王容燕, 马娟, 高波, 李秀花, 李焦生, 陈书龙. 土壤中烟嘧磺隆和莠去津残留对甘薯的药害评价[J]. 农药学学报, 2021, 23(5): 915-921. DOI: 10.16801/j.issn.1008-7303.2021.0086
    引用本文: 王容燕, 马娟, 高波, 李秀花, 李焦生, 陈书龙. 土壤中烟嘧磺隆和莠去津残留对甘薯的药害评价[J]. 农药学学报, 2021, 23(5): 915-921. DOI: 10.16801/j.issn.1008-7303.2021.0086
    WANG Rongyan, MA Juan, GAO Bo, LI Xiuhua, LI Jiaosheng, CHEN Shulong. Phytotoxicities of nicosulfuron and atrazine residues in soil on sweetpotato[J]. Chinese Journal of Pesticide Science, 2021, 23(5): 915-921. DOI: 10.16801/j.issn.1008-7303.2021.0086
    Citation: WANG Rongyan, MA Juan, GAO Bo, LI Xiuhua, LI Jiaosheng, CHEN Shulong. Phytotoxicities of nicosulfuron and atrazine residues in soil on sweetpotato[J]. Chinese Journal of Pesticide Science, 2021, 23(5): 915-921. DOI: 10.16801/j.issn.1008-7303.2021.0086

    土壤中烟嘧磺隆和莠去津残留对甘薯的药害评价

    Phytotoxicities of nicosulfuron and atrazine residues in soil on sweetpotato

    • 摘要: 为了明确玉米田除草剂烟嘧磺隆和莠去津土壤残留对后茬作物甘薯生长的影响,于2017年分别在河北省保定满城区、文安县、霸州市和石家庄藁城区采集甘薯田土壤样品,采用QuEChERS法,结合超高效液相色谱-串联质谱法 (UPLC-MS/MS) 测定了土壤中烟嘧磺隆和莠去津的残留量;通过盆栽试验,测定了烟嘧磺隆、莠去津以及二者混用对甘薯的药害作用。结果表明:在甘薯药害表现严重的河北保定满城区、文安县、霸州市3地甘薯田土壤中烟嘧磺隆的残留量在11.80~87.97 μg/(kg土) 之间,莠去津残留量在2.71~8.40 μg/(kg土) 之间;而在石家庄藁城区无药害症状甘薯田土壤中只检测到莠去津,含量在3.43~4.42 μg/(kg土) 之间。盆栽试验结果表明,栽后20 d每千克甘薯田土壤中烟嘧磺隆含量大于1 μg时,甘薯产生药害症状;烟嘧磺隆对甘薯根系IC50值为3.74 μg/(kg土),IC10值为1.27 μg/(kg土)。土壤中莠去津含量在2~40 μg/(kg土) 范围内,对甘薯茎叶和根系没有可见药害症状,但对根系生长具有轻微抑制作用。烟嘧磺隆与莠去津按质量比10 : 1、5 : 1、5 : 2和5 : 5混用对甘薯药害有一定的拮抗作用,共毒系数CTC50值分别为66.25、59.16、61.30和79.47。烟嘧磺隆对甘薯药害症状主要表现为植株矮小,叶片小,整株或心叶黄化,根系发育受阻,侧根短粗。生产上造成甘薯药害的诱因是土壤中残留的烟嘧磺隆,对甘薯药害阈值为1 μg/(kg土)。

       

      Abstract: To clarify the phytotoxicity of nicosulfuron and atrazine residues in the soil of corn fields on the growth of sweetpotato in the next year, the soil samples from sweetpotato fields were collected from Mancheng District of Baoding City, Wen’an County, Bazhou City and Gaocheng District of Shijiazhuang City of Hebei Province. The QuEChERS with ultra-performance liquid chromatography-mass spectrometry (UPLC-MS/MS) was used to determine their residues. The phytotoxicity of nicosulfuron, atrazine and their mixture in the soil on sweetpotato was evaluated in the pot experiments. The results showed that the residues of nicosulfuron in the soil of sweetpotato fields in Mancheng District of Baoding City, Wen’an County, and Bazhou City, of Hebei Province with severe phytotoxicity were 11.80-87.97 μg/kg soil, and the atrazine residues were 2.71-8.40 μg/kg soil. Only atrazine with the contents of 3.43-4.42 μg/kg soil was detected in the non-phytotoxic sweetpotato field in Gaocheng District of Shijiazhuang City, Hebei Province. The results of pot experiments with different herbicide treatments showed phytotoxic symptoms of sweetpotato 20 days after the treatment of 1 μg or more nicosulfuron per kilogram of soil. The IC50 value of nicosulfuron to roots was 3.74 μg/kg soil, while the IC10 value was 1.27 μg/kg soil. Atrazine in the range of 2-40 μg/kg soil have no visible phytotoxicity on the aboveground and underground parts of sweetpotato, but have slight inhibitory effect on the growth of the root system. The combination of nicosulfuron and atrazine in the ratio of 10 : 1, 5 : 1, 5 : 2 and 5 : 5 had antagonistic effect on sweetpotato phytotoxicity. Their co-toxicity coefficients CTC50 value were 66.25, 59.16, 61.30 and 79.47, respectively. The phytotoxic symptoms of nicosulfuron to sweetpotato included plants stunted, leaf blade smaller, whole plant or new leaves yellowish, rootlet development reduced, lateral roots short and thick. These results suggested that nicosulfuron is the main factor caused the phytotoxicity of sweetpotao, and its phytotoxic threshold was 1 μg/kg soil.

       

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