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本文引用的文献

1
Interspecific variation in resistance and tolerance to herbicide drift reveals potential consequences for plant community co-flowering interactions and structure at the agro-eco interface.种间对除草剂漂移的抗性和耐受性的变化揭示了在农业生态界面,植物群落共同开花相互作用和结构的潜在后果。
Ann Bot. 2022 Dec 31;130(7):1015-1028. doi: 10.1093/aob/mcac137.
2
Damage and recovery from drift of synthetic-auxin herbicide dicamba depends on concentration and varies among floral, vegetative, and lifetime traits in rapid cycling Brassica rapa.合成生长素除草剂麦草畏的漂移造成的损伤和恢复取决于浓度,并因快速循环油菜中花、营养和终生特征的不同而有所差异。
Sci Total Environ. 2021 Dec 20;801:149732. doi: 10.1016/j.scitotenv.2021.149732. Epub 2021 Aug 18.
3
Effects of glyphosate spray-drift on plant flowering.草甘膦喷雾漂移对植物开花的影响。
Environ Pollut. 2021 Jul 1;280:116953. doi: 10.1016/j.envpol.2021.116953. Epub 2021 Mar 23.
4
The role of climate change in pollinator decline across the Northern Hemisphere is underestimated.气候变化在北半球传粉媒介减少中的作用被低估了。
Sci Total Environ. 2021 Jun 25;775:145788. doi: 10.1016/j.scitotenv.2021.145788. Epub 2021 Feb 12.
5
Effects of Low Doses of Herbicides on Different Endpoints in the Life Cycle of Nontarget Terrestrial Plants.低剂量除草剂对非靶标陆生植物生命周期中不同终点的影响。
Environ Toxicol Chem. 2021 May;40(5):1389-1404. doi: 10.1002/etc.4992. Epub 2021 Apr 9.
6
Contribution of Extensive Farming Practices to the Supply of Floral Resources for Pollinators.粗放式农业实践对传粉者花卉资源供应的贡献。
Insects. 2020 Nov 20;11(11):818. doi: 10.3390/insects11110818.
7
Scientific Opinion addressing the state of the science on risk assessment of plant protection products for in-soil organisms.关于植物保护产品对土壤生物风险评估的科学现状的科学意见。
EFSA J. 2017 Feb 22;15(2):e04690. doi: 10.2903/j.efsa.2017.4690. eCollection 2017 Feb.
8
Herbicides as anthropogenic drivers of eco-evo feedbacks in plant communities at the agro-ecological interface.除草剂作为农业生态界面植物群落中生态-进化反馈的人为驱动因素。
Mol Ecol. 2021 Nov;30(21):5406-5421. doi: 10.1111/mec.15510. Epub 2020 Jul 10.
9
Effects of Herbicides on Flowering.除草剂对开花的影响。
Environ Toxicol Chem. 2020 May;39(6):1244-1256. doi: 10.1002/etc.4712. Epub 2020 Apr 29.
10
Feasibility of assessing vegetative and generative endpoints of crop- and non- crop terrestrial plant species for non-target terrestrial plant (NTTP) regulatory testing under greenhouse conditions.评估温室条件下非目标陆生植物(NTTP)法规测试中作物和非作物陆生植物种的营养和生殖终点的可行性。
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模拟除草剂飘移改变了本地植物的开花物候。

Simulated herbicide drift alters native plant flowering phenology.

机构信息

US Environmental Protection Agency, Center for Public Health and Environmental Assessment, Pacific Ecological Systems Division, Corvallis, OR, USA.

National Asian Pacific Center on Aging, Senior Environmental Employment Program, Corvallis, OR, USA.

出版信息

Ecotoxicology. 2024 Nov;33(9):1009-1025. doi: 10.1007/s10646-024-02795-3. Epub 2024 Sep 12.

DOI:10.1007/s10646-024-02795-3
PMID:39264548
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC11559356/
Abstract

Data for herbicide effects on plant flowering are needed to determine potential impacts on plant reproduction. Thus, flowering phenology was determined for up to 12 weeks after herbicide treatment for native Willamette Valley plants growing in small plots on two Oregon State University experimental farms. Six perennial species were evaluated: Camassia leichtlinii (CALE), Elymus glaucus (ELGL), Eriophyllum lanatum (ERLA), Festuca idahoensis subsp. roemeri (FEID), Iris tenax (IRTE), and Prunella vulgaris var. lanceolata (PRVU). Effects of glyphosate and dicamba, alone and in combination, were determined using simulated drift rates of 0.1 or 0.2 x field application rates (FAR) of 1119 g ha active ingredient (a.i.) (830 g ha acid glyphosate) for glyphosate and 560 g ha a.i. for dicamba. Flowering phenology was evaluated as stage of development on a scale from no buds (converted to 0), buds (1), pre-flowering (2), flowering (3), post-flowering (4), to mature seeds (5) before herbicide treatment and for 12 weeks after treatment. Flowering response to herbicides varied by species and farm; but, in general, dicamba and glyphosate resulted in earlier flowering stages (delayed or not full flowering) for the dicot ERLA, and to a lesser extent, PRVU; and glyphosate resulted in earlier flowering stages for the monocot IRTE. Based on these data, the concentration of herbicide affecting flowering stage was 0.1 x FAR. Once flowering stage was inhibited by dicamba and glyphosate, plants generally did not recover to full flowering. This study provided evidence that common herbicides can affect flowering phenology of native plants with implications for seed production.

摘要

需要有关除草剂对植物开花影响的数据,以确定其对植物繁殖的潜在影响。因此,在俄勒冈州立大学两个实验农场的小块地中,对生长的本地威拉米特谷植物进行了长达 12 周的除草剂处理后,确定了开花物候。评估了六种多年生物种:Camassia leichtlinii(CALE),Elymus glaucus(ELGL),Eriophyllum lanatum(ERLA),Festuca idahoensis subsp. roemeri(FEID),Iris tenax(IRTE)和Prunella vulgaris var. lanceolata(PRVU)。使用模拟漂移率为 0.1 或 0.2 x 田间施用量(FAR)的草甘膦和二甲苯单独以及组合,确定了草甘膦的 1119 g/ha 有效成分(830 g/ha 酸草甘膦)和二甲苯的 560 g/ha 有效成分。开花物候学是根据无芽(转换为 0),芽(1),开花前(2),开花(3),开花后(4),到成熟种子(5)的发育阶段进行评估的,在施药前和施药后 12 周进行评估。除草剂对物种和农场的开花反应不同;但是,一般来说,二甲苯和草甘膦使双子叶植物 ERLA 更早进入开花阶段(开花延迟或不完全),而 PRVU 的程度较小;草甘膦使单子叶植物 IRTE 更早进入开花阶段。根据这些数据,影响开花阶段的除草剂浓度为 0.1 x FAR。一旦开花阶段被二甲苯和草甘膦抑制,植物通常不会完全恢复开花。这项研究提供了证据,表明常见的除草剂会影响本地植物的开花物候,从而影响种子的产生。