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