Eker Selim, Ozturk Levent, Yazici Atilla, Erenoglu Bulent, Romheld Volker, Cakmak Ismail
Department of Soil Science, Faculty of Agriculture, Cukurova University, 01330 Adana, Turkey.
J Agric Food Chem. 2006 Dec 27;54(26):10019-25. doi: 10.1021/jf0625196.
Evidence clearly shows that cationic micronutrients in spray solutions reduce the herbicidal effectiveness of glyphosate for weed control due to the formation of metal-glyphosate complexes. The formation of these glyphosate-metal complexes in plant tissue may also impair micronutrient nutrition of nontarget plants when exposed to glyphosate drift or glyphosate residues in soil. In the present study, the effects of simulated glyphosate drift on plant growth and uptake, translocation, and accumulation (tissue concentration) of iron (Fe), manganese (Mn), zinc (Zn), and copper (Cu) were investigated in sunflower (Helianthus annuus L.) plants grown in nutrient solution under controlled environmental conditions. Glyphosate was sprayed on plant shoots at different rates between 1.25 and 6.0% of the recommended dosage (i.e., 0.39 and 1.89 mM glyphosate isopropylamine salt). Glyphosate applications significantly decreased root and shoot dry matter production and chlorophyll concentrations of young leaves and shoot tips. The basal parts of the youngest leaves and shoot tips were severely chlorotic. These effects became apparent within 48 h after the glyphosate spray. Glyphosate also caused substantial decreases in leaf concentration of Fe and Mn while the concentration of Zn and Cu was less affected. In short-term uptake experiments with radiolabeled Fe (59Fe), Mn (54Mn), and Zn (65Zn), root uptake of 59Fe and 54Mn was significantly reduced in 12 and 24 h after application of 6% of the recommended dosage of glyphosate, respectively. Glyphosate resulted in almost complete inhibition of root-to-shoot translocation of 59Fe within 12 h and 54Mn within 24 h after application. These results suggest that glyphosate residues or drift may result in severe impairments in Fe and Mn nutrition of nontarget plants, possibly due to the formation of poorly soluble glyphosate-metal complexes in plant tissues and/or rhizosphere interactions.
有证据清楚表明,喷雾溶液中的阳离子微量营养素会因形成金属 - 草甘膦络合物而降低草甘膦控制杂草的除草效果。当暴露于草甘膦漂移或土壤中的草甘膦残留时,植物组织中这些草甘膦 - 金属络合物的形成也可能损害非靶标植物的微量营养素营养。在本研究中,在可控环境条件下,对在营养液中生长的向日葵(Helianthus annuus L.)植株,研究了模拟草甘膦漂移对铁(Fe)、锰(Mn)、锌(Zn)和铜(Cu)的植物生长、吸收、转运和积累(组织浓度)的影响。以推荐剂量的1.25%至6.0%之间的不同速率(即0.39和1.89 mM草甘膦异丙胺盐)向植物地上部分喷洒草甘膦。草甘膦处理显著降低了根和地上部分的干物质产量以及幼叶和茎尖的叶绿素浓度。最幼嫩叶片和茎尖的基部严重褪绿。这些影响在草甘膦喷雾后48小时内变得明显。草甘膦还导致叶片中铁和锰的浓度大幅下降,而锌和铜的浓度受影响较小。在使用放射性标记的铁(59Fe)、锰(54Mn)和锌(65Zn)进行的短期吸收实验中,分别在施用6%推荐剂量的草甘膦后12小时和24小时,59Fe和54Mn的根系吸收显著降低。草甘膦导致施用后12小时内59Fe和24小时内54Mn从根到地上部分的转运几乎完全受到抑制。这些结果表明,草甘膦残留或漂移可能导致非靶标植物的铁和锰营养严重受损, 这可能是由于在植物组织和/或根际相互作用中形成了难溶性的草甘膦 - 金属络合物。