的各项生物学指标,说明该菌株对阿特拉津污染土壤具有良好的修复能力。为阿特拉津降解菌剂的推广利用提供参考。     

除草剂阿特拉津对土壤脲酶活性的影响

研究了阿特拉津对4种典型施肥处理的土壤脲酶活力的影响。结果表明,处理初期,低浓度阿特拉津对土壤脲酶有一定刺激作用,高浓度处理在整个试验过程中对脲酶有明显抑制作用,阿特拉津对不同肥力土壤中脲酶的影响有明显差异,对照土壤和NPK肥土壤中脲酶活力较低,脲酶受抑制明显,抑制率分别高达30．35％和28．89％;NPK+秸秆和NPK+有机肥土壤的脲酶活力高,脲酶抑制率低,最高抑制率分别为21．35％和16．86％,不同肥力土壤在整个处理过程中,脲酶抑制率均为先逐渐增大到最大值,然后又逐渐降低;高肥力土壤脲酶抑制率最大值出现的时间比低肥力土壤迟,表明高肥力土壤对阿特拉津有较强的耐受能力。     

阿特拉津降解菌T_3 AB_1的分离鉴定及土壤修复

【目的】从阿特拉津污染土壤分离高效降解菌株,进行分类学鉴定、降解特性及黑土修复能力初步研究,为阿特拉津污染土壤微生物修复提供新的菌株。【方法】通过形态特征、生理生化特征和16S rDNA序列分析方法进行菌株鉴定;通过培养时间、温度、pH值等环境因素的研究得出菌株的最佳降解条件;通过降解菌株接种于不同种类除草剂为唯一碳氮源培养基获得该菌株的降解谱;通过土壤接种和敏感作物盆栽生测试验验证菌株对阿特拉津污染土壤修复能力。【结果】本试验从黑龙江省讷河市长期施用阿特拉津的玉米田地中分离出一株能以阿特拉津为唯一碳氮源生长的细菌T3AB1,初步鉴定为节杆菌属(Arthrobacter sp.),该菌株在72 h内对500 mg/L阿特拉津(pH 8.0)的降解率高达99%,其降解能力较高的条件为pH7.0-8.0、25-30℃、摇培72-108 h,该菌株能够利用甲氧咪草烟、咪唑乙烟酸、氟磺胺草醚、氟乐灵、异噁草松为唯一碳氮源进行生长,处理168 h的降解率能够达到12.66%-40.54%,该菌株处理21 d能够显著恢复敏感作物水稻的各项生物量指标,且随着处理时间的延长,其对土壤的修复作用也会逐渐增强。【结论】从黑龙江省污染土壤中筛选得到的高效降解阿特拉津的节杆菌属近缘种T3AB1,土壤接种实验表明该菌株具有很好的土壤修复作用,可为阿特拉津生物修复的研究提供适宜菌种资源。     

阿特拉津降解菌SA1的分离鉴定及其降解特性研究

为进行阿特拉津(AT)污染的生物修复,从AT降解混合菌群中,经长期的交替液体摇瓶培养和平板划线分离,筛选到一株能完全降解AT的菌株SA1。经生理生化特征及16S rDNA序列分析,将该菌鉴定为假单胞菌属(Pseudomonas sp.)。与已报道的AT降解菌Pseudomonas sp.ADP不同,SA1能以AT为唯一碳源、氮源和能源生长,培养基中添加铵盐不抑制SA1的降解功能,而添加葡萄糖时,累积的氰尿酸会被快速降解。SA1生长的最适温度为37℃,最适pH值为7.0。SA1的静息细胞在10℃~40℃或pH值4~11时均能高效降解AT,比ADP降解具有更广的pH和温度范围,表明SA1降解菌株具有广阔的应用前景。SA1中AT降解基因为保守的atzABCD,并含有IS1071的tnpA基因片段,传代过程中降解基因会以一定频率丢失。     

一株阿特拉津降解菌的分离鉴定及降解特性

从农药厂废水处理池的活性污泥中分离到一株阿特拉津降解菌X-4, 根据其生理生化特性和16S rRNA基因序列相似性分析, 将其初步鉴定为节杆菌属(Arthrobacter sp.)。该菌能以阿特拉津为唯一碳氮源生长, 42 h内对100 mg/L的阿特拉津降解效果为95.7%, 降解阿特拉津的最适温度为30 °C, pH为7.0。该菌对多种重金属离子都存在抗性, 显示了其在去除阿特拉津和重金属复合污染方面的应用潜力。对其降解基因的初步研究显示, 该菌含有trzN、atzB和atzC 3个阿特拉津降解相关基因。     

阿特拉津降解菌株的分离和鉴定

从农药厂废水中分离到6株能以除草剂阿特拉津为唯一氮源生长的细菌,即假单胞菌（Pseudomonas spp,.)AD1,AD2和AD6,土壤杆菌（Agrobacterium sp.)AD4,黄单胞菌（Xanthomonas sp.)AD5,欧氏菌（Erwinia sp.)AD7,AD1菌株能使无机盐培养基中的0．3g/L阿特拉津在72h内降解99．9％,当以AD1,AD2,AD4,AD5,AD6和AD7菌株的总DNA为模板进行PCR扩增时,除AD2菌株以外,均得到了与献报道的假单胞菌ADP菌株的阿特拉津氯水解酶基因（atzA)同源的PCR产物。     

阿特拉津降解菌株AD111的分离鉴定及其降解特性

【背景】玉豆轮作过程中,玉米田中长残留除草剂阿特拉津易对下茬大豆作物产生不良影响。【目的】从黑龙江省安达市的农田土筛选一株能适应该土壤环境生长的阿特拉津降解菌并研究其降解特性。【方法】利用富集培养法,分离、筛选一株阿特拉津高效降解菌并结合外观形态、生理生化及16SrRNA基因序列测定对其进行鉴定,通过单一变量法设置不同的碳源、pH、温度和阿特拉津浓度,研究降解菌株最佳发酵及降解条件。【结果】得到一株在BSM-G中能够以阿特拉津为唯一氮源生长的高效阿特拉津降解菌AD111,鉴定为马德普拉塔无色小杆菌(Achromobacter marplatensis)。菌株AD111降解阿特拉津的最适温度为35℃,最适pH为8.0,最佳碳源为蔗糖,24 h内对浓度为50 mg/L的阿特拉津降解率达到99.7%,对300 mg/L的阿特拉津降解率达到81.9%。【结论】降解菌AD111具有较好的环境适应及阿特拉津降解能力,为解决黑龙江偏碱土壤中阿特拉津残留提供了良好的候选菌株。     

基因工程菌对阿特拉津的生物转化及其影响因素

研究考察了基因工程菌转化阿特拉津的共代谢碳源、转化动力学和影响因素。结果表明,作为共代谢碳源,葡萄糖优于乙酸盐,碳源浓度对转化影响不大,对工程菌生长影响显著。阿特拉津比转化速率与工程菌初始密度无关,与阿特拉津初始浓度有关,用Monod方程拟合转化动力学,求得方程参数为V_(max)=0．168/h,Ks= 30．49mg/L。降低温度会显著降低阿特拉津比转化速率;偏碱性的条件下,阿特拉津转化率较高,酸性条件严重抑制阿特拉津转化;盐度在一定范围内不影响转化活性;Co~(2 )、Fe~(2 )、Fe~(3 )和Zn~(2 )促进阿特拉津转化,Mn~(2 )、Ni~(2 )和Cu~(2 )抑制阿特拉津转化。菌体细胞对阿特拉津的吸附和转化作用呈正相关关系。     

工业废水中阿特拉津降解细菌的遗传和生理多样性

【目的】通过遗传学和生理学实验,揭示分离自工业废水的阿特拉津降解细菌具有遗传和生理多样性,为阐明阿特拉津生物降解的分子机理和阿特拉津降解细菌在污染环境生物修复中的应用提供新见解。【方法】用普通PCR方法检测菌株的阿特拉津降解基因,分析其降解基因组成;用基因组重复序列PCR技术(rep-PCR)分析降解菌株的基因组类型;用Western blot方法检测菌株阿特拉津降解途径的第一个酶三嗪水解酶(TrzN);用不同氮源(阿特拉津、莠灭净、扑草净、西玛津、氰草净、阿特拉通和氰尿酸)和碳源(蔗糖、葡萄糖、麦芽糖、乳糖、柠檬酸钠、乙酸钠和琥珀酸钠)培养降解菌株,通过检测培养液的OD600值,证明菌株能够利用的氮源和碳源种类。【结果】对分离自工业废水的27个阿特拉津降解菌株所进行的阿特拉津降解基因PCR检测表明,其降解基因组成分别为trzN-atzBC、trzN-atzABC和atzADEF;通过rep-PCR实验将27个阿特拉津降解菌株分为7个群;Western blot结果表明,27个菌株中有24个含有三嗪水解酶TrzN;氮源利用实验表明,2个菌株能够利用所有7种氮源生长,其余25个菌株只能利用其中的2-6种;碳源利用实验表明,10个菌株能够利用所有7种碳源生长,其余17个菌株只能利用其中的3-6种。【结论】分离自某工业废水的27株阿特拉津降解功能菌存在相当广泛的遗传和生理学上的多样性,trzN-atzABC降解基因组成为首次发现。     

基于XGBoost模型的土壤中阿特拉津降解预测

利用自动机器学习方法建立预测土壤中除草剂阿特拉津降解效率的最佳模型,可评估土壤中阿特拉津的残存风险。本研究收集了49篇已发表文献中的494对数据,选择土壤pH、有机质含量、饱和导水率、土壤湿度、阿特拉津初始浓度、培养时间和接菌量7个因素作为输入特征,以阿特拉津在土壤中的一级反应速率常数作为输出特征,建立了6种预测土壤中阿特拉津降解效率的模型。通过线性回归和相关评价指标对模型性能进行综合分析。结果表明：XGBoost模型在预测一级反应速率常数(k)方面性能表现最佳。基于预测模型获得各因素的特征重要性排名,依次为土壤湿度>培养时间>pH>有机质>阿特拉津初始浓度>饱和导水率>接菌量;应用SHAP解释各特征与土壤中阿特拉津降解能力间的潜在联系以及各特征贡献度发现,时间对k有负贡献,而饱和导水率则对k有正贡献。土壤湿度、阿特拉津初始浓度、pH、接菌量和有机质含量的高值普遍分布在SHAP=0两侧,说明它们对土壤中阿特拉津降解存在复杂贡献。XGBoost模型结合SHAP方法在预测k性能和可解释性方面具有较高的准确性。通过机器学习方法,充分挖掘历史试验数据的价值,...     

The variability of soil microbial community composition of different types of tidal wetland in Chongming Dongtan and its effect on soil microbial respiration

Previous studies have shown that the soil enzyme activity and microbial respiration intensities varied in two different types of tidal wetland in Chongming Dongtan, the first a sandy soil in a scouring bank with Phragmites australis and the second a saline-alkali clay soil in silting bank with P. australis/Spartina alterniflora/Scirpus mariqueter, resulting in different organic carbon reservation capabilities; however, their microbial biomass did not differ significantly. To clarify the microbial mechanism that explains the variability of soil respiration among different wetland areas, the community structure and abundance of soil microorganisms in different types of wetland were investigated using denaturing gradient gel electrophoresis (DGGE) plus real-time quantitative polymerase chain reaction (PCR) technologies, and the relationship between soil environmental factors and the microbial community structure and the soil respiration intensity was elucidated. The results revealed that the soil microbial diversity and community structure differed between the two typical wetland areas. The common population was uncultured bacterium in both areas, and the most abundant community was α-, β-, γ-Proteobacteria, which play an important role in the cycling of carbon in soil. However, the abundance of α-Proteobacteria in Area A was 18.2% of that in Area B (P <0.05), while the β-Proteobacteria in Area A was 3.23 times higher than that in Area B (P <0.05). In addition, one cellulose-degrading bacteria, uncultured Bacilli, was detected in Area A. PCA (Principal component analysis) revealed that γ-Proteobacteria and β-Proteobacteria had the greatest impact on soil respiration intensity. Both soil water content and salinity depressed the propagation of β-Proteobacteria. Considering the similar microbial biomass and abundance of γ-Proteobacteria between the two areas, the lower level of β-Proteobacteria, uncultured Bacilli bacterium in Area B might be important factors involved in the lower soil respiration, and hence the higher soil organic carbon reservation capability in Area B.     

恩诺沙星残留对土壤细菌种群基因多样性的影响

为了解恩诺沙星在环境中残留对土壤微生物的影响,应用扩增核糖体DNA限制性分析(ARDRA)对土壤细菌16S rDNA基因多样性进行了研究,并结合肠杆菌基因间的重复共有序列(ERIC-PCR)指纹图谱分析了恩诺沙星对土壤细菌种群基因多样性的影响.结果表明: 恩诺沙星作用于土壤后第35天,添加药物组的细菌总数均低于对照,且药物浓度越高,细菌数量越少;ARDRA分析将分离的土壤细菌分成了不同的操作分类单元(OTU),各组的OTUs类型数分别为：Ⅰ组15个、Ⅱ组13个、Ⅲ组10个、Ⅳ组8个、Ⅴ组6个、Ⅵ组6个;对各组优势OTU进行了ERIC-PCR基因指纹图谱分析,Ⅰ～Ⅵ组的Shannon-Wiener指数分别为2.78、2.14、1.78、1.11、0.69和0.31,对照组的Margalef指数、Simpson指数和Pielou指数均明显高于添加药物组,且各多样性指数随药物浓度的增加而减少.     

稀土元素对土栖动物群落结构的影响及对蛴螬的生态毒性

采用土施法和OECD推荐的滤纸接触法研究了稀土(ReCl₃·6H₂O)对豆田土栖动物群落结构的影响以及稀土对蛴螬的生态毒性.结果表明,对照与各处理之间动物种类数、主要动物种群数量、多样性指数差异均不显著;急性和慢性毒性试验表明,对照与各处理间的死亡率差异不显著.在稀土有效施用范围内,稀土对蛴螬的生态毒性很小,不会明显改变蛴螬种群结构.     

Broad-scale analysis of soil microbial community DNA from Upland grasslands

We have applied a broad-scale approach to the analysis of DNA extracted from soils which support characteristic grasslands at an upland site in the UK. To test for the degree of coherence between microbial and vascular communities, grasslands were characterised as improved, semi-improved, or unimproved, according to the degree of management they had received and consequent botanical composition. Microbial DNA was extracted directly from the grassland soils and analysed by three techniques: (i) thermal denaturation, which profiles the guanine and cytosine (G÷C) base distribution within the community; (ii) cross hybridisation of the DNA which measures the degree of similarity between the samples; (iii) measurement of reassociation kinetics of denatured DNA, which provides a measure of the complexity of the DNA. Thermal denaturation revealed significant differences in the %G+C composition of the communities. DNA from the improved soil had the highest median %G+C value, whilst that from the unimproved soil had the lowest. The relative distribution of G+C bases also differed significantly between the samples from the three grasslands. Cross hybridisation of DNA from the different soils also indicated significant differences in the degree of similarity between the DNA from the grasslands, with unimproved showing 59% similarity to improved. Indices from the cross hybridisation assay suggested that, in terms of complexity, the samples ranked unimproved > semi-improved > improved. Reassociation kinetics supported this conclusion, but the rates of reassociation were such that less than 40% reassociation occurred over a 31-day period, thus preventing calculation of C _o t_1/2.     

Fungal degradation of chlorpyrifos by Verticillium sp. DSP in pure cultures and its use in bioremediation of contaminated soil and pakchoi

Pesticides residues in soils and on vegetables are a public safety concern. Pretreatment with microorganisms degrading pesticides has the potential to alleviate the conditions. For this purpose, the degradation characteristics of chlorpyrifos by an isolated fungal strain Verticillium sp. DSP in pure cultures, soil, and on pakchoi (Brassica chinensis L.) were investigated. Degradation rate of chlorpyrifos in the mineral salts medium was proportional to the concentrations of chlorpyrifos ranging from 1 to 100 mg l⁻¹. The rate of degradation for chlorpyrifos (1 mg l⁻¹) in the mineral salts medium was 1.12 and 1.04 times faster at pH 7.0 than those at pHs 5.0 and 9.0, and the degradation at 35 °C was 1.15 and 1.12 times faster, respectively, than those at 15 and 20 °C. The addition of the fungal strain DSP into the contaminated soils was found to significantly increase the degradation of chlorpyrifos. Degradation rates of chlorpyrifos in inoculated soils were 3.61, 1.50 and 1.10 times faster in comparison with the sterilized soil, previously chlorpyrifos-untreated soil, and previously chlorpyrifos-treated soil under laboratory conditions. In contrast to the controls, the half-lives of chlorpyrifos were significantly shortened by 10.9% and 17.6% on treated pakchoi, 12.0% and 37.1% in inoculated soils, respectively, in the greenhouse and open field. The results indicate that the fungal strain DSP can be used successfully for the removal or detoxification of chlorpyrifos residues in/on contaminated soil and vegetable.     

玉米秸秆还田对黑土微生物群落功能多样性的影响

为了解玉米秸秆还田对土壤微生物群落功能多样性的影响,采用ECO-Biolog微平板法,分析了以无玉米秸秆还田为对照(CK),6000 kg·hm^-2(S1)、9000 kg·hm^-2(S2)、12000 kg·hm^-2(S3)和15000 kg·hm^-2(S4)四个秸秆还田量的土壤微生物碳源代谢特征。结果表明:随着玉米秸秆还田量的增加,土壤微生物平均颜色变化率(AWCD)也随之增加,24~96 h的AWCD值变化迅速,96 h后进入平稳期,S4处理AWCD值始终大于其他处理;秸秆还田对Shannon指数与Simpson指数没有显著影响(P>0.05),但与CK相比,S4处理McIntosh指数显著增加了57.5%(P<0.05);主成分分析结果显示,秸秆还田影响着土壤微生物群落碳代谢能力,S1、CK、S2和S3处理在PC1和PC2上出现显著的分异,糖类、多聚物类、羧酸类碳源是研究区域内土壤微生物利用的主要碳源。因此,在东北黑土区增加玉米秸秆还田量能够提高土壤微生物对碳源的利用能力,提升黑土肥力。     

Biodegradaon of phenanthrene in soil microcosms stimulated by an introduced Alcaligenes sp.

Abstract A phenanthrene degrading strain of Alcaligenes sp. was isolated from oil polluted soil. Addition of Alcaligenes sp. to soil microcosms supplemented with phenanthrene (1 mg/g dry soil) resulted in degradation of the added phenanthrene within 11 days. The phenanthrene concentration declined only 12% in uninoculated soil during 42 days. The total phenanthrene degradation potential of Alcaligenes sp. was 2.3 mg/g dry soil during a period of 22 days. The amount of CO₂ evolved during 22 days corresponded to the conversion of 91% of the degraded phenanthrene to CO₂. The Alcaligenes sp. were not able to degrade phenanthrene in sterile soil.     

氯嘧磺隆对土壤微生物群落结构的影响

采用磷脂脂肪酸(PLFA)法研究了黑龙江省苇河地区不同氯嘧磺隆施药历史下土壤微生物群落结构的差异, 并测定了土壤中氯嘧磺隆的残留量.结果表明：不同施药历史下氯嘧磺隆在土壤中的残留量均很低;随着施用氯嘧磺隆年限的增加,土壤微生物的PLFA总量减少, 革兰氏阴性菌/革兰氏阳性菌（GN/GP）和真菌/细菌比降低,土壤微生物的压力指数增加.主成分分析表明,氯嘧磺隆显著改变了大豆田土壤微生物群落结构.     

Bioremediation of a polyaromatic hydrocarbon contaminated soil by native soil microbiota and bioaugmentation with isolated microbial consortia

Biodegradation of a mixture of PAHs was assessed in forest soil microcosms performed either without or with bioaugmentation using individual fungi and bacterial and a fungal consortia. Respiratory activity, metabolic intermediates and extent of PAH degradation were determined. In all microcosms the low molecular weight PAH’s naphthalene, phenanthrene and anthracene, showed a rapid initial rate of removal. However, bioaugmentation did not significantly affect the biodegradation efficiency for these compounds. Significantly slower degradation rates were demonstrated for the high molecular weight PAH’s pyrene, benz[a]anthracene and benz[a]pyrene. Bioaugmentation did not improve the rate or extent of PAH degradation, except in the case of Aspergillus sp. Respiratory activity was determined by CO₂ evolution and correlated roughly with the rate and timing of PAH removal. This indicated that the PAHs were being used as an energy source. The native microbiota responded rapidly to the addition of the PAHs and demonstrated the ability to degrade all of the PAHs added to the soil, indicating their ability to remediate PAH-contaminated soils.