微生物降解磺酰脲类除草剂的研究进展

磺酰脲类除草剂具有高效和高选择性等优点,但其微量残留在土壤环境中就会对敏感作物会产生药害。因此,解决其残留问题便成为当今的研究热点。其中微生物降解是磺酰脲类除草剂降解的最有效方法之一。本文综述了降解磺酰脲类除草剂微生物种类、降解机理及研究现状,并展望了微生物降解磺酰脲类除草剂修复污染土壤的前景。     

三唑并嘧啶磺酰胺类除草剂的研究概况

三唑并嘧啶磺酰胺类除草剂是将磺酰脲类除草剂通过脲桥的结构改造和修饰而得,它既保持了磺酰脲类除草剂的超高效性,又克服了一些磺酰脲类除草剂品种在土壤中残留期较长、易对后茬作物造成伤害等缺点。本文综述了三唑并嘧啶磺酰胺类除草剂的结构、主要品种、作用机理、应用研究和发展前景。     

磺酰脲类除草剂及其安全剂研究进展

本文简述了磺酰脲类除草剂的概况、长残留药害以及使用安全剂缓解残留药害的研究进展,并展望了磺酰脲类除草剂及其安全剂的发展前景。     

毛细管电泳定量测定稻田土壤中痕量磺酰脲类除草剂残留

研究了提取浓缩和毛细管电泳相结合测定稻田土壤中低剂量多个磺酰脲类除草剂混合残留的分析方法。结果表明: 毛细管电泳可有效分离和定量测定稻田土壤中甲磺隆、氯磺隆和氯嘧磺隆混合残留。通过定量补偿甲磺隆、氯磺隆和氯嘧磺隆可使残留检测限达到ng/kg级,回收率>87%。表明毛细管电泳具有定量测定土壤中ng/kg级磺酰脲类除草剂残留的能力。     

磺酰脲类除草剂的微生物降解研究进展

磺酰脲类除草剂是使用最广泛的除草剂之一。微生物降解是磺酰脲类除草剂在土壤中降解的重要方式。本文简要概述了土壤微生物对磺酰脲类除草剂的降解、降解机理及影响微生物降解磺酰脲类除草剂的因素。     

磺酰脲类除草剂与杂草对其抗性的研究进展

1磺酰脲类除草剂的概况1.1磺酰脲类除草剂的发展20世纪70年代末,美国杜邦公司Levitt等首次开发和报道了磺酰脲类除草剂绿磺隆的除草活性[1]。80年代初,这一除草剂开始进行大规模商品化生产,此后,又不断研制和开发了许多磺酰脲类除草剂新品种。此类除草剂问世以后,以其活性高、选择性强、杀草谱广及对动物安全等特性在世界各地得到广泛应用。目前有关磺酰脲类除草剂的专利有400多项,已商品化的有30多种。这类除草剂有很高的除草效率,用量一般为2~100 g/hm2,比传统除草剂的除草效率高100~1 000倍[2]。磺酰脲类除草剂对动物低毒,在非靶标生物…     

磺酰脲类除草剂的降解机制及代谢产物的研究进展

磺酰脲类除草剂是一类高效,低毒和高选择性的除草剂,该类除草剂能有效防除阔叶杂草,其中有些品种对禾本科杂草也有一定的抑制作用。但同时因其用量低、对哺乳动物低毒以及独特的除草活性等特点而得到广泛应用。因此,了解磺酰脲类除草剂在土壤中的环境行为及归趋对于其科学合理使用、防止作物药害和保护农业生态环境具有非常重要的意义。根据笔者对磺酰脲类除草剂的深入研究,并总结归纳国内外的相关文献报道,对磺酰脲类除草剂的降解机制及其代谢产物的研究进行了综述,最后展望了磺酰脲类除草剂未来的发展趋势。     

磺酰脲类除草剂在不同土壤中淋溶行为的生物测定技术

磺酰脲类除草剂在不同土壤中淋溶行为的生物测定技术Ｐ，ＧＵＮＴＨＥＲ．Ｗ，ＰＥＳＴＥＭＥＲＡ．ＲＡＨＭＡＮ．Ｈ．ＮＯＲＤＭＥＹＥＲ前言生物测定是对土壤或水中除草剂进行定量分析的有效工具。早期开发的磺酰脲类除草剂（如绿磺隆、甲磺隆）在土壤中残留期长，特别...     

三种磺酰脲类除草剂的光解和水解作用

磺酰脲类除草剂属高效除草剂,即用量少,除草活性高。其残留期因药剂而异,据报道,它们的主要降解方式是水解、微生物降解及水溶性光分解作用,在田间土壤含水量与药剂的降解速度成正比。作者研究了氯磺隆(Chlorsulfuron)、氯嘧磺隆(Chlorimuronethyl)、吡嘧磺隆(Pyrarosulfuron-ethyl)3种磺酰脲类除草剂水溶液的水溶性光分解作用和水解作用,对了解该类除草剂的降解作用有重要意义。     

磺酰脲类除草剂与其抗药性的研究进展

本文简述了磺酰脲类除草剂的概况及其抗性和延缓其抗性的研究进展,展望了磺酰脲类除草剂制成混配制剂对延缓抗性发展的前景。     

Characterization of acetolactate synthase from sulfonylurea herbicide‐resistant Schoenoplectus juncoides

Ten accessions of sulfonylurea‐resistant Schoenoplectus juncoides were collected from paddy fields in Japan. In order to characterize acetolactate synthase from sulfonylurea‐resistant S. juncoides, acetolactate synthase amino acid substitutions, whole‐plant growth inhibition and acetolactate synthase enzyme inhibition were examined. Schoenoplectus juncoides has two acetolactate synthase genes (ALS1 and ALS2). The sulfonylurea‐resistant accessions harbored amino acid substitutions at Pro197 or Trp574 in either ALS1 or ALS2 (the amino acid number is standardized to the Arabidopsis thaliana sequence). The whole plants of all the sulfonylurea‐resistant accessions showed resistance to imazosulfuron. The resistance level depended on the altered amino acid residues in acetolactate synthase. The acetolactate synthase enzyme that was partially purified from all the sulfonylurea‐resistant accessions was less sensitive to imazosulfuron, compared to the susceptible accession, suggesting that the resistance is related to the altered acetolactate synthase enzyme. In addition, the concentration–response inhibition of acetolactate synthase activity by imazosulfuron in the sulfonylurea‐resistant accessions was remarkably different with the presence of an amino acid substitution in either ALS1 or ALS2. Furthermore, the concentration–response inhibition of acetolactate synthase activity in the sulfonylurea‐resistant accessions with a P197S, P197T or W574L mutation showed a double‐sigmoid curve. The regression analysis of enzyme inhibition suggested that the abundance ratio of ALS1 to ALS2 enzymes was approximately 70:30%, with a range of ±15%. Taken together, these results suggest that the resistance of sulfonylurea‐resistant accessions of S. juncoides is related to altered acetolactate synthase in either ALS1 or ALS2, although the abundance of the altered acetolactate synthase in the plants is different among the sulfonylurea‐resistant accessions.     

Spontaneous ultraweak photon emission from rice (Oryza sativa L.) and paddy weeds treated with a sulfonylurea herbicide

All living organisms spontaneously generate ultraweak photon emissions, which originate from biochemical reactions in cells. Current research uses the ultraweak photon emissions from organisms as a novel tool to investigate the physiological states of plants. In this study, we found ultraweak photon emissions from leaf segments of rice and several paddy weed species treated with a sulfonylurea herbicide. There is a definite difference in photon emissions among plant species, and rice (Oryza sativa), barnyardgrass (Echinochloa crus-galli) and Cyperus serotinus showed extremely strong enhancement of photon emissions. Photon emissions from these three species treated with sulfonylurea herbicide were suppressed when the leaf segments were treated with the cytochrome P450 monooxygenase (P450) inhibitors, piperonyl butoxide and malathion. These results suggest that P450 inhibitors affect the ultraweak photon emissions from plants.     

Corn poppy (Papaver rhoeas) cross-resistance to ALS-inhibiting herbicides

BACKGROUND: Papaver rhoeas (L.) has evolved resistance to tribenuron in winter wheat fields in northern Greece owing to multiple Pro₁₉₇ substitutions. Therefore, the cross‐resistance pattern to other sulfonylurea and non‐sulfonylurea ALS‐inhibiting herbicides of the tribenuron resistant (R) and susceptible (S) corn poppy populations was studied by using whole‐plant trials and in vitro ALS catalytic activity assays. RESULTS: The whole‐plant trials revealed that tribenuron R populations were also cross‐resistant to sulfonylureas mesosulfuron + iodosulfuron, chlorsulfuron and triasulfuron. The whole‐plant resistance factors (RFs) calculated for pyrithiobac, imazamox and florasulam ranged from 12.4 to > 88, from 1.5 to 28.3 and from 5.6 to 25.4, respectively, and were lower than the respective tribenuron RF values (137 to > 2400). The ALS activity assay showed higher resistance of the ALS enzyme to sulfonylurea herbicides (tribenuron > chlorsulfuron) and lower resistance to non‐sulfonylurea ALS‐inhibiting herbicides (pyrithiobac > florasulam ≈ imazamox). CONCLUSION: These findings indicate that Pro₁₉₇ substitution by Ala, Ser, Arg or Thr in corn poppy results in a less sensitive ALS enzyme to sulfonylurea herbicides than to other ALS‐inhibiting herbicides. The continued use of sulfonylurea herbicides led to cross‐resistance to all ALS‐inhibiting herbicides, making their use impossible in corn poppy resistance management programmes. Copyright © 2011 Society of Chemical Industry     

Chemistry of sulfonylurea herbicides

The discovery of the sulfonylurea class of herbicides is one of the most dramatic breakthroughs in herbicide research in several decades. Sulfonylureas possess unprecedented levels of herbicidal activity–as low as 1 g ha^?1–very low mammalian toxicity, and very desirable environmental properties. This review will discuss the structure-activity relationships of sulfonylureas, their physical and chemical properties, and their methods of synthesis.     

Cross-resistance pattern and alternative herbicides for Cyperus difformis resistant to sulfonylurea herbicides in Korea

A Cyperus difformis L accession from Chonnam province, Korea was tested for resistance to the sulfonylurea herbicide, imazosulfuron. The accession was confirmed to be resistant (R) and was cross-resistant to other sulfonylurea herbicides, bensulfuron-methyl, cyclosulfamuron and pyrazosulfuron-ethyl, the pyrimidinyl thiobenzoate herbicide, bispyribac-sodium, and the imidazolinone herbicide imazapyr, but not to imazaquin. Multiple resistance was tested using twelve herbicides with target sites other than acetolactate synthase (ALS). The R biotype could be controlled by other herbicides with different modes of action such as butachlor, carfentrazone-ethyl, clomeprop, dithiopyr, esprocarb, mefenacet, oxadiazon, pretilachlor, pyrazolate and thiobencarb, applied to soil at recommended rates. Several sulfonylurea herbicide-based mixtures can control both the R and S biotypes of C difformis, except sulfonylurea plus dimepiperate, molinate or pyriftalid, and pyrazolate plus butachlor. Although mixtures of sulfonylurea herbicides might be more effective, they should be avoided and used only in special cases. In terms of in vitro ALS activity, the R biotype was 1139-, 3583-, 1482-, 416-, 5- and 9-fold more resistant to bensulfuron-methyl, cyclosulfamuron, imazosulfuron, pyrazosulfuron-ethyl, bispyribac-sodium and imazapyr, respectively, than the S biotype. The in vivo ALS activity of the R biotype was also less affected by the sulfonylurea herbicides, imazosulfuron and pyrazosulfuron-ethyl, than the S biotype. Results of in vitro and in vivo ALS assays indicated that the resistance mechanism of C difformis to ALS inhibitor herbicides was primarily due to an alteration in the target enzyme, ALS. Greenhouse experiments showed delayed flowering and reduced seed production of the R biotype, which could possibly result in reduced fitness. This unusual observation needs to be confirmed in field situations.     

Sulfonylurea resistance in Lindernia micrantha, an annual paddy weed in Japan

Resistance to sulfonylurea herbicides, including bensulfuron-methyl, pyrazosulfuron-ethyl, imazosulfuron and ethoxysulfuron, was discovered in naturally occurring populations of Lindernia micrantha D. Don in rice fields that had been treated with sulfonylurea-based herbicides for 3–7 consecutive years. The resistant biotype was approximately 80≈300 times more resistant than the susceptible one to the above four sulfonylurea herbicides. This is the second confirmed occurrence of herbicide resistance resulting from the use of sulfonylurea herbicides in Japan. Several herbicides with different modes of action, including pretilachlor, cafenstrole, bifenox, naproanilide, thiobencarb + simetryn + MCPB, MCPA-thioethyl + simetryn and cyhalofop-butyl + bentazone, effectively controlled the resistant biotype in pot trials.     

Resistance of Camelina microcarpa to acetolactate synthase inhibiting herbicides

An accession of Camelina microcarpa suspected to be resistant to sulfonylurea herbicides was identified in Oregon in 1998 field experiments. Greenhouse research confirmed that the putative resistant biotype was resistant to chlorsulfuron and metsulfuron on a whole plant level. Compared with the resistant (R) biotype, the susceptible (S) biotype was 1000 and 10 000‐fold more sensitive to metsulfuron and chlorsulfuron respectively. The R biotype was also resistant to other sulfonylurea, sulfonylaminocarbonyl‐triazolinone, imidazolinone and triazolopyrimidine herbicides. An in vivo enzyme assay indicated that acetolactate synthase (ALS) from the R plants required 111 times more chlorsulfuron to inhibit activity by 50% compared with the amount required to have a similar effect on ALS from S plants. Analysis of the nucleotide and amino acid sequences demonstrated that a single‐point mutation from G to T in the als1 gene conferred the change from the amino acid tryptophan to leucine at position 572 in the resistant biotype. This research confirmed that ALS inhibitor resistance in an Oregon accession of C. microcarpa is based on an altered target site conferred by a single‐point mutation.