浙江农业学报 ›› 2022, Vol. 34 ›› Issue (11): 2512-2521.DOI: 10.3969/j.issn.1004-1524.2022.11.20
收稿日期:
2021-05-23
出版日期:
2022-11-25
发布日期:
2022-11-29
通讯作者:
徐明飞
作者简介:
*徐明飞,E-mail: 280971884@qq.com基金资助:
LYU Lu(), WU Shenggan, WANG Qiang, ZHAO Xueping, XU Mingfei(
)
Received:
2021-05-23
Online:
2022-11-25
Published:
2022-11-29
Contact:
XU Mingfei
摘要:
葡萄在种植过程中,易感染真菌性病害。即使有大量已登记的杀菌剂产品,仍有未登记的杀菌剂被用于防治或被推荐用于防治葡萄真菌性病害。未登记杀菌剂的施用是否会对葡萄园环境生物造成危害,需引起足够的关注。本研究选取葡萄上未登记但有残留检出或被推荐使用的杀菌剂三唑酮、乙霉威、四氟醚唑、吡唑萘菌胺、乙烯菌核利,对葡萄园环境生物鸟类、蜜蜂、非靶标节肢动物及土壤生物进行了初级风险评估。结果显示,三唑酮及四氟醚唑对鸟类的长期暴露风险商值大于1,风险不可接受;乙霉威对捕食性非靶标节肢动物的危害商值大于5,初级风险不可接受。吡唑萘菌胺及乙烯菌核利对所评估的陆生生物风险均可接受。本研究为所选杀菌剂在葡萄上的科学施用及后续的农药登记提供参考。
中图分类号:
吕露, 吴声敢, 王强, 赵学平, 徐明飞. 几种杀菌剂对葡萄园典型陆生生物的初级风险评估[J]. 浙江农业学报, 2022, 34(11): 2512-2521.
LYU Lu, WU Shenggan, WANG Qiang, ZHAO Xueping, XU Mingfei. Primary risk assessment of several fungicides to typical vineyard terrestrial organisms[J]. Acta Agriculturae Zhejiangensis, 2022, 34(11): 2512-2521.
杀菌剂 Fungicide | 含量剂型 Formulation | 登记作物 Crop | 施药方法 Application method | 制剂施药量 Application rate of preparation | 有效成分施药量 Application rate of active ingredient/ (g·hm-2) | 施药次数 Number of applications | 施药间隔 Time interval/d |
---|---|---|---|---|---|---|---|
三唑酮 Triadimefon | 25%可湿性粉剂 25% Wettable powder | 小麦 Wheat | 喷雾 Spray | 750~1 200 g·hm-2 | 300 | 2 | 7 |
乙霉·多菌灵 Diethofencarb· carbendazim | 50%可湿性粉剂(乙霉 威25%,多菌灵25%) 50% Wettable powder (diethofencarb 25%, carbendazim 25%) | 番茄 Tomato | 喷雾 Spray | 1 500~2 250 g·hm-2 | 562.5(乙霉威 diethofencarb) | 2 | 10 |
四氟醚唑 Tetraconazole | 4%水乳剂 4% emulsion, oil in water | 黄瓜/甜瓜 Cucumber/ muskmelon | 喷雾 Spray | 1 000~1 500 g·hm-2 | 60 | 3 | 10 |
吡萘·嘧菌酯 Isopyrazam· azoxystrobin | 29%悬浮剂(吡唑萘菌胺 11.2%,嘧菌酯17.8%) 29% Suspension concentrate (isopyrazam 11.2%, azoxystrobin 17.8%) | 西瓜 Watermelon | 喷雾 Spray | 450~900 mL·hm-2 | 100.8(吡唑萘菌胺 isopyrazam) | 3 | 7 |
乙烯菌核利 Vinclozolin | 50%干悬浮剂 50% Dry flowable | 番茄 Tomato | 喷雾 Spray | 1 125~1 500 g·hm-2 | 750 | 3 | 7 |
表1 所选杀菌剂的田间施用信息
Table 1 Application information of the selected fungicides in field
杀菌剂 Fungicide | 含量剂型 Formulation | 登记作物 Crop | 施药方法 Application method | 制剂施药量 Application rate of preparation | 有效成分施药量 Application rate of active ingredient/ (g·hm-2) | 施药次数 Number of applications | 施药间隔 Time interval/d |
---|---|---|---|---|---|---|---|
三唑酮 Triadimefon | 25%可湿性粉剂 25% Wettable powder | 小麦 Wheat | 喷雾 Spray | 750~1 200 g·hm-2 | 300 | 2 | 7 |
乙霉·多菌灵 Diethofencarb· carbendazim | 50%可湿性粉剂(乙霉 威25%,多菌灵25%) 50% Wettable powder (diethofencarb 25%, carbendazim 25%) | 番茄 Tomato | 喷雾 Spray | 1 500~2 250 g·hm-2 | 562.5(乙霉威 diethofencarb) | 2 | 10 |
四氟醚唑 Tetraconazole | 4%水乳剂 4% emulsion, oil in water | 黄瓜/甜瓜 Cucumber/ muskmelon | 喷雾 Spray | 1 000~1 500 g·hm-2 | 60 | 3 | 10 |
吡萘·嘧菌酯 Isopyrazam· azoxystrobin | 29%悬浮剂(吡唑萘菌胺 11.2%,嘧菌酯17.8%) 29% Suspension concentrate (isopyrazam 11.2%, azoxystrobin 17.8%) | 西瓜 Watermelon | 喷雾 Spray | 450~900 mL·hm-2 | 100.8(吡唑萘菌胺 isopyrazam) | 3 | 7 |
乙烯菌核利 Vinclozolin | 50%干悬浮剂 50% Dry flowable | 番茄 Tomato | 喷雾 Spray | 1 125~1 500 g·hm-2 | 750 | 3 | 7 |
杀菌剂 Fungicide | 生物类别 Category | 物种名称 Species | 毒性终点 End point | 毒性值 Toxicity | 数据来源 Data source |
---|---|---|---|---|---|
三唑酮 Triadimefon | 鸟类 Birds | 北美鹌鹑 Bobwhite quail | 急性经口毒性LD50 Acute LD50/(mg·kg-1·d-1) | >2 000 | [ |
北美鹌鹑 Bobwhite quail | 短期饲喂毒性LC50 Short-term LC50/(mg·kg-1·d-1) | 8 392 | |||
北美鹌鹑 Bobwhite quail | 繁殖毒性NOEL Long-term NOEL/(mg·kg-1·d-1) | 20 | |||
蜜蜂 Honeybees | 意大利蜜蜂 Apis mellifera | 急性接触毒性LD50/(μg·蜂-1) Acute contact toxicity LD50/(μg·bee-1) | >25 | ||
土壤生物 Soil organisms | 赤子爱胜蚓 Eisenia foetida | 14 d急性LC50 Acute LC50 for 14 days/(mg·kg-1) | >50 | [ | |
吡唑萘菌胺 Isopyrazam | 鸟类 Birds | 山齿鹑 Colinus virginianus | 急性经口毒性LD50 Acute LD50/(mg·kg-1·d-1) | >2 000 | [ |
山齿鹑 Colinus virginianus | 短期饲喂毒性LD50 Short-term LD50/(mg·kg-1·d-1) | 1 310 | |||
山齿鹑 Colinus virginianus | 繁殖毒性NOEL Long-term NOEL/(mg·kg-1·d-1) | 32.5 | |||
蜜蜂 Honeybees | 意大利蜜蜂 Apis mellifera | 急性经口毒性LD50/(μg·蜂-1) Acute oral toxicity LD50/(μg·bee-1) | >95.5 | ||
急性接触毒性LD50/(μg·蜂-1) Acute contact toxicity LD50/(μg·bee-1) | >100 | ||||
非靶标节肢动 物Non-target arthropods | 梨盲走螨 Typhlodromus pyri | 急性毒性LR50 Acute LR50/(g·hm-2) | 174.75 | ||
蚜茧蜂 Aphidius rhopalosiphi | 急性毒性LR50 Acute LR50/(g·hm-2) | 41.2 | |||
杀菌剂 Fungicide | 生物类别 Category | 物种名称 Species | 毒性终点 End point | 毒性值 Toxicity | 数据来源 Data source |
土壤生物 Soil organisms | 赤子爱胜蚓 Eisenia foetida | 14 d急性LC50 Acute LC50 for 14 days/(mg·kg-1) | >500 | ||
土壤微生物(氮转化) Soil micro-organisms (Nitrogen mineralisation) | 28 d-NOEC | 1.67 mg·kg-1剂量下, 效应最大为14.8% Maximum effect was 14.8% at 1.67 mg·kg-1 | |||
乙霉威 Diethofencarb | 鸟类 Birds | 绿头鸭 Anas platyrhynchos | 急性经口毒性LD50 Acute LD50/(mg·kg-1·d-1) | >2 250 | [ |
山齿鹑 Colinus virginianus | 急性经口毒性LD50 Acute LD50/(mg·kg-1·d-1) | >2 250 | |||
绿头鸭 Anas platyrhynchos | 短期饲喂毒性LD50 Short-term LD50/(mg·kg-1·d-1) | >1 629 | |||
山齿鹑 Colinus virginianus | 短期饲喂毒性LD50 Short-term LD50/(mg·kg-1·d-1) | >1 813 | |||
山齿鹑 Colinus virginianus | 繁殖毒性NOEL Long-term NOEL/(mg·kg-1·d-1) | 78.7 | |||
蜜蜂 Honeybees | 意大利蜜蜂 Apis mellifera | 急性经口毒性LD50/(μg·蜂-1) Acute oral toxicity LD50/(μg·bee-1) | >100 | ||
急性接触毒性LD50/(μg·蜂-1) Acute contact toxicity LD50/(μg·bee-1) | >100 | ||||
非靶标节肢动 物Non-target arthropods | 蚜茧蜂 Aphidius rhopalosiphi | 急性毒性LR50 Acute LR50/(g·hm-2) | >1 500 | ||
梨盲走螨 Typhlodromus pyri | 急性毒性LR50 Acute LR50/(g·hm-2) | 7.2 | |||
土壤生物 Soil organisms | 赤子爱胜蚓 Eisenia foetida | 14 d急性LC50 Acute LC50 for 14 days/(mg·kg-1) | >500 | ||
土壤微生物(氮转化) Soil micro-organisms (Nitrogen mineralisation) | 28 d-NOEC | 7 mg·kg-1剂量下, 效应<25% Effect<25% at 7 mg·kg-1 | |||
四氟醚唑 Tetraconazole | 鸟类 Birds | 北美鹌鹑 Bobwhite quail | 急性经口毒性LD50 Acute LD50/(mg·kg-1·d-1) | 132 | [ |
野鸭 Mallard duck | 短期饲喂毒性LD50 Short-term LD50/(mg·kg-1·d-1) | 55.2 | |||
野鸭 Mallard duck | 繁殖毒性NOEL Long-term NOEL/(mg·kg-1·d-1) | 1.6 | |||
蜜蜂 Honeybees | 意大利蜜蜂 Apis mellifera | 急性经口毒性LD50/(μg·蜂-1) Acute oral toxicity LD50/(μg·bee-1) | >130 | ||
急性接触毒性LD50/(μg·蜂-1) Acute contact toxicity LD50/(μg·bee-1) | 63 | ||||
非靶标节肢动 物Non-target arthropods | 蚜茧蜂 Aphidius rhopalosiphi | 急性毒性LR50 Acute LR50/(g·hm-2) | 125 | ||
草蛉Chrysoperla carnea | 急性毒性LR50 Acute LR50/(g·hm-2) | >250 | |||
土壤生物 Soil organisms | 赤子爱胜蚓 Eisenia foetida | 14 d急性LC50 Acute LC50 for 14 days/(mg·kg-1) | 71 | ||
土壤微生物(氮转化) Soil micro-organisms (Nitrogen mineralisation) | 28 d-NOEC | 0.502 mg·kg-1剂量下, 效应<25% Effect<25% at 0.502 mg·kg-1 | |||
杀菌剂 Fungicide | 生物类别 Category | 物种名称 Species | 毒性终点 End point | 毒性值 Toxicity | 数据来源 Data source |
乙烯菌核利 Vinclozolin | 鸟类 Birds | 绿头鸭 Anas platyrhynchos | 急性经口毒性LD50 Acute LD50/(mg·kg-1·d-1) | >5 629 | [ |
蜜蜂 Honeybees | 意大利蜜蜂 Apis mellifera | 急性经口毒性LD50/(μg·蜂-1) Acute oral toxicity LD50/(μg·bee-1) | >100 | ||
土壤生物 Soil organisms | 赤子爱胜蚓 Eisenia foetida | 14 d急性LC50 Acute LC50 for 14 days/(mg·kg-1) | >1 000 |
表2 所选杀菌剂对陆生生物的毒性效应数据
Table 2 Toxicity data of the selected fungicides to terrestrial organisms
杀菌剂 Fungicide | 生物类别 Category | 物种名称 Species | 毒性终点 End point | 毒性值 Toxicity | 数据来源 Data source |
---|---|---|---|---|---|
三唑酮 Triadimefon | 鸟类 Birds | 北美鹌鹑 Bobwhite quail | 急性经口毒性LD50 Acute LD50/(mg·kg-1·d-1) | >2 000 | [ |
北美鹌鹑 Bobwhite quail | 短期饲喂毒性LC50 Short-term LC50/(mg·kg-1·d-1) | 8 392 | |||
北美鹌鹑 Bobwhite quail | 繁殖毒性NOEL Long-term NOEL/(mg·kg-1·d-1) | 20 | |||
蜜蜂 Honeybees | 意大利蜜蜂 Apis mellifera | 急性接触毒性LD50/(μg·蜂-1) Acute contact toxicity LD50/(μg·bee-1) | >25 | ||
土壤生物 Soil organisms | 赤子爱胜蚓 Eisenia foetida | 14 d急性LC50 Acute LC50 for 14 days/(mg·kg-1) | >50 | [ | |
吡唑萘菌胺 Isopyrazam | 鸟类 Birds | 山齿鹑 Colinus virginianus | 急性经口毒性LD50 Acute LD50/(mg·kg-1·d-1) | >2 000 | [ |
山齿鹑 Colinus virginianus | 短期饲喂毒性LD50 Short-term LD50/(mg·kg-1·d-1) | 1 310 | |||
山齿鹑 Colinus virginianus | 繁殖毒性NOEL Long-term NOEL/(mg·kg-1·d-1) | 32.5 | |||
蜜蜂 Honeybees | 意大利蜜蜂 Apis mellifera | 急性经口毒性LD50/(μg·蜂-1) Acute oral toxicity LD50/(μg·bee-1) | >95.5 | ||
急性接触毒性LD50/(μg·蜂-1) Acute contact toxicity LD50/(μg·bee-1) | >100 | ||||
非靶标节肢动 物Non-target arthropods | 梨盲走螨 Typhlodromus pyri | 急性毒性LR50 Acute LR50/(g·hm-2) | 174.75 | ||
蚜茧蜂 Aphidius rhopalosiphi | 急性毒性LR50 Acute LR50/(g·hm-2) | 41.2 | |||
杀菌剂 Fungicide | 生物类别 Category | 物种名称 Species | 毒性终点 End point | 毒性值 Toxicity | 数据来源 Data source |
土壤生物 Soil organisms | 赤子爱胜蚓 Eisenia foetida | 14 d急性LC50 Acute LC50 for 14 days/(mg·kg-1) | >500 | ||
土壤微生物(氮转化) Soil micro-organisms (Nitrogen mineralisation) | 28 d-NOEC | 1.67 mg·kg-1剂量下, 效应最大为14.8% Maximum effect was 14.8% at 1.67 mg·kg-1 | |||
乙霉威 Diethofencarb | 鸟类 Birds | 绿头鸭 Anas platyrhynchos | 急性经口毒性LD50 Acute LD50/(mg·kg-1·d-1) | >2 250 | [ |
山齿鹑 Colinus virginianus | 急性经口毒性LD50 Acute LD50/(mg·kg-1·d-1) | >2 250 | |||
绿头鸭 Anas platyrhynchos | 短期饲喂毒性LD50 Short-term LD50/(mg·kg-1·d-1) | >1 629 | |||
山齿鹑 Colinus virginianus | 短期饲喂毒性LD50 Short-term LD50/(mg·kg-1·d-1) | >1 813 | |||
山齿鹑 Colinus virginianus | 繁殖毒性NOEL Long-term NOEL/(mg·kg-1·d-1) | 78.7 | |||
蜜蜂 Honeybees | 意大利蜜蜂 Apis mellifera | 急性经口毒性LD50/(μg·蜂-1) Acute oral toxicity LD50/(μg·bee-1) | >100 | ||
急性接触毒性LD50/(μg·蜂-1) Acute contact toxicity LD50/(μg·bee-1) | >100 | ||||
非靶标节肢动 物Non-target arthropods | 蚜茧蜂 Aphidius rhopalosiphi | 急性毒性LR50 Acute LR50/(g·hm-2) | >1 500 | ||
梨盲走螨 Typhlodromus pyri | 急性毒性LR50 Acute LR50/(g·hm-2) | 7.2 | |||
土壤生物 Soil organisms | 赤子爱胜蚓 Eisenia foetida | 14 d急性LC50 Acute LC50 for 14 days/(mg·kg-1) | >500 | ||
土壤微生物(氮转化) Soil micro-organisms (Nitrogen mineralisation) | 28 d-NOEC | 7 mg·kg-1剂量下, 效应<25% Effect<25% at 7 mg·kg-1 | |||
四氟醚唑 Tetraconazole | 鸟类 Birds | 北美鹌鹑 Bobwhite quail | 急性经口毒性LD50 Acute LD50/(mg·kg-1·d-1) | 132 | [ |
野鸭 Mallard duck | 短期饲喂毒性LD50 Short-term LD50/(mg·kg-1·d-1) | 55.2 | |||
野鸭 Mallard duck | 繁殖毒性NOEL Long-term NOEL/(mg·kg-1·d-1) | 1.6 | |||
蜜蜂 Honeybees | 意大利蜜蜂 Apis mellifera | 急性经口毒性LD50/(μg·蜂-1) Acute oral toxicity LD50/(μg·bee-1) | >130 | ||
急性接触毒性LD50/(μg·蜂-1) Acute contact toxicity LD50/(μg·bee-1) | 63 | ||||
非靶标节肢动 物Non-target arthropods | 蚜茧蜂 Aphidius rhopalosiphi | 急性毒性LR50 Acute LR50/(g·hm-2) | 125 | ||
草蛉Chrysoperla carnea | 急性毒性LR50 Acute LR50/(g·hm-2) | >250 | |||
土壤生物 Soil organisms | 赤子爱胜蚓 Eisenia foetida | 14 d急性LC50 Acute LC50 for 14 days/(mg·kg-1) | 71 | ||
土壤微生物(氮转化) Soil micro-organisms (Nitrogen mineralisation) | 28 d-NOEC | 0.502 mg·kg-1剂量下, 效应<25% Effect<25% at 0.502 mg·kg-1 | |||
杀菌剂 Fungicide | 生物类别 Category | 物种名称 Species | 毒性终点 End point | 毒性值 Toxicity | 数据来源 Data source |
乙烯菌核利 Vinclozolin | 鸟类 Birds | 绿头鸭 Anas platyrhynchos | 急性经口毒性LD50 Acute LD50/(mg·kg-1·d-1) | >5 629 | [ |
蜜蜂 Honeybees | 意大利蜜蜂 Apis mellifera | 急性经口毒性LD50/(μg·蜂-1) Acute oral toxicity LD50/(μg·bee-1) | >100 | ||
土壤生物 Soil organisms | 赤子爱胜蚓 Eisenia foetida | 14 d急性LC50 Acute LC50 for 14 days/(mg·kg-1) | >1 000 |
参数 Parameters | 输入值 Input values | 备注 Notes | |||||
---|---|---|---|---|---|---|---|
三唑酮 Triadimefon | 乙霉威 Diethofencarb | 四氟醚唑 Tetraconazole | 吡唑萘菌胺 Isopyrazam | 乙烯菌核利 Vinclozolin | |||
土壤降解半衰期 Half-life in soil/d | 26 | 4.72 | 83.3 | 84 | 40.5 | [19-21,23,24] | |
土壤容重 Soil density/(kg·m-3) | 1 500 | 1 500 | 1 500 | 1 500 | 1 500 | 默认值 Default values | |
土壤深度 Depth/m | 0.05 | 0.05 | 0.05 | 0.05 | 0.05 | 喷施农药默认分布在0~0.05 m的土壤表层 By default, the spraying pesticide is distributed in the surface layer of soil at 0-0.05 m | |
作物名称 Name of crops | 烟草 Tobacco | 烟草 Tobacco | 烟草 Tobacco | 烟草 Tobacco | 烟草 Tobacco | — | |
农药施用时期 Growth stage (BBCH) | 0-09 | 0-09 | 0-09 | 0-09 | 0-09 | 模型以此计算作物截留系数 The crop interception coefficient was calculated based on BBCH | |
施用次数 Number of applications | 2 | 2 | 3 | 3 | 3 | — | |
施药量 | 300 | 562.5 | 60 | 100.8 | 750 | — | |
Application rate/ (g·hm-2) | |||||||
施用间隔期 Time interval/d | 7 | 10 | 10 | 7 | 7 | 多次施药的间隔时间 Interval time of multiple applications |
表3 土壤生物风险评估PECsoil_SFO_China (xls)模型的输入参数
Table 3 Input parameters of PECsoil_SFO_China (xls) model for soil organisms risk assessment
参数 Parameters | 输入值 Input values | 备注 Notes | |||||
---|---|---|---|---|---|---|---|
三唑酮 Triadimefon | 乙霉威 Diethofencarb | 四氟醚唑 Tetraconazole | 吡唑萘菌胺 Isopyrazam | 乙烯菌核利 Vinclozolin | |||
土壤降解半衰期 Half-life in soil/d | 26 | 4.72 | 83.3 | 84 | 40.5 | [19-21,23,24] | |
土壤容重 Soil density/(kg·m-3) | 1 500 | 1 500 | 1 500 | 1 500 | 1 500 | 默认值 Default values | |
土壤深度 Depth/m | 0.05 | 0.05 | 0.05 | 0.05 | 0.05 | 喷施农药默认分布在0~0.05 m的土壤表层 By default, the spraying pesticide is distributed in the surface layer of soil at 0-0.05 m | |
作物名称 Name of crops | 烟草 Tobacco | 烟草 Tobacco | 烟草 Tobacco | 烟草 Tobacco | 烟草 Tobacco | — | |
农药施用时期 Growth stage (BBCH) | 0-09 | 0-09 | 0-09 | 0-09 | 0-09 | 模型以此计算作物截留系数 The crop interception coefficient was calculated based on BBCH | |
施用次数 Number of applications | 2 | 2 | 3 | 3 | 3 | — | |
施药量 | 300 | 562.5 | 60 | 100.8 | 750 | — | |
Application rate/ (g·hm-2) | |||||||
施用间隔期 Time interval/d | 7 | 10 | 10 | 7 | 7 | 多次施药的间隔时间 Interval time of multiple applications |
杀菌剂 Fungicides | AR/ (g·hm-2) | PEDacute/ (mg·kg-1·d-1) | 毒性终点 End point/(mg·kg-1·d-1) | PNED/ (mg·kg-1·d-1) | RQ |
---|---|---|---|---|---|
三唑酮Triadimefon | 300.0 | 10.0 | 2 000 | 200.0 | 0.050 2 |
乙霉威Diethofencarb | 562.5 | 17.5 | 2 250 | 225.0 | 0.077 7 |
四氟醚唑Tetraconazole | 60.0 | 2.15 | 132 | 13.2 | 0.163 0 |
吡唑萘菌胺Isopyrazam | 100.8 | 3.86 | 2 000 | 200.0 | 0.019 3 |
乙烯菌核利Vinclozolin | 750.0 | 28.7 | 5 629 | 562.9 | 0.051 0 |
表4 所选杀菌剂对鸟类的初级急性风险评估结果
Table 4 Primary acute risk assessment results of the fungicides to birds
杀菌剂 Fungicides | AR/ (g·hm-2) | PEDacute/ (mg·kg-1·d-1) | 毒性终点 End point/(mg·kg-1·d-1) | PNED/ (mg·kg-1·d-1) | RQ |
---|---|---|---|---|---|
三唑酮Triadimefon | 300.0 | 10.0 | 2 000 | 200.0 | 0.050 2 |
乙霉威Diethofencarb | 562.5 | 17.5 | 2 250 | 225.0 | 0.077 7 |
四氟醚唑Tetraconazole | 60.0 | 2.15 | 132 | 13.2 | 0.163 0 |
吡唑萘菌胺Isopyrazam | 100.8 | 3.86 | 2 000 | 200.0 | 0.019 3 |
乙烯菌核利Vinclozolin | 750.0 | 28.7 | 5 629 | 562.9 | 0.051 0 |
杀菌剂 Fungicides | AR/ (g·hm-2) | PEDshort-term/ (mg·kg-1·d-1) | 毒性终点 End point/(mg·kg-1·d-1) | PNED/ (mg·kg-1·d-1) | RQ |
---|---|---|---|---|---|
三唑酮Triadimefon | 300.0 | 5.24 | 839.2 | 83.90 | 0.062 5 |
乙霉威Diethofencarb | 562.5 | 9.21 | 1 719.0 | 172.00 | 0.053 6 |
四氟醚唑Tetraconazole | 60.0 | 1.18 | 55.5 | 5.55 | 0.212 0 |
吡唑萘菌胺Isopyrazam | 100.8 | 2.20 | 1 310.0 | 131.00 | 0.016 8 |
表5 所选杀菌剂对鸟类的初级短期风险评估结果
Table 5 Primary short-term risk assessment results of the fungicides to birds
杀菌剂 Fungicides | AR/ (g·hm-2) | PEDshort-term/ (mg·kg-1·d-1) | 毒性终点 End point/(mg·kg-1·d-1) | PNED/ (mg·kg-1·d-1) | RQ |
---|---|---|---|---|---|
三唑酮Triadimefon | 300.0 | 5.24 | 839.2 | 83.90 | 0.062 5 |
乙霉威Diethofencarb | 562.5 | 9.21 | 1 719.0 | 172.00 | 0.053 6 |
四氟醚唑Tetraconazole | 60.0 | 1.18 | 55.5 | 5.55 | 0.212 0 |
吡唑萘菌胺Isopyrazam | 100.8 | 2.20 | 1 310.0 | 131.00 | 0.016 8 |
杀菌剂 Fungicides | PEDlong-term/ (mg·kg-1·d-1) | 毒性终点 End point/(mg·kg-1·d-1) | PNED/ (mg·kg-1·d-1) | RQ |
---|---|---|---|---|
三唑酮Triadimefon | 2.780 | 2.0 | 0.400 | 6.95 |
乙霉威Diethofencarb | 4.880 | 78.7 | 15.700 | 0.31 |
四氟醚唑Tetraconazole | 0.625 | 1.6 | 0.320 | 1.95 |
吡唑萘菌胺Isopyrazam | 1.170 | 32.5 | 6.500 | 0.18 |
表6 所选杀菌剂对鸟类的初级长期风险评估结果
Table 6 Primary long-term risk assessment results of the fungicides to birds
杀菌剂 Fungicides | PEDlong-term/ (mg·kg-1·d-1) | 毒性终点 End point/(mg·kg-1·d-1) | PNED/ (mg·kg-1·d-1) | RQ |
---|---|---|---|---|
三唑酮Triadimefon | 2.780 | 2.0 | 0.400 | 6.95 |
乙霉威Diethofencarb | 4.880 | 78.7 | 15.700 | 0.31 |
四氟醚唑Tetraconazole | 0.625 | 1.6 | 0.320 | 1.95 |
吡唑萘菌胺Isopyrazam | 1.170 | 32.5 | 6.500 | 0.18 |
杀菌剂 Fungicides | AR/(g· hm-2) | 急性毒性LD50/ (μg·蜂-1) Acute toxicity LD50/ (μg·bee-1) | RQsp |
---|---|---|---|
三唑酮Triadimefon | 300.0 | 25.0 | 0.240 |
乙霉威Diethofencarb | 562.5 | 100.0 | 0.113 |
四氟醚唑Tetraconazole | 60.0 | 63.0 | 0.019 |
吡唑萘菌胺Isopyrazam | 100.8 | 95.5 | 0.211 |
乙烯菌核利Vinclozolin | 750.0 | 100.0 | 0.150 |
表7 所选杀菌剂对蜜蜂的初级风险评估结果
Table 7 Primary risk assessment results of the fungicides to honeybees
杀菌剂 Fungicides | AR/(g· hm-2) | 急性毒性LD50/ (μg·蜂-1) Acute toxicity LD50/ (μg·bee-1) | RQsp |
---|---|---|---|
三唑酮Triadimefon | 300.0 | 25.0 | 0.240 |
乙霉威Diethofencarb | 562.5 | 100.0 | 0.113 |
四氟醚唑Tetraconazole | 60.0 | 63.0 | 0.019 |
吡唑萘菌胺Isopyrazam | 100.8 | 95.5 | 0.211 |
乙烯菌核利Vinclozolin | 750.0 | 100.0 | 0.150 |
杀菌剂 Fungicides | 种类 Classification | AR/(g·hm-2) | PERin/(g·hm-2) | LR50/(g·hm-2) | HQin |
---|---|---|---|---|---|
乙霉威Diethofencarb | 寄生性Parasites | 562.5 | 844 | 1 500 | 0.563 |
捕食性Predator | 562.5 | 844 | 7.2 | 117 | |
四氟醚唑Tetraconazole | 寄生性Parasites | 60 | 105 | 125 | 0.840 |
捕食性Predator | 60 | 105 | 250 | 0.420 | |
吡唑萘菌胺Isopyrazam | 寄生性Parasites | 100.8 | 201 | 41.2 | 4.88 |
捕食性Predator | 100.8 | 201 | 174.75 | 1.15 |
表8 所选杀菌剂在农田内暴露场景下对非靶标节肢动物的初级风险评估结果
Table 8 Primary risk assessment results of the fungicides to non-target arthropods in the in-field scenarios
杀菌剂 Fungicides | 种类 Classification | AR/(g·hm-2) | PERin/(g·hm-2) | LR50/(g·hm-2) | HQin |
---|---|---|---|---|---|
乙霉威Diethofencarb | 寄生性Parasites | 562.5 | 844 | 1 500 | 0.563 |
捕食性Predator | 562.5 | 844 | 7.2 | 117 | |
四氟醚唑Tetraconazole | 寄生性Parasites | 60 | 105 | 125 | 0.840 |
捕食性Predator | 60 | 105 | 250 | 0.420 | |
吡唑萘菌胺Isopyrazam | 寄生性Parasites | 100.8 | 201 | 41.2 | 4.88 |
捕食性Predator | 100.8 | 201 | 174.75 | 1.15 |
杀菌剂 Fungicides | 种类 Classification | AR/(g·hm-2) | PERoff/(g·hm-2) | LR50/(g·hm-2) | HQoff |
---|---|---|---|---|---|
乙霉威Diethofencarb | 寄生性Parasites | 562.5 | 12.2 | 1 500 | 0.040 7 |
捕食性Predator | 562.5 | 12.2 | 7.2 | 8.470 0 | |
四氟醚唑Tetraconazole | 寄生性Parasites | 60 | 1.45 | 125 | 0.058 0 |
捕食性Predator | 60 | 1.45 | 250 | 0.029 0 | |
吡唑萘菌胺Isopyrazam | 寄生性Parasites | 100.8 | 2.77 | 41.2 | 0.337 0 |
捕食性Predator | 100.8 | 2.77 | 174.75 | 0.079 4 |
表9 所选杀菌剂在农田外暴露场景下对非靶标节肢动物的初级风险评估结果
Table 9 Primary risk assessment results of the fungicides to non-target arthropods in the off-field scenarios
杀菌剂 Fungicides | 种类 Classification | AR/(g·hm-2) | PERoff/(g·hm-2) | LR50/(g·hm-2) | HQoff |
---|---|---|---|---|---|
乙霉威Diethofencarb | 寄生性Parasites | 562.5 | 12.2 | 1 500 | 0.040 7 |
捕食性Predator | 562.5 | 12.2 | 7.2 | 8.470 0 | |
四氟醚唑Tetraconazole | 寄生性Parasites | 60 | 1.45 | 125 | 0.058 0 |
捕食性Predator | 60 | 1.45 | 250 | 0.029 0 | |
吡唑萘菌胺Isopyrazam | 寄生性Parasites | 100.8 | 2.77 | 41.2 | 0.337 0 |
捕食性Predator | 100.8 | 2.77 | 174.75 | 0.079 4 |
杀菌剂 Fungicides | 种类 Classification | PECmax/ (mg·kg-1) | 毒性终点 End point/(mg·kg-1) | PNEC/ (mg·kg-1) | RQ |
---|---|---|---|---|---|
三唑酮Triadimefon | 蚯蚓Earthworms | 0.731 9 | 50 | 5.00 | 0.146 00 |
乙霉威Diethofencarb | 蚯蚓Earthworms | 0.922 7 | 500 | 50.0 | 0.018 50 |
土壤微生物Soil micro-organisms | 0.922 7 | 7 | 7.00 | 0.132 00 | |
四氟醚唑Tetraconazole | 蚯蚓Earthworms | 0.221 3 | 71 | 7.10 | 0.031 20 |
土壤微生物Soil micro-organisms | 0.221 3 | 0.502 | 0.502 | 0.441 00 | |
吡唑萘菌胺Isopyrazam | 蚯蚓Earthworms | 0.381 0 | 500 | 50.0 | 0.007 62 |
土壤微生物Soil micro-organisms | 0.381 0 | 1.67 | 1.67 | 0.228 00 | |
乙烯菌核利Vinclozolin | 蚯蚓Earthworms | 2.674 0 | 1000 | 100 | 0.026 70 |
表10 所选杀菌剂对土壤生物的初级风险评估结果
Table 10 Primary risk assessment results of the fungicides to soil organisms
杀菌剂 Fungicides | 种类 Classification | PECmax/ (mg·kg-1) | 毒性终点 End point/(mg·kg-1) | PNEC/ (mg·kg-1) | RQ |
---|---|---|---|---|---|
三唑酮Triadimefon | 蚯蚓Earthworms | 0.731 9 | 50 | 5.00 | 0.146 00 |
乙霉威Diethofencarb | 蚯蚓Earthworms | 0.922 7 | 500 | 50.0 | 0.018 50 |
土壤微生物Soil micro-organisms | 0.922 7 | 7 | 7.00 | 0.132 00 | |
四氟醚唑Tetraconazole | 蚯蚓Earthworms | 0.221 3 | 71 | 7.10 | 0.031 20 |
土壤微生物Soil micro-organisms | 0.221 3 | 0.502 | 0.502 | 0.441 00 | |
吡唑萘菌胺Isopyrazam | 蚯蚓Earthworms | 0.381 0 | 500 | 50.0 | 0.007 62 |
土壤微生物Soil micro-organisms | 0.381 0 | 1.67 | 1.67 | 0.228 00 | |
乙烯菌核利Vinclozolin | 蚯蚓Earthworms | 2.674 0 | 1000 | 100 | 0.026 70 |
[1] | 王忠跃. 中国葡萄病虫害与综合防控技术[M]. 北京: 中国农业出版社, 2009. |
[2] | 黄云霄, 李敏, 潘学军, 等. 几种杀菌剂对葡萄霜霉病的防治效果[J]. 农药, 2018, 57(11): 836-839. |
HUANG Y X, LI M, PAN X J, et al. Control effect of several fungicides on grape downy mildew[J]. Agrochemicals, 2018, 57(11): 836-839. (in Chinese with English abstract) | |
[3] | 刘河疆, 康露, 华震宇, 等. 新疆鲜食葡萄产区农药残留风险评估[J]. 江西农业大学学报, 2018, 40(4): 714-724. |
LIU H J, KANG L, HUA Z Y, et al. Risk assessment of pesticide residues in Xinjiang table grape producing areas[J]. Acta Agriculturae Universitatis Jiangxiensis, 2018, 40(4): 714-724. (in Chinese with English abstract) | |
[4] | 孙红艳, 贾琦, 于世锋, 等. 西安市葡萄和芹菜农药残留风险点分析[J]. 现代农业科技, 2019(3): 95-96, 100. |
SUN H Y, JIA Q, YU S F, et al. Analysis of pesticide residue risk points in grape and celery in Xi’an[J]. Modern Agricultural Science and Technology, 2019(3): 95-96, 100. (in Chinese) | |
[5] | 单守明. 葡萄优质高效栽培[M]. 北京: 机械工业出版社, 2016. |
[6] | 王忠跃. 葡萄病虫草害防治技术问答[M]. 北京: 金盾出版社, 2012. |
[7] | 白明第, 陆晓英, 吴代东, 等. 云南“阳光玫瑰”葡萄关键栽培技术及发展建议[J]. 中国南方果树, 2019, 48(5): 116-121. |
BAI M D, LU X Y, WU D D, et al. Key cultivation techniques and development suggestions of Yunnan “Sunshine Rose” grape[J]. South China Fruits, 2019, 48(5): 116-121. (in Chinese) | |
[8] | 昌云军, 管雪强. 葡萄[M]. 北京: 中国农业大学出版社, 2005. |
[9] | 马小河, 王敏, 周旭凌, 等. 葡萄主要病虫害规范化防控技术[J]. 山西果树, 2016(2): 56-58. |
MA X H, WANG M, ZHOU X L, et al. Standardized prevention and control technology of major diseases and pests of grape[J]. Shanxi Fruits, 2016(2): 56-58. (in Chinese) | |
[10] | 夏宏义, 吴伟, 曾祥国, 等. 6种杀菌剂对草莓白粉病的田间防效[J]. 浙江农业科学, 2020, 61(7): 1402-1403. |
XIA H Y, WU W, ZENG X G, et al. Field control effect of six fungicides against strawberry powdery mildew[J]. Journal of Zhejiang Agricultural Sciences, 2020, 61(7): 1402-1403. (in Chinese) | |
[11] | 凤舞剑, 杨俊杰, 陶佩琳, 等. 几种杀菌剂对高架草莓白粉病的药效试验[J]. 现代化农业, 2020(8): 5-7. |
FENG W J, YANG J J, TAO P L, et al. Effect of several fungicides on powdery mildew of elevated strawberry[J]. Modernizing Agriculture, 2020(8): 5-7. (in Chinese) | |
[12] | 申瑞平, 宋莹莹, 王秋红, 等. 两种新型琥珀酸脱氢酶抑制剂的抑菌活性比较[J]. 农药科学与管理, 2014, 35(8): 52-57. |
SHEN R P, SONG Y Y, WANG Q H, et al. Compare of fungistasis of two new succinate dehydrogenase inhibitor[J]. Pesticide Science and Administration, 2014, 35(8): 52-57. (in Chinese with English abstract) | |
[13] | 单正军, 陈祖义. 农药对陆生环境生物的污染影响及污染控制技术[J]. 农药科学与管理, 2007, 28(11): 18-26. |
SHAN Z J, CHEN Z Y. Pollution effects of pesticides on terrestrial environmental organisms and pollution control techniques[J]. Pesticide Science and Administration, 2007, 28(11): 18-26. (in Chinese) | |
[14] | 吴志凤, 周艳明, 周欣欣. 农药登记环境风险评估的现状及展望[J]. 农药科学与管理, 2015, 36(1): 12-15. |
WU Z F, ZHOU Y M, ZHOU X X. Present situation and prospect of environment risk assessment(ERA) for pesticide registration[J]. Pesticide Science and Administration, 2015, 36(1): 12-15. (in Chinese with English abstract) | |
[15] | 顾宝根, 程燕, 周军英, 等. 美国农药生态风险评价技术[J]. 农药学学报, 2009, 11(3): 283-290. |
GU B G, CHENG Y, ZHOU J Y, et al. Review on USA pesticide ecological risk assessment techniques[J]. Chinese Journal of Pesticide Science, 2009, 11(3): 283-290. (in Chinese with English abstract) | |
[16] | 于彩虹, 李春燕, 林荣华, 等. 农药对陆生生物的生态毒性及风险评估[J]. 生态毒理学报, 2015, 10(6): 21-28. |
YU C H, LI C Y, LIN R H, et al. Eco-toxicity and risk assessment of pesticide on terrestrial organisms[J]. Asian Journal of Ecotoxicology, 2015, 10(6): 21-28. (in Chinese with English abstract) | |
[17] |
WALTER H, TOBLER H, GRIBKOV D, et al. Sedaxane, isopyrazam and solatenolTM: novel broad-spectrum fungicides inhibiting succinate dehydrogenase (SDH)-synthesis challenges and biological aspects[J]. Chimia, 2015, 69(7): 425-434.
DOI URL |
[18] | U S E P A. Reregistration eligibility decision (RED) for triadimefon and tolerance reassessment (TRED) for triadimenol[R]. Washington DC: United States Environmental Protection Agency, 2006. |
[19] | University of Hertfordshire. The PPDB Pesticide Properties Database-triadimefon[EB/OL]. [2020-11-24]. http://sitem.herts.ac.uk/aeru/iupac/Reports/648.htm. |
[20] | AUTHORITY E F S. Conclusion on the peer review of the pesticide risk assessment of the active substance isopyrazam[J]. EFSA Journal, 2012, 10(3): 2600. 1-110. |
[21] | AUTHORITY E F S. Conclusion on the peer review of the pesticide risk assessment of the active substance diethofencarb[J]. EFSA Journal, 2010, 8(9): 1721. 1-55. |
[22] | European Food Safety Authority. Conclusion regarding the peer review of the pesticide risk assessment of the active substance tetraconazole[J]. EFSA Journal, 2008, 6(10): RN-152, 1-86. |
[23] | University of Hertfordshire. The PPDB Pesticide Properties Database-vinclozolin[EB/OL]. [2020-11-24]. http://sitem.herts.ac.uk/aeru/iupac/Reports/680.htm. |
[24] | University of Hertfordshire. The PPDB Pesticide Properties Database-tetraconazole[EB/OL]. [2020-11-24]. http://sitem.herts.ac.uk/aeru/iupac/Reports/626.htm. |
[25] | MEIER U. Growth stage of mono- and dicotyledonous plants:BBCH monograph[M]. 2nd ed. Berlin: Federal Biological Research Centre for Agriculture and Forestry, 2001. |
[26] | 于洋, 郑永权, 张楠, 等. 蔬菜常用农药在地下水中残留风险评估[J]. 生态毒理学报, 2017, 12(4): 183-192. |
YU Y, ZHENG Y Q, ZHANG N, et al. Groundwater risk assessment of pesticides commonly used on vegetables[J]. Asian Journal of Ecotoxicology, 2017, 12(4): 183-192. (in Chinese with English abstract) |
[1] | 郑美瑜, 王璐, 刘哲, 张文娟, 高浦, 陆胜民. 桑黄中抑制α-葡萄糖苷酶活性成分提取及其化学成分鉴定[J]. 浙江农业学报, 2022, 34(5): 949-958. |
[2] | 倪敏舒, 陈丽, 鲍熹, 徐悦, 庄腾寒, 冯磊. 内质网分子伴侣GRP94对伪狂犬病毒增殖的调节作用[J]. 浙江农业学报, 2022, 34(11): 2386-2394. |
[3] | 商佳胤, 张新建, 李凯, 张鹤, 王丹. 不同覆盖材料对设施葡萄根系分布及土壤理化特性的影响[J]. 浙江农业学报, 2022, 34(10): 2240-2250. |
[4] | 汤佳宁, 王永侠, 刘金松, 曾新福, 杨彩梅. 中链脂肪酸及其酯对致病菌的抑菌作用[J]. 浙江农业学报, 2021, 33(9): 1611-1616. |
[5] | 孙彩霞, 欧阳志周, 刘玉红, 于国光. 西兰花中3种杀菌剂的残留动态与风险评估[J]. 浙江农业学报, 2021, 33(7): 1292-1299. |
[6] | 田玉潭, 马露, 刘军, 李冬冬, 陶迎梅, 赵晓璐, 马亚男, 孙少忆, 刘敦华. 葡萄酒渣多酚-壳聚糖-CMC可食性复合膜在水煮羊肉贮藏中的应用[J]. 浙江农业学报, 2021, 33(6): 1095-1103. |
[7] | 吴剑, 王剑功, 褚伟雄. 纳他霉素处理对电商物流过程中葡萄品质的影响[J]. 浙江农业学报, 2021, 33(5): 916-922. |
[8] | 王国荣, 冯晓晓, 吴慧明, 曹婷婷, 李倩, 郑永利. 芹菜茎基腐病病原菌鉴定、消长动态调查与防治药剂筛选[J]. 浙江农业学报, 2021, 33(4): 661-669. |
[9] | 杨颖, 施迎春, 邢建荣, 刘哲, 郑美瑜, 陆胜民. 葡萄柚精油“除萜赋香”工艺的优化研究[J]. 浙江农业学报, 2021, 33(11): 2128-2136. |
[10] | 宋雯, 王强, 张佳, 柳采秀, 张楠, 陈丽萍, 聂东兴, 姚海利, 苍涛. 不同施肥方式下氯吡脲对藤稔葡萄生长和品质的影响[J]. 浙江农业学报, 2021, 33(10): 1879-1888. |
[11] | 练华山, 李欣欣, 林立金, 廖明安. 表油菜素内酯对夏黑葡萄幼苗生长的影响[J]. 浙江农业学报, 2021, 33(10): 1889-1896. |
[12] | 崔鹏飞, 魏灵珠, 程建徽, 向江, 李明山, 吴江, . 不同砧木对天工翠玉葡萄生长和果实品质的影响[J]. 浙江农业学报, 2021, 33(1): 52-61. |
[13] | 徐雪芬, 倪春辉, 李惠霞, 李焕宇, 李文豪, 陈垣, 胡芳弟. 党参根腐病病原菌鉴定及其室内毒力测定[J]. 浙江农业学报, 2021, 33(1): 96-103. |
[14] | 葛金涛, 王江英, 赵文静, 邵小斌, 朱朋波, 汤雪燕, 孙明伟, 刘兴满. 魏可葡萄气生根发育的转录组分析[J]. 浙江农业学报, 2020, 32(9): 1645-1655. |
[15] | 孟司奇, 丁高蓝, 肖兴宁, 肖英平, 杨华, 汪雯. 巴氏杀菌乳中金黄色葡萄球菌的生长预测模型构建[J]. 浙江农业学报, 2020, 32(7): 1281-1288. |
阅读次数 | ||||||||||||||||||||||||||||||||||||||||||||||||||
全文 606
|
|
|||||||||||||||||||||||||||||||||||||||||||||||||
摘要 299
|
|
|||||||||||||||||||||||||||||||||||||||||||||||||