Ecology and Environment ›› 2021, Vol. 30 ›› Issue (6): 1269-1275.DOI: 10.16258/j.cnki.1674-5906.2021.06.018
• Research Articles • Previous Articles Next Articles
LI Tao1(), MENG Dandan2, GUO Shuiliang2, YUAN Guohui1, QIAN Zhenguan1, LV Weiguang1,*(
)
Received:
2020-12-26
Online:
2021-06-18
Published:
2021-09-10
Contact:
LV Weiguang
李涛1(), 孟丹丹2, 郭水良2, 袁国徽1, 钱振官1, 吕卫光1,*(
)
通讯作者:
吕卫光
作者简介:
李涛(1982年生),男,副研究员,硕士,主要从事杂草综合治理技术研究。E-mail: litao@saas.sh.cn
基金资助:
CLC Number:
LI Tao, MENG Dandan, GUO Shuiliang, YUAN Guohui, QIAN Zhenguan, LV Weiguang. Acute Toxicity of Seventeen Herbicides Commonly Used to Earthworm (Eisenia fetida)[J]. Ecology and Environment, 2021, 30(6): 1269-1275.
李涛, 孟丹丹, 郭水良, 袁国徽, 钱振官, 吕卫光. 17种常用除草剂对蚯蚓的急性毒性[J]. 生态环境学报, 2021, 30(6): 1269-1275.
Add to citation manager EndNote|Ris|BibTeX
URL: https://www.jeesci.com/EN/10.16258/j.cnki.1674-5906.2021.06.018
除草剂原药 Herbicide | 供试剂量 Test dose/ (μg∙cm-2) | t/h | 回归方程 Regression equation | LC50/ (μg∙cm-2) | 95%置信限 95% Confidence limits/(μg∙cm-2) | 相关系数r The correlation coefficient | 毒性等级 Toxicity grade |
---|---|---|---|---|---|---|---|
二氯喹啉酸 Quinclorac | 10, 100, 200, 500, 1000 | 24 | y= -7.51+5.66x | 161.8 | 59.3-441.6 | 0.873 | 低毒 Low toxicity |
48 | y= = -7.34+5.37x | 143.0 | 53.4-382.5 | 0.878 | 低毒 Low toxicity | ||
灭草松 Bentazone | 50, 60, 80, 90, 100 | 24 | y= -45.04+26.82x | 73.4 | 65.3-82.5 | 0.928 | 中毒 Medium toxicity |
48 | y= -33.19+21.36x | 61.3 | 50.3-74.7 | 0.875 | 中毒 Medium toxicity | ||
2甲4氯钠 MCPA-Na | 200, 400, 600, 800, 1000 | 24 | y= -13.79+7.82x | 252.4 | 152.2-418.8 | 0.900 | 低毒 Low toxicity |
48 | y= -13.10+7.88x | 198.2 | 118.5-331.6 | 0.927 | 低毒 Low toxicity | ||
噁唑酰草胺 Metamifop | 5, 10, 15, 20, 40 | 24 | y= -1.61+6.63x | 9.9 | 7.1-13.9 | 0.935 | 高毒 High toxicity |
48 | y= -1.78+7.69x | 7.6 | 4.9-11.8 | 0.924 | 高毒 High toxicity | ||
双草醚 Bispyribac-sodium | 200, 400, 600, 800, 1000 | 24 | y= -20.95+8.77x | 908.3 | 602.2-1369.9 | 0.910 | 低毒 Low toxicity |
48 | y= -17.99+8.17x | 649.2 | 500.2-842.7 | 0.935 | 低毒 Low toxicity | ||
丙草胺 Pretilachlor | 2, 4, 8, 10, 100 | 24 | y= -2.34+6.28x | 14.8 | 10.4-20.9 | 0.977 | 中毒 Medium toxicity |
48 | y= -0.60+5.45x | 10.7 | 7.7-14.8 | 0.977 | 中毒 Medium toxicity | ||
高效氟吡甲禾灵 Haloxyfop-R-methyl | 0.5, 1, 10, 50, 80 | 24 | y=0.52+2.94x | 33.3 | 23.0-48.3 | 0.992 | 中毒 Medium toxicity |
48 | y=0.49+4.08x | 12.7 | 6.0-27.1 | 0.953 | 中毒 Medium toxicity | ||
苯唑草酮 Topramezone | 100, 200, 400, 600, 800 | 24 | y= -21.57+10.95x | 266.4 | 205.6-345.3 | 0.960 | 低毒 Low toxicity |
48 | y= -21.19+11.27x | 211.1 | 147.7-301.6 | 0.941 | 低毒 Low toxicity | ||
烟嘧磺隆 Nicosulfuron | 200, 400, 600, 800, 1000 | 24 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity |
48 | y= -21.73+10.13x | 433.7 | 278.7-674.9 | 0.900 | 低毒 Slight toxicity | ||
草铵膦 Glufosinate ammonium | 200, 400, 600, 800, 1000 | 24 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity |
48 | ‒ | 466.9 | 374.6-581.9 | ‒ | 低毒 Low toxicity | ||
二甲戊灵 Pendimethalin | 200, 400, 600, 800, 1000 | 24 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity |
48 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity | ||
乙羧氟草醚 Fluoroglycofen | 200, 400, 600, 800, 1000 | 24 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity |
48 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity | ||
吡嘧磺隆 Pyrazosulfuron-ethyl | 200, 400, 600, 800, 1000 | 24 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity |
48 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity | ||
氰氟草酯 Cyhalofop-butyl | 200, 400, 600, 800, 1000 | 24 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity |
48 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity | ||
五氟磺草胺 Penoxsulam | 200, 400, 600, 80, 1000 | 24 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity |
48 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity | ||
硝磺草酮 Mesotrione | 200, 400, 600, 800, 1000 | 24 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity |
48 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity | ||
嘧啶肟草醚 Pyribenzoxim | 200, 400, 600, 800, 1000 | 24 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity |
48 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity |
Table 1 Acute toxicity of herbicides to Eisenia fetida by using filter paper contact test
除草剂原药 Herbicide | 供试剂量 Test dose/ (μg∙cm-2) | t/h | 回归方程 Regression equation | LC50/ (μg∙cm-2) | 95%置信限 95% Confidence limits/(μg∙cm-2) | 相关系数r The correlation coefficient | 毒性等级 Toxicity grade |
---|---|---|---|---|---|---|---|
二氯喹啉酸 Quinclorac | 10, 100, 200, 500, 1000 | 24 | y= -7.51+5.66x | 161.8 | 59.3-441.6 | 0.873 | 低毒 Low toxicity |
48 | y= = -7.34+5.37x | 143.0 | 53.4-382.5 | 0.878 | 低毒 Low toxicity | ||
灭草松 Bentazone | 50, 60, 80, 90, 100 | 24 | y= -45.04+26.82x | 73.4 | 65.3-82.5 | 0.928 | 中毒 Medium toxicity |
48 | y= -33.19+21.36x | 61.3 | 50.3-74.7 | 0.875 | 中毒 Medium toxicity | ||
2甲4氯钠 MCPA-Na | 200, 400, 600, 800, 1000 | 24 | y= -13.79+7.82x | 252.4 | 152.2-418.8 | 0.900 | 低毒 Low toxicity |
48 | y= -13.10+7.88x | 198.2 | 118.5-331.6 | 0.927 | 低毒 Low toxicity | ||
噁唑酰草胺 Metamifop | 5, 10, 15, 20, 40 | 24 | y= -1.61+6.63x | 9.9 | 7.1-13.9 | 0.935 | 高毒 High toxicity |
48 | y= -1.78+7.69x | 7.6 | 4.9-11.8 | 0.924 | 高毒 High toxicity | ||
双草醚 Bispyribac-sodium | 200, 400, 600, 800, 1000 | 24 | y= -20.95+8.77x | 908.3 | 602.2-1369.9 | 0.910 | 低毒 Low toxicity |
48 | y= -17.99+8.17x | 649.2 | 500.2-842.7 | 0.935 | 低毒 Low toxicity | ||
丙草胺 Pretilachlor | 2, 4, 8, 10, 100 | 24 | y= -2.34+6.28x | 14.8 | 10.4-20.9 | 0.977 | 中毒 Medium toxicity |
48 | y= -0.60+5.45x | 10.7 | 7.7-14.8 | 0.977 | 中毒 Medium toxicity | ||
高效氟吡甲禾灵 Haloxyfop-R-methyl | 0.5, 1, 10, 50, 80 | 24 | y=0.52+2.94x | 33.3 | 23.0-48.3 | 0.992 | 中毒 Medium toxicity |
48 | y=0.49+4.08x | 12.7 | 6.0-27.1 | 0.953 | 中毒 Medium toxicity | ||
苯唑草酮 Topramezone | 100, 200, 400, 600, 800 | 24 | y= -21.57+10.95x | 266.4 | 205.6-345.3 | 0.960 | 低毒 Low toxicity |
48 | y= -21.19+11.27x | 211.1 | 147.7-301.6 | 0.941 | 低毒 Low toxicity | ||
烟嘧磺隆 Nicosulfuron | 200, 400, 600, 800, 1000 | 24 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity |
48 | y= -21.73+10.13x | 433.7 | 278.7-674.9 | 0.900 | 低毒 Slight toxicity | ||
草铵膦 Glufosinate ammonium | 200, 400, 600, 800, 1000 | 24 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity |
48 | ‒ | 466.9 | 374.6-581.9 | ‒ | 低毒 Low toxicity | ||
二甲戊灵 Pendimethalin | 200, 400, 600, 800, 1000 | 24 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity |
48 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity | ||
乙羧氟草醚 Fluoroglycofen | 200, 400, 600, 800, 1000 | 24 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity |
48 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity | ||
吡嘧磺隆 Pyrazosulfuron-ethyl | 200, 400, 600, 800, 1000 | 24 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity |
48 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity | ||
氰氟草酯 Cyhalofop-butyl | 200, 400, 600, 800, 1000 | 24 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity |
48 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity | ||
五氟磺草胺 Penoxsulam | 200, 400, 600, 80, 1000 | 24 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity |
48 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity | ||
硝磺草酮 Mesotrione | 200, 400, 600, 800, 1000 | 24 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity |
48 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity | ||
嘧啶肟草醚 Pyribenzoxim | 200, 400, 600, 800, 1000 | 24 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity |
48 | ‒ | >1000.0 | ‒ | ‒ | 微毒 Slight toxicity |
除草剂原药 Herbicide | 供试剂量 Test dose/ (mg∙kg-1) | t/d | 回归方程 Regression equation | LC50/ (mg∙kg-1) | 95%置信限 95% Confidence limits/(mg∙kg-1) | 相关系数r The correlation coefficient | 毒性等级 Toxicity grade |
---|---|---|---|---|---|---|---|
二氯喹啉酸 Quinclorac | 100, 200, 500, 600, 800 | 7 | y= -11.70+5.54x | 1032.9 | 651.7-1637.0 | 0.957 | 低毒 Low toxicity |
14 | y= -8.62+4.77x | 715.0 | 401.0-1274.7 | 0.902 | 低毒 Low toxicity | ||
灭草松 Bentazone | 100, 200, 500, 600, 800 | 7 | y= -0.50+1.49x | 1062.3 | 971.5-1161.5 | 0.998 | 低毒 Low toxicity |
14 | y=2.47+0.90x | 649.5 | 527.1-800.2 | 0.983 | 低毒 Low toxicity | ||
2甲4氯钠 MCPA-Na | 200, 300, 400, 600, 800 | 7 | y= -19.42+9.65x | 340.3 | 256.5-451.6 | 0.903 | 低毒 Low toxicity |
14 | y= -19.44+9.68x | 335.0 | 256.0-438.3 | 0.913 | 低毒 Low toxicity | ||
噁唑酰草胺 Metamifop | 200, 300, 400, 500, 800 | 7 | ‒ | >800.0 | ‒ | ‒ | 低毒 Low toxicity |
14 | y= -20.05+9.87x | 345.7 | 257.4-464.3 | 0.881 | 低毒 Low toxicity | ||
双草醚 Bispyribac-sodium | 100, 200, 300, 400, 500, 600, 800 | 7 | ‒ | >800.0 | ‒ | ‒ | 低毒 Low toxicity |
14 | ‒ | >800.0 | ‒ | ‒ | 低毒 Low toxicity | ||
丙草胺 Pretilachlor | 50, 100, 200, 300, 500 | 7 | y=1.55+1.31x | 423.1 | 210.1-852.3 | 0.891 | 低毒 Low toxicity |
14 | y= -1.79+1.38x | 211.5 | 156.6-285.6 | 0.953 | 低毒 Low toxicity | ||
高效氟吡甲禾灵 Haloxyfop-R-methyl | 100, 150, 200, 500, 800, 1000 | 7 | y= -12.43+7.71x | 181.6 | 130.7-252.3 | 0.952 | 低毒 Low toxicity |
14 | y= -9.78+6.80x | 148.9 | 102.2-217.0 | 0.950 | 低毒 Low toxicity | ||
乙羧氟草醚 Fluoroglycofen | 200, 400, 500, 600, 800 | 7 | y= -15.50+6.92x | 914.4 | 677.3-1234.3 | 0.954 | 低毒 Low toxicity |
14 | y= -17.19+7.63x | 810.0 | 658.9-995.9 | 0.971 | 低毒 Low toxicity | ||
苯唑草酮 Topramezone | 200, 400, 500, 600, 800 | 7 | y= -3.14+2.79x | 832.7 | 567.4-1222.2 | 0.915 | 低毒 Low toxicity |
14 | y= -1.90+2.50x | 573.3 | 438.0-750.4 | 0.910 | 低毒 Low toxicity | ||
烟嘧磺隆 Nicosulfuron | 200, 400, 500, 600, 800 | 7 | y= -17.55+7.84x | 754.5 | 585.3-972.8 | 0.951 | 低毒 Low toxicity |
14 | y= -17.61+7.94x | 703.1 | 515.6-958.6 | 0.920 | 低毒 Low toxicity | ||
草铵膦 Glufosinate ammonium | 100, 150, 200, 300, 400, 500, 800 | 7 | ‒ | >800.0 | ‒ | ‒ | 低毒 Low toxicity |
14 | ‒ | >800.0 | ‒ | ‒ | 低毒 Low toxicity | ||
二甲戊灵 Pendimethalin | 200, 400, 500, 600, 800, 1000 | 7 | y= -13.72+6.98x | 480.3 | 293.0-787.4 | 0.721 | 低毒 Low toxicity |
14 | y= -17.64+8.93x | 342.4 | 220.9-530.6 | 0.829 | 低毒 Low toxicity | ||
吡嘧磺隆 Pyrazosulfuron-ethyl | 200, 400, 500, 600, 1000 | 7 | y= -15.33+6.53x | 1292.6 | 569.7-2933.0 | 0.843 | 低毒 Low toxicity |
14 | y= -5.87+4.10x | 883.2 | 573.5-1360.0 | 0.906 | 低毒 Low toxicity | ||
氰氟草酯 Cyhalofop-butyl | 100, 200, 300, 400, 500, 600, 800 | 7 | y= -0.57+1.29x | 2703.1 | 2087.4-3500.3 | 0.991 | 低毒 Low toxicity |
14 | y=0.66+1.31x | 2002.5 | 1083.6-3700.9 | 0.937 | 低毒 Low toxicity | ||
五氟磺草胺 Penoxsulam | 200, 400, 600, 600, 800, 1000 | 7 | y= -0.79+1.63x | 3645.4 | 1104.8-12028.0 | 0.887 | 低毒 Low toxicity |
14 | y=0.54+1.30x | 2756.4 | 1826.6-4159.3 | 0.979 | 低毒 Low toxicity | ||
硝磺草酮 Mesotrione | 200, 400, 500, 600, 800, 1000 | 7 | ‒ | >1000.0 | ‒ | ‒ | 低毒 Low toxicity |
14 | y= -0.44+1.67x | 1802.8 | 1082.0-3003.6 | 0.955 | 低毒 Low toxicity | ||
嘧啶肟草醚 Pyribenzoxim | 200, 400, 500, 600, 800, 1000 | 7 | y= -16.88+7.14x | 1164.9 | 588.9-2428.0 | 0.851 | 低毒 Low toxicity |
14 | y= -2.71+2.50x | 743.6 | 585.8-944.0 | 0.955 | 低毒 Low toxicity |
Table 2 Acute toxicity of herbicides to Eisenia fetida by using artificial soil test
除草剂原药 Herbicide | 供试剂量 Test dose/ (mg∙kg-1) | t/d | 回归方程 Regression equation | LC50/ (mg∙kg-1) | 95%置信限 95% Confidence limits/(mg∙kg-1) | 相关系数r The correlation coefficient | 毒性等级 Toxicity grade |
---|---|---|---|---|---|---|---|
二氯喹啉酸 Quinclorac | 100, 200, 500, 600, 800 | 7 | y= -11.70+5.54x | 1032.9 | 651.7-1637.0 | 0.957 | 低毒 Low toxicity |
14 | y= -8.62+4.77x | 715.0 | 401.0-1274.7 | 0.902 | 低毒 Low toxicity | ||
灭草松 Bentazone | 100, 200, 500, 600, 800 | 7 | y= -0.50+1.49x | 1062.3 | 971.5-1161.5 | 0.998 | 低毒 Low toxicity |
14 | y=2.47+0.90x | 649.5 | 527.1-800.2 | 0.983 | 低毒 Low toxicity | ||
2甲4氯钠 MCPA-Na | 200, 300, 400, 600, 800 | 7 | y= -19.42+9.65x | 340.3 | 256.5-451.6 | 0.903 | 低毒 Low toxicity |
14 | y= -19.44+9.68x | 335.0 | 256.0-438.3 | 0.913 | 低毒 Low toxicity | ||
噁唑酰草胺 Metamifop | 200, 300, 400, 500, 800 | 7 | ‒ | >800.0 | ‒ | ‒ | 低毒 Low toxicity |
14 | y= -20.05+9.87x | 345.7 | 257.4-464.3 | 0.881 | 低毒 Low toxicity | ||
双草醚 Bispyribac-sodium | 100, 200, 300, 400, 500, 600, 800 | 7 | ‒ | >800.0 | ‒ | ‒ | 低毒 Low toxicity |
14 | ‒ | >800.0 | ‒ | ‒ | 低毒 Low toxicity | ||
丙草胺 Pretilachlor | 50, 100, 200, 300, 500 | 7 | y=1.55+1.31x | 423.1 | 210.1-852.3 | 0.891 | 低毒 Low toxicity |
14 | y= -1.79+1.38x | 211.5 | 156.6-285.6 | 0.953 | 低毒 Low toxicity | ||
高效氟吡甲禾灵 Haloxyfop-R-methyl | 100, 150, 200, 500, 800, 1000 | 7 | y= -12.43+7.71x | 181.6 | 130.7-252.3 | 0.952 | 低毒 Low toxicity |
14 | y= -9.78+6.80x | 148.9 | 102.2-217.0 | 0.950 | 低毒 Low toxicity | ||
乙羧氟草醚 Fluoroglycofen | 200, 400, 500, 600, 800 | 7 | y= -15.50+6.92x | 914.4 | 677.3-1234.3 | 0.954 | 低毒 Low toxicity |
14 | y= -17.19+7.63x | 810.0 | 658.9-995.9 | 0.971 | 低毒 Low toxicity | ||
苯唑草酮 Topramezone | 200, 400, 500, 600, 800 | 7 | y= -3.14+2.79x | 832.7 | 567.4-1222.2 | 0.915 | 低毒 Low toxicity |
14 | y= -1.90+2.50x | 573.3 | 438.0-750.4 | 0.910 | 低毒 Low toxicity | ||
烟嘧磺隆 Nicosulfuron | 200, 400, 500, 600, 800 | 7 | y= -17.55+7.84x | 754.5 | 585.3-972.8 | 0.951 | 低毒 Low toxicity |
14 | y= -17.61+7.94x | 703.1 | 515.6-958.6 | 0.920 | 低毒 Low toxicity | ||
草铵膦 Glufosinate ammonium | 100, 150, 200, 300, 400, 500, 800 | 7 | ‒ | >800.0 | ‒ | ‒ | 低毒 Low toxicity |
14 | ‒ | >800.0 | ‒ | ‒ | 低毒 Low toxicity | ||
二甲戊灵 Pendimethalin | 200, 400, 500, 600, 800, 1000 | 7 | y= -13.72+6.98x | 480.3 | 293.0-787.4 | 0.721 | 低毒 Low toxicity |
14 | y= -17.64+8.93x | 342.4 | 220.9-530.6 | 0.829 | 低毒 Low toxicity | ||
吡嘧磺隆 Pyrazosulfuron-ethyl | 200, 400, 500, 600, 1000 | 7 | y= -15.33+6.53x | 1292.6 | 569.7-2933.0 | 0.843 | 低毒 Low toxicity |
14 | y= -5.87+4.10x | 883.2 | 573.5-1360.0 | 0.906 | 低毒 Low toxicity | ||
氰氟草酯 Cyhalofop-butyl | 100, 200, 300, 400, 500, 600, 800 | 7 | y= -0.57+1.29x | 2703.1 | 2087.4-3500.3 | 0.991 | 低毒 Low toxicity |
14 | y=0.66+1.31x | 2002.5 | 1083.6-3700.9 | 0.937 | 低毒 Low toxicity | ||
五氟磺草胺 Penoxsulam | 200, 400, 600, 600, 800, 1000 | 7 | y= -0.79+1.63x | 3645.4 | 1104.8-12028.0 | 0.887 | 低毒 Low toxicity |
14 | y=0.54+1.30x | 2756.4 | 1826.6-4159.3 | 0.979 | 低毒 Low toxicity | ||
硝磺草酮 Mesotrione | 200, 400, 500, 600, 800, 1000 | 7 | ‒ | >1000.0 | ‒ | ‒ | 低毒 Low toxicity |
14 | y= -0.44+1.67x | 1802.8 | 1082.0-3003.6 | 0.955 | 低毒 Low toxicity | ||
嘧啶肟草醚 Pyribenzoxim | 200, 400, 500, 600, 800, 1000 | 7 | y= -16.88+7.14x | 1164.9 | 588.9-2428.0 | 0.851 | 低毒 Low toxicity |
14 | y= -2.71+2.50x | 743.6 | 585.8-944.0 | 0.955 | 低毒 Low toxicity |
[1] |
BLOUIN M, HODSON M E, DELGADO E A, et al., 2013. A review of earthworm impact on soil function and ecosystem services[J]. European Journal of Soil Science, 64(2): 161-182.
DOI URL |
[2] | Fründ H C, Butt K, Capowiez Y, et al., 2010. Using earthworms as model organisms in the laboratory: Recommendations for experimental implementations[J]. Pedobiologia-International Journal of Soil Biology, 53(2): 119-125. |
[3] |
HACKENBERGER D K, STJEPANOVIĆ N, LONČARIĆ Ž, et al., 2018. Acute and subchronic effects of three herbicides on biomarkers and reproduction in earthworm Dendrobaena veneta[J]. Chemosphere, 208: 722-730.
DOI URL |
[4] |
HEIMBACH F, 1992. Correlation between data from laboratory and field tests for investigating the toxicity of pesticides to earthworms[J]. Soil Biology & Biochemistry, 24(12): 1749-1753.
DOI URL |
[5] |
JOUQUET P, PLUMERE T, THU T D, et al., 2010. The rehabilitation of tropical soils using compost and vermicompost is affected by the presence of endogeic earthworms[J]. Applied Soil Ecology, 46(1): 125-133.
DOI URL |
[6] | MANONO B, 2016. Agro-ecological role of earthworms (Oligochaetes) in sustainable agriculture and nutrient use efficiency: A review[J]. Journal of Agriculture and Ecology Research International, 8(1): 1-18. |
[7] | MUTHUKARUPPAN G, JANARDHANAN S, VIJAYALAKSHMI G, 2005. Sublethal toxicity of the herbicide butachlor on the earthworm Perionyx sansibaricus and its histological changes[J]. Journal of Soils & Sediments, 5(2): 82-86. |
[8] | OECD, 1984. OECD guideline for testing of chemicals, No. 207, earthworm, acute toxicity test [S]. Paris: OECD. |
[9] |
OJHA R B, DEVKOTA D, 2014. Earthworms: ‘Soil and ecosystem engineers'-a review[J]. World Journal of Agricultural Research, 2(26): 257-260.
DOI URL |
[10] | ROBERTS B L, DOROUGH H W, 1984. Relative toxicities of chemicals to the earthworm Eisenia foetida[J]. Environmental Toxicology & Chemistry, 3(1): 67-78. |
[11] |
SAXENA P N, GUPTA S K, MURTHY R C, 2014. Comparative toxicity of carbaryl, carbofuran, cypermethrin and fenvalerate in Metaphire posthuma and Eisenia fetida-A possible mechanism[J]. Ecotoxicology and Environmental Safety, 100(1): 218-225.
DOI URL |
[12] |
TRIPATHI G, KACHHWAHA N, DABI I, 2010. Comparative studies on carbofuran-induced changes in some cytoplasmic and mitochondrial enzymes and proteins of epigeic, anecic and endogeic earthworms[J]. Pesticide Biochemical Physiology, 96(1): 30-35.
DOI URL |
[13] |
UDOVIC M, LESTAN D, 2010. Eisenia fetida avoidance behavior as a tool for assessing the efficiency of remediation of Pb, Zn and Cd polluted soil[J]. Environment Pollution, 158(8): 2766-2772.
DOI URL |
[14] |
WANG Y H, WU S G, CHEN L P, et al., 2012a. Toxicity assessment of 45 pesticides to the epigeic earthworm Eisenia fetida[J]. Chemosphere, 88(4): 484-491.
DOI URL |
[15] |
WANG Y H, CANG T, ZHAO X P, et al., 2012b. Comparative acute toxicity of twenty-four insecticides to earthworm, Eisenia fetida[J]. Ecotoxicology and Environmental Safety, 79: 122-128.
DOI URL |
[16] | WANG Z Z, ZHANG Y M, GUO Y C, et al., 2000. Effects of organophosphorus pesticide pollution on soil animals[J]. Journal of Environmental Sciences, 12(1): 47-56. |
[17] | ZAREA M J, KARIMI N, 2012. Effect of ferbicides on earthworms[J]. Dynamic Soil, Dynamic Plant, 6(1): 5-13. |
[18] | 陈爱梅, 王金花, 夏晓明, 等, 2013. 不同剂型吡虫啉对蚯蚓和斑马鱼的急性毒性评价[J]. 农业环境科学学报, 32(9): 1758-1763. |
CHEN A M, WANG J H, XIA X M et al., 2013. Acute toxicity of imidacloprid with different formulation on earthworm and zebrafish[J]. Journal of Agro-Environment Science, 32(9): 1758-1763. | |
[19] | 付青, 昌盛, 樊月婷, 等, 2019. 北江清远段有机氯农药的污染特征与风险评估[J]. 生态环境学报, 28(8): 1656-1663. |
FU Q, CHANG S, FAN Y T, et al., 2019. Pollution characteristics and risk assessment of organochloride pesticides in the Qingyuan section of Beijiang river[J]. Ecology and Environmental Sciences, 28(8): 1656-1663. | |
[20] | 郭佳惠, 孔云, 李刚, 等, 2016. 转基因作物对土壤无脊椎动物的影响[J]. 生态学杂志, 35(10): 2838-2844. |
GUO J H, KONG Y, LI G, et al., 2016. Impact of genetically modified crops on soil invertebrates[J]. Chinese Journal of Ecology, 35(10): 2838-2844. | |
[21] | 姜锦林, 程燕, 卜元卿, 等, 2014. 农药对蚯蚓的生长和繁殖毒性及其在生态风险评价中的应用[J]. 农药科学与管理, 35(9): 23-32. |
JIANG J L, CHENG Y, BU Y Q, et al., 2014. Effects of pesticides on the growth and reproduction of earthworm and its application in ecological risk assessment[J]. Pesticide Science and Administration, 35(9): 23-32. | |
[22] | 林涛, 游泳, 傅建炜, 等, 2015. 9种农药对家蚕和蚯蚓的急性毒性[J]. 生物安全学报, 24(3): 248-251. |
LIN T, YOU Y, FU J W, et al., 2015. Acute toxicitv ot nine pesticides to the silkworm, Bombyx mori and the earthworm Eisenia foetida[J]. Journal of Biosafety, 24(3): 248-251. | |
[23] | 蒲生彦, 上官李想, 刘世宾, 等, 2019. 生物炭及其复合材料在土壤污染修复中的应用研究进展[J]. 生态环境学报, 28(3): 629-635. |
PU S Y, SHANG G L X, LIU S B, et al., 2019. A review of the application of biochar and its composites in soil remediation[J]. Ecology and Environmental Sciences, 28(3): 629-635. | |
[24] | 宋雪英, 崔小维, 李嘉康, 等, 2016. 邻苯二甲酸酯类塑化剂的土壤生态毒理学研究进展[J]. 生态环境学报, 25(11): 1885-1890. |
SONG X Y, CUI X W, LI J K, et al., 2016. Research advances in soil ecotoxicology of phthalic acid esters (PAEs) exposure[J]. Ecology and Environmental Sciences, 25(11): 1885-1890. | |
[25] | 谭华东, 李勤奋, 张汇杰, 等, 2021. 南渡江农业土壤中农药分布特征与生态风险评估[J]. 生态环境学报, 30(1): 181-189. |
TAN H D, LI Q F, ZHANG H F, et al., 2021. Distribution and ecotoxicological risk of current-use pesticides in agricultural soil from Nandu River basin in Hainan[J]. Ecology and Environmental Sciences, 30(1): 181-189. | |
[26] | 王飞菲, 郑梦梦, 刘树海, 等, 2014. 两种除草剂对蚯蚓的急性毒性及氧化胁迫效应[J]. 生态毒理学报, 9(6): 1210-1218. |
WANG F F, ZHENG M M, LIU S H, et al., 2014. Acute toxicity and oxidative stress of two herbicides on earthworm Eisenia fetida [J]. Asian Journal of Eeotoxicology, 9(6): 1210-1218. | |
[27] | 王彦华, 俞卫华, 杨立之, 等, 2012. 22种常用除草剂对蚯蚓 (Eisenia fetida) 的急性毒性[J]. 生态毒理学报, 7(3): 317-325. |
WANG Y H, YU W H, YANG L Z, et al., 2012. Acute toxicity of twenty-two commonly used herbicides to earthworm (Eisenia fetida)[J]. Asian Journal of Ecotoxicology, 7(3): 317-325. | |
[28] | 吴娜娜, 钱虹, 郑璐, 等, 2015. 氮沉降增加对原始阔叶红松林蚯蚓种类和数量的影响[J]. 生态环境学报, 24(11): 1814-1817. |
WU N N, QIAN H, ZHENG L, et al., 2015. Effects of elevated nitrogen deposition on earthworm species and density in mixed broad-leaf Korean Pine Forest in Changbai Mountain[J]. Ecology and Environmental Sciences, 24(11): 1814-1817. | |
[29] | 张慧琦, 王坤, 岳士忠, 等, 2017. 土壤镉污染对赤子爱胜蚓 (Eisenia fetida) 和加州腔蚓 (Metaphire californica) 体表角质层的影响[J]. 生态环境学报, 2017, 26(10): 1807-1813. |
ZHANG H Q, WANG K, YUE S Z, et al., 2017. The impact of soil cadmium on the ultrastructural cuticle of two earthworms species Eisenia fetida and Metaphire californica[J]. Ecology and Environmental Sciences, 26(10): 1807-1813. | |
[30] | 中华人民共和国农业部, 2014. 化学农药环境安全评价试验准则第15部分: 蚯蚓急性毒性试验: GB/T 31270.15—2014 [S]. 北京: 中国标准出版社: 6. |
Ministry of Agriculture of the People's Republic of China, 2014. Test guidelines on environmental safety assessment for chemical pesticides-Part 15: Earthworm acute toxicity test: GB/T 31270.15- 2014 [S]. Beijing: China Standard Press: 6. |
[1] | YOU Hongjian, ZHANG Wenwen, LAN Zhengfang, MA Lan, ZHANG Baodi, MU Xiaokun, LI Wenhui, CAO Yune. Effects of Earthworm in-situ Composting and Biochar on Cucumber Root-knot Nematodes and Rhizosphere Microorganisms [J]. Ecology and Environment, 2023, 32(1): 99-109. |
[2] | LIU Kehui, LI Guangluan, LI Chunming, ZHAO Keyi, ZHANG Ningning, XUE Jieyi, LI Yi, YU Fangming, DUAN Min. A Review of Research on Lijiang Ecological Environment Based on Bibliometric and Knowledge Mapping Analysis Over the Past Four Decades [J]. Ecology and Environment, 2022, 31(2): 409-420. |
[3] | LIU Qiang, YANG Zhongyang, CHEN Yiqing, LEI Jinrui, CHEN Zongzhu, CHEN Xiaohua. Multi-scenario Simulation of Land Use Change and Its Eco-environmental Effect in Hainan Island Based on CA-Markov Model [J]. Ecology and Environment, 2021, 30(7): 1522-1531. |
[4] | ZHANG Xiaojin, DAI Zhengwei, DAI Yu, DAI Guofei, YANG Ping, FANG Yuanyuan, PENG Ningyan. Research Progress on the Methods of Simultaneous Algae Control and Microcystin Removal [J]. Ecology and Environment, 2021, 30(7): 1549-1554. |
Viewed | ||||||
Full text |
|
|||||
Abstract |
|
|||||
Copyright © 2021 Editorial Office of ACTA PETROLEI SINICA
Address:No. 6 Liupukang Street, Xicheng District, Beijing, P.R.China, 510650
Tel: 86-010-62067128, 86-010-62067137, 86-010-62067139
Fax: 86-10-62067130
Email: syxb@cnpc.com.cn
Support byBeijing Magtech Co.ltd, E-mail:support@magtech.com.cn