土壤环境中除草剂甲磺隆降解的研究Ⅰ.土壤性质的影响

采用方差分析,研究了各土壤中不同形态甲磺隆残留量的差异程度;通过主因子分析,选出5个主因子,它们代表了整体信息量的90.4%;回归分析后建立了土壤性质和甲磺隆残留间的多元回归方程;经偏相关分析和通径分析得出,土壤pH值和微生物活性是甲磺隆降解的主要影响因素。     

土壤环境中除草剂甲磺隆降解的研究I.土壤性质的影响

采用方差分析,研究了各土壤中不同形态甲磺隆残留量的差异程度;通过主因子分析,选出5个主因子,它们代表了整体信息量的90.4%;回归分析后建立了土壤性质和甲磺隆残留间的多元回归方程;经偏相关分析和通径分析得出,土壤pH值和微生物活性是甲磺隆降解的主要影响因素.     

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.     

氯嘧磺隆与尿素对土壤微生物生物量碳、氮及无机氮的影响

通过室内培养试验,研究了不同浓度氯嘧磺隆(20、200、2000 μg·kg-1土)单一施用及与尿素(120 mg· kg-1土)配合施用情况下,土壤微生物生物量碳、氮和土壤铵态氮、硝态氮随时间的动态变化规律.结果表明:各浓度氯嘧磺隆单独处理在整个培养期(60 d)中对微生物生物量碳、氮均有抑制作用,且浓度越高,后期抑制作用越强;各浓度氯嘧磺隆处理在培养前期对硝态氮、铵态氮没有明显影响,中期(15 d)能显著提高土壤中铵态氮的含量,后期(30 d后)显著提高了土壤中硝态氮的含量.尿素单独施用及与氯嘧磺隆配施均能在短时间内增加微生物生物量碳、氮,但随后配施处理的促进作用减弱;尿素单独和配施均能持久增加土壤中铵态氮、硝态氮含量.     

甲磺隆对微囊藻生长和光合系统的影响

研究选取了水体常见蓝藻优势种类——铜绿微囊藻(Microcystis aeruginosa PCC7806)作为研究对象, 了解磺酰脲类除草剂甲磺隆(Metsulfuron-methyl)对铜绿微囊藻生长和光合系统的影响。研究表明, 当甲磺隆浓度大于80 mg/L时, 对铜绿微囊藻的生长具有显著抑制。通过回归分析和Probit分析, 甲磺隆对铜绿微囊藻生长的EC₅₀为81.998 mg/L。细胞色素研究结果显示, 实验第6天, 各浓度处理下单位细胞内Chl.a和类胡萝卜素含量均低于对照组, 且当甲磺隆浓度为80 mg/L时, 单位细胞内类胡萝卜素含量显著低于对照组。快速叶绿素荧光诱导动力学变化结果分析显示, 实验第6天甲磺隆胁迫下单位反应中心捕获的用于电子传递的能量(ET₀/RC)及单位反应中心用于电子传递的量子产额(φE₀)受到显著抑制, 综合细胞色素变化结果显示, 甲磺隆能显著抑制光合系统反应中心电子受体侧电子性能。综上所述, 甲磺隆可能作用于光合系统反应中心电子受体侧, 从而对铜绿微囊藻光合系统造成影响。     

抗甲磺隆假单胞菌的分离及其乙酰乳酸合酶的大小亚基ilvIH基因的克隆和表达

乙酰乳酸合酶(也称乙酰羟酸合酶acetohydroxyacid synthase,AHAS)是植物、真菌和细菌细胞内支链氨基酸Val、Leu、Ile生物合成过程中关键酶,是乙酰乳酸合酶抑制剂类除草剂如磺酰脲类、咪唑啉酮类、嘧啶水杨酸和磺酰氨类的作用靶标.[目的]获得抗甲磺隆的乙酰乳酸合酶基因,构建其表达载体,并分析基因中的位点突变与乙酰乳酸合酶对磺酰脲类除草剂抗性产生原因.[方法]从长期使用甲磺隆的土壤中分离到l株抗甲磺隆的菌株Lm10,利用PCR技术从Lm10总DNA中克隆到乙酰乳酸合酶的大小亚基基因ilvIH,对ilvIH氨基酸序列进行比对分析.分别将ilvI和ilvH分别连接到表达载体pET29a( )多克隆位点,转化大肠杆菌(Escherichia coli)获得转化子BL21(pET-I)和BL21(pET-H),并诱导表达.[结果]菌株Lm10鉴定为假单孢菌(Pseudomonas sp.),对甲磺隆的最高耐受浓度达到14000 μmol/L,且对各种乙酰乳酸合酶抑制剂类除草剂具有交叉抗性.Lm10与甲磺隆敏感菌株KT2440的小亚基氨基酸序列完全相同,而大亚基有6个氨基酸位点发生变异.转化子在IPTG诱导下,乙酰乳酸合酶的大小亚基的蛋白成功表达,粗酶液酶活试验结果表明Lm10的ilvI基因表达的乙酰乳酸合酶大亚基对甲磺隆有很强的抗性.[结论]发现菌株Lm10的乙酰乳酸合酶大亚基对甲磺隆有很强的抗性,抗甲磺隆菌株Lm10与敏感菌株KT2440的ilvI有6个氨基酸位点差异,这些位点突变可能是乙酰乳酸合酶对甲磺隆抗性产生的原因.     

溶液pH值及模拟酸雨对两种磺酰脲类除草剂在土壤中行为的影响

采用平衡振荡法和土柱淋洗法,研究了溶液pH及模拟酸雨对土壤中苄嘧磺隆和甲磺隆行为的影响.结果表明,Freundlich方程能较好地描述苄嘧磺隆和甲磺隆的吸附等温线,水-土壤系统pH升高能明显地降低这两种除草剂在土壤中的吸附,促进其在土壤中的迁移,且吸附常数(K_f)与土壤有机质含量、粘土含量呈正相关,而与土壤pH呈负相关.pH值高的模拟酸雨对除草剂在土壤中淋溶贡献较大,且淋溶量随雨量的增大而增大.除草剂在土壤中的淋溶与土壤性质密切相关,有机质含量和粘粒含量较高的土壤对除草剂的持留能力较强.     

几种除草剂对薇甘菊的防控效果

【背景】薇甘菊是一种外来入侵的恶性杂草,对当地农、林业造成了严重的危害。【方法】研究了草甘膦、氨氯吡啶酸、甲嘧磺隆、噻吩磺隆、苯磺隆、百草枯、五氟磺草胺、单嘧磺隆和单嘧磺脂9种除草剂对薇甘菊的化学防治,调查各药剂对薇甘菊的植株鲜重抑制率、叶片覆盖度和抑花率。【结果】氨氯吡啶酸25～100gai.hm-2、草甘膦1538～2306gai.hm-2、甲嘧磺隆100～400gai.hm-2、百草枯750、1125gai.hm-2、五氟磺草胺125gai.hm-2、噻吩磺隆11.25～33.75gai.hm-2和单嘧磺脂15～60gai.hm-2对薇甘菊营养生长控制效果较好。其中,百草枯短时间有效,草甘膦、五氟磺草胺、单嘧磺脂、单嘧磺隆、氨氯吡啶酸和甲嘧磺隆对薇甘菊的抑花率较高,苯磺隆和单嘧磺隆基本无效,且9种药剂对橡胶树均未表现出药害。【结论与意义】适当降低氨氯吡啶酸、甲嘧磺隆、草甘膦、五氟磺草胺、噻吩磺隆和单嘧磺脂的浓度可以保持薇甘菊营养生长而扼制种子蔓延。本研究首次发现五氟磺草胺、噻吩磺隆和单嘧磺脂对薇甘菊有良好的抑制效果。     

豆磺隆对北方草甸棕壤土壤酶活性的影响

通过室内模拟方法, 以北方具有代表性的草甸棕壤为研究对象, 研究了除草剂豆磺隆对土壤脲酶、转化酶和三种磷酸酶活性的影响。结果显示, 在试验浓度范围内 , 豆磺隆对土壤脲酶和转化酶总体上有激活作用 , 影响幅度分别为 3.07%-20.02%和−1.73%-5.67%; 除个别浓度外, 豆磺隆对三种土壤磷酸酶均有抑制作用 , 豆磺隆浓度为 5 mg⋅kg–1时对酸性磷酸酶的抑制作用最强, 抑制率为 17.92%, 对中性磷酸酶的抑制率仅在 0.77%-1.54%之间 , 对碱性磷酸酶的抑制率为 8.95%-20.60%。豆磺隆对脲酶、转化酶、酸性磷酸酶和中性磷酸酶活性的影响较小 , 且未表现出明显规律性, 仅与碱性磷酸酶呈显著(p < 0.05)的对数负相关关系 , 表明碱性磷酸酶在一定程度上可作为豆磺隆污染土壤的监测指标。     

不同土壤细菌种群结构对氯嘧磺隆胁迫的响应及降解菌系的获得

应用PCR-DGGE、DNA测序等方法,在室内驯化条件下研究了8种来源于中国不同地区土壤样品细菌种群结构对氯嘧磺隆胁迫的响应。结果表明:在氯嘧磺隆100～500mg·L-1浓度梯度下,土壤细菌群落组成有明显的更迭现象,多样性发生明显变化,驯化至10周,绝大部分细菌种群消失,样品的细菌种群结构趋于简单并呈现趋同效应;DNA测序结果表明,在驯化第10周可培养Methylophilus sp.、Beta proteobacterium、uncultured bacterium成为优势菌属,所获细菌种群出现的16个优势种群中有10个与已知的具有有机污染物降解功能和有机污染环境修复功能细菌的相似性大于97%;其中5个与嗜甲基菌16S rDNA部分序列相似性达98%以上。获得了一组对氯嘧磺隆具有降解作用的细菌菌系,可在5d内将100mg·L-1氯嘧磺隆降解67%;其主要组成为嗜甲基菌属(Methylophilus sp.)、丛毛单胞菌属(Comamonas sp.)、鞘酯杆菌属(Sphingobacterium sp.)和嗜氢菌属(Hydrogenophi-lus sp.)。     

Rapid biodegradation of metsulfuron-methyl by a soil fungus in pure cultures and soil

Summary Four strains of bacteria, 9 strains of fungi and 20 strains of actinomycetes capable of utilizing metsulfuron-methyl as sole carbon and energy source were isolated from a metsulfuron-methyl-treated soil by the enrichment culture method. A fungus named DS11F was selected as the most highly effective one according to the maximum tolerance concentration of 1,200 mg l⁻¹ and metsulfuron-methyl-degrading rate of 0.0716 g g⁻¹ cells h⁻¹, and was identified as an unknown strain of Penicillium sp. on the basis of colony growth, morphology and biochemical characteristics.␣Through liquid pure culture, the optimal metsulfuron-methyl-degrading conditions of DS11F were determined to be metsulfuron-methyl concentration 22.6 mg l⁻¹, inoculum concentration 12.25 mg l⁻¹, pH 7.0 and temperature 30°C. As additional C sources, supernatant of soaked compost could increase metsulfuron-methyl degradation by 8%, but glucose was ineffective. DS11F inoculation was found to significantly enhance the degradation of metsulfuron-methyl in soil, with the reduction of the concentration reaching 50% in 6 days. Admixture of compost could promote metsulfuron-methyl degradation to some extent. The growth of the inocula in the soils remained dominant and degradation resumed immediately when metsulfuron-methyl was applied again. The results show that addition of the isolated Penicillium sp. enhances the degradation of metsulfuron-methyl in water and soil.     

Immobilization of esterase SulE in cross-linked gelatin/chitosan and its application in remediating soils polluted with tribenuron-methyl and metsulfuron-methyl

The esterase SulE is known to be an important and primary enzyme for the degradation of many sulfonylurea herbicides such as tribenuron-methyl, metsulfuron-methyl, and chlorimuron-ethyl. The disadvantages of applying free enzyme include poor stability and rapid deactivation in the natural environment, but these problems can be mitigated by using immobilized enzymes. In this study, cross-linked gelatin/chitosan (GLT/CTS) was selected as the enzyme immobilization carrier because its SulE activity recovery was higher than those of γ-polyglutamate/gelatin (γ-PGA/GLT) and γ-polyglutamate/chitosan (γ-PGA/CTS). The immobilization conditions were further optimized, and the effects of pH and temperature on GLT/CTS-SulE and free SulE activities to degrade tribenuron-methyl and metsulfuron-methyl were investigated. A microcosm experiment was conducted to assess the effectiveness of GLT/CTS-SulE in remediating soils polluted with tribenuron-methyl and metsulfuron-methyl. The results showed that, compared with free SulE, GLT/CTS-SulE displayed better pH and temperature adaptabilities and higher degradation efficiencies for both herbicides in soil, especially tribenuron-methyl. The results indicate that this is an excellent method to immobilize SulE for enhanced remediation of soils polluted with tribenuron-methyl or metsulfuron-methyl in situ.     

Mineralization Potential of Atrazine and Degradation Intermediates from Clustered Characteristics in Inoculated Soils

Soil properties impact pesticide persistence. Because these characteristics operate together in situ, identification of their clustered associations can help explain pesticide fate. Factor analysis was used to reduce the dimensionality of soil characteristics by grouping them into clustered independent factors, which were then related to the mineralization of atrazine and selected degradation intermediates. A Sharpsburg silty clay loam, Ortello sandy loam, and Hord silt loam were inoculated with a Hord soil that had a high capacity for atrazine mineralization. The soils were spiked with ¹⁴C-radiolabeled atrazine, deethylatrazine, hydroxyatrazine, N-isopropylammeline, N-isopropylammelide or cyanuric acid and sampled during incubation for 80 d (atrazine) or 40 d (degradation intermediates) at 22°C. Low mineralization in uninoculated soils demonstrated that the absence of atrazine-mineralizing microorganisms was most limiting. In inoculated soils, regression analysis indicated mineralization of atrazine (R² = 0.88) and its degradation intermediates (R² ≥ 0.89) was related to factors associated with bioavailability and microbial activity. For atrazine, this relationship indicated mineralization may be positively influenced by higher pH and available phosphorus, lower NO₃-N, organic carbon and clay contents, and lower adsorption. Our results show how factor analysis can be used in conjunction with multiple regression to determine mineralization potential and thus help identify soils with limited degradation capacities and possible long-term persistence.     

Degradation of Triazine-2-14C Metsulfuron–Methyl in Soil from an Oil Palm Plantation

Triazine-2-¹⁴C metsulfuron–methyl is a selective, systemic sulfonylurea herbicide. Degradation studies in soils are essential for the evaluation of the persistence of pesticides and their breakdown products. The purpose of the present study was to investigate the degradation of triazine-2-¹⁴C metsulfuron–methyl in soil under laboratory conditions. A High Performance Liquid Chromatograph (HPLC) equipped with an UV detector and an on-line radio-chemical detector, plus a Supelco Discovery column (250 x 4.6 mm, 5 μm), and PRP–1 column (305 x 7.0 mm, 10 μm) was used for the HPLC analysis. The radioactivity was determined by a Liquid Scintillation Counter (LSC) in scintillation fluid. The soil used was both sterilized and non-sterilized in order to observe the involvement of soil microbes. The estimated DT₅₀ and DT₉₀ values of metsulfuron-methyl in a non-sterile system were observed to be 13 and 44 days, whereas in sterilized soil, the DT₅₀ and DT₉₀ were 31 and 70 days, respectively. The principal degradation product after 60 days was CO₂. The higher cumulative amount of ¹⁴CO₂ in ¹⁴C- triazine in the non-sterilized soil compared to that in the sterile system suggests that biological degradation by soil micro-organisms significantly contributes to the dissipation of the compound. The major routes of degradation were O-demethylation, sulfonylurea bridge cleavage and the triazine “ring-opened.”     

Study of Biochemical Pathway and Enzyme Involved in Metsulfuron-Methyl Degradation by <Emphasis Type="Italic">Ancylobacter</Emphasis> sp. XJ-412-1 Isolated from Soil

Ancylobacter sp. XJ-412-1, capable of degrading metsulfuron-methyl, was isolated from sulfonylurea-contaminated soil. When metsulfuron-methyl was provided as the sole carbon source, more than 90.5% of metsulfuron-methyl at concentration of 50 mg l⁻¹ was degraded by strain XJ-412-1 after incubation at 30°C for 7 days. The initial degradation products of metsulfuron-methyl (MSM), thifensulfuron-methyl (TSM), and bensulfuron-methyl (BSM) by XJ-412-1 were identified as corresponding deesterified derivatives by liquid chromatography-mass spectrometry, which indicated a primary pathway of the deesterification of these three sulfonylurea herbicides. The carboxyesterase activity of the cell-free extracts was assayed and strongly inhibited by 4-chloromercuribenzoic acid (PCMB), diethyl pyrocarbonate (DEPC), phenylmethylsulfonyl fluoride (PMSF), and malathion.     

Rehabilitation of Semiarid Landscapes in Australia. I. Restoring Productive Soil Patches

A rehabilitation procedure designed to reestablish resource control processes in a degraded Acacia aneura woodland was successful in improving soil nitrogen and carbon content, exchange properties, and water infiltration rates. Soil respiration rates and soil fauna populations increased, and soil temperatures were moderated. The procedure comprised laying piles of branches in patches on the contour of bare, gently sloping landscapes, with the expectation that soil, water, and litter would accumulate in these branch piles, thus improving the soil habitat and its productive potential. The procedure was derived from landscape function analysis, indicating that surface water flow was the principal means of resource transfer in these landscapes. Under degradation such overland flow results in a loss of resources. This rehabilitation procedure reversed loss processes, resulting in gains in the productive potential of soils within patches. This procedure was successful despite grazing pressure being maintained throughout the experiment.     

辽宁省冰砬山森林立地分类的研究

森林立地的研究是人工林集约经营的基础,正确地选择宜林地,科学造林,真正做到适地适树,必须进行森林立地分类。森林立地分类应是以现代森林生态学和生态系统理论为依据,研究植被(立木、下木、地被物)和地形、植被与土壤以及地形和土壤的关系。在揭     

川西亚高山不同林龄云杉人工林土壤微生物群落结构

以川西亚高山云杉人工林林地土壤为对象,采用磷脂脂肪酸(PLFA)法研究了4种不同林龄(50、38、27和20年)的人工林土壤微生物多样性和群落结构特征.结果表明: 随着林龄的增加,土壤有机碳和全氮含量逐步增加;土壤微生物Shannon多样性和Pielou均匀度指数则呈现先增后减的趋势.土壤微生物总PLFAs量、细菌PLFAs量、真菌PLFAs量、放线菌PLFAs量以及丛枝菌根真菌PLFAs量均表现为随林龄的增加而增加.主成分分析(PCA)表明,不同林龄人工林的土壤微生物群落结构之间存在显著差异,其中,第1主成分(PC1)和第2主成分(PC2)共同解释了土壤微生物群落结构总变异的66.8%.冗余分析(RDA)表明,对土壤微生物群落结构产生显著影响的环境因子分别为土壤有机碳、全氮、全钾以及细根生物量.随着人工造林时间的延长,土壤肥力和微生物生物量增加,森林生态系统的恢复进程稳定.     

闽江河口湿地土壤盐分的空间分异与集聚特征

探究河口湿地土壤盐分的空间异质性,揭示分异格局下的空间集聚特征,对河口湿地的可持续发展具有重要意义。本文以福州市闽江河口湿地的Landsat 8遥感影像、数字高程模型和地面实测土壤盐分为数据源,利用相关性分析与主成分分析法选取显著性环境因子,去除变量间的共线性,分别采用支持向量机回归克里格法(SVROK)和回归克里格法(RK)分析了土壤盐分空间异质性,在基础上运用空间自相关法定量描述了土壤盐分空间集聚特征。结果表明: 通过主成分分析提取出3个主成分,可解释数据总方差的85%,反映植被覆盖、土壤属性和地形状况等综合变化信息,并保留原始变量的大部分信息;土壤盐分及其插值残差的空间变异受结构性因素和随机性因素的影响,采用主成分为自变量所建立的SVROK模型能更为精准地体现土壤盐分 “北高南低”的空间异质特征;土壤盐分的Moran I大于0.5,具有显著的空间正相关,空间集聚程度较高,呈现出“高值集聚、低值广布、低值包围高值”的空间集聚特征。