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A whole-plant bioassay system for the detection of residues of ALS/AHAS inhibiting herbicides in soils and determination of safe planting intervals for sensitive crops.

机译:一种用于检测土壤中ALS / AHAS抑制性除草剂残留并确定敏感作物安全种植间隔的全植物生物测定系统。

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摘要

In Ontario, the ALS/AHAS herbicides, including the sulfonylureas, imidazolinones and triazolopyrimidines, are used to control a wide range of weeds in many crop species. These herbicides have very high biological activity (i.e. dose ranges of g ai ha-1 vs. kg ai ha-1 for older generation chemistries) which has potential to cause significant negative impact to non-target plants or subsequently planted sensitive crops such as Beta vulgaris (sugar beet), and Brassica spp. (canola and cole crops) among others. The injury to sensitive crops varies with herbicide type as well as climatic and edaphic factors. Sulfonylurea herbicides degrade primarily by chemical hydrolysis and tend to persist in alkaline soils. Imidazolinone herbicides degrade primarily by microbial activity and are more persistent in acidic soils. This research was conducted to develop a whole-plant bioassay system to detect injurious concentrations of these herbicides in different soil types across southern Ontario. A loam soil was fortified with 0.0, 0.01, 0.05, 0.1, 0.5, 1, 2.5, 5 and 10 mukg-1 of each herbicide into which indicator crops of sugar beet, canola, rutabaga and sweet corn were seeded and grown for 30 days under optimized growth room conditions. Plant dry weight data were subjected to a log-logistic regression analysis to determine the I50 concentrations of each herbicide by indicator species combination. I50 values for chlorimuron were 0.11 (se0.005), 0.09 (se0.004), and 0.10-0.11 (se0.009) mug kg-1 for canola, rutabaga and sugar beet, respectively. For flumetsulam the I 50 values were 0.95-1.10 (se0.075), 0.69-0.85 (se0.062), and 0.67-1.76 (se0.139) for canola, rutabaga and sugar beet, respectively while I50 values for imazethapyr were 0.42-0.65 (se0.057), 0.54-0.91 (se0.071), and 0.30-0.46 (se0.032) mug kg-1 respectively, for canola, rutabaga and sugar beet. The whole-plant bioassay system was utilized to determine the in situ concentration of chlorimuron and imazethapyr in field samples collected at various intervals following field application to a soybean crop in 1998 or 1999 in four-replicate RCBD experiments at five sites across Ontario. Each of the sites differed in soil pH and other edaphic factors. Growth response of sugar beet in herbicide-treated field soil samples was compared to general and soil-specific dose-response curves developed by spiking untreated site-specific soil with 0.0, 0.05, 0.1, 0.5, 1.0, 2.5 mug kg-1 of each herbicide. The results indicate that the degradation rate of chlorimuron and imazethapyr varied by site but were similar within a site, reflecting differences in soil conditions among sites (pH, texture, OM, etc). However, three years following herbicide application there was no difference in herbicide concentration detected by bioassay among the sites. I10 values would be a more appropriate economic indicator of acceptable crop injury for these herbicides and were estimated to be 0.005-0.090 and 0.067-0.405 pg kg-1 for chlorimuron and imazethapyr, respectively, using sugar beet as the indicator species. The whole-plant bioassay system was developed and validated across a range of southern Ontario soils and was able to detect injurious concentrations of chlorimuron and imazethapyr that were at levels less than the detection limits of liquid chromatography and capillary electrophoresis. This bioassay system can be used to determine when sensitive crop species can safely be seeded into sites previously treated with the ALS/AHAS herbicides.
机译:在安大略省,包括磺酰脲类,咪唑啉酮类和三唑并嘧啶类在内的ALS / AHAS除草剂可用于控制许多农作物中的多种杂草。这些除草剂具有非常高的生物活性(即,对于较老一代的化学药品而言,g ai ha-1相对于kg ai ha-1的剂量范围)可能会对非目标植物或随后种植的敏感作物(例如Beta)造成重大负面影响寻常(甜菜)和芸苔属。 (油菜和油菜作物)等。对敏感农作物的伤害因除草剂类型以及气候和水生因素而异。磺酰脲类除草剂主要通过化学水解降解,并倾向于在碱性土壤中持续存在。咪唑啉酮除草剂主要通过微生物活性降解,并且在酸性土壤中更持久。进行这项研究是为了开发一种全植物生物测定系统,以检测安大略省南部不同土壤类型中这些除草剂的有害浓度。分别用0.0、0.01、0.05、0.1、0.5、1、2.5、5和10公斤1的除草剂强化壤土,并在其中播种甜菜,低芥酸菜子,大头菜和甜玉米等指示性作物并生长30天在优化的生长室条件下。对植物干重数据进行对数逻辑回归分析,以通过指示剂种类组合确定每种除草剂的I50浓度。双低油菜籽,大头菜和甜菜的嘧啶隆的I50值分别为0.11(se <0.005),0.09(se <0.004)和0.10-0.11(se <0.009)杯子kg-1。对于flumetsulam,低芥酸菜籽,大头菜和甜菜的I 50值分别为0.95-1.10(se <0.075),0.69-0.85(se <0.062)和0.67-1.76(se <0.139),而咪唑乙烟的I50值为0.42对于低芥酸菜子,大头菜和甜菜,分别为-0.65(se <0.057),0.54-0.91(se <0.071)和0.30-0.46(se <0.032)马克杯kg-1。在1998年或1999年在安大略省的五个地点进行了四次重复的RCBD实验后,在1998年或1999年对大豆作物进行田间施用后,在不同间隔收集的田间样品中,采用了整个植物的生物测定系统来测定敌百虫和咪草乙烟的原位浓度。每个站点的土壤pH值和其他土壤因子都不同。将通过除草剂处理的田间土壤样品中甜菜的生长响应与通过添加0.0、0.05、0.1、0.5、1.0、2.5马克杯kg-1的未经处理的特定地点土壤而形成的一般和特定土壤剂量反应曲线进行比较除草剂。结果表明,毒死ur和咪唑乙​​烟的降解率随地点而异,但在地点内相似,反映了地点之间土壤条件的差异(pH,质地,OM等)。然而,施用除草剂三年后,通过生物测定法检测到的各部位间除草剂浓度没有差异。 I10值将是这些除草剂可接受的作物伤害的更合适的经济指标,使用甜菜作为指示剂种类,对氯草隆和咪草乙烟的I10值分别估计为0.005-0.090和0.067-0.405 pg kg-1。开发了整个植物生物测定系统,并在安大略省南部的各种土壤上进行了验证,能够检测出有害浓度的嘧菌隆和咪唑乙烟,含量低于液相色谱和毛细管电泳的检测极限。该生物测定系统可用于确定何时可以安全地将敏感作物种种到先前用ALS / AHAS除草剂处理过的部位。

著录项

  • 作者

    McDonald, Ian Douglas.;

  • 作者单位

    University of Guelph (Canada).;

  • 授予单位 University of Guelph (Canada).;
  • 学科 Agriculture Agronomy.;Agriculture Soil Science.;Agriculture Plant Culture.
  • 学位 Ph.D.
  • 年度 2009
  • 页码 178 p.
  • 总页数 178
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

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