Department of Plant Physiology, University of Gdańsk, Gdynia, Poland.
J Environ Sci Health B. 2012 Sep;47(8):814-22. doi: 10.1080/03601234.2012.676443.
In this study, we evaluate the toxicity of MCPA (auxin-like growth inhibitor), chloridazon (CHD) (PSII-inhibitor) and their mixtures to floating plants and planktonic algae. Toxicity of MCPA (4-chloro-2-methylphenoxyacetic acid) and CHD (5-amino-4-chloro-2-phenyl-3(2H)-pyridazinone) was first assessed in two growth inhibition tests with Lemna minor (ISO/DIS 20079) and Desmodesmus subspicatus (ISO 8692). Next, herbicide mixtures at concentrations corresponding to the EC values were used to assess their interactive effects, and the biomarkers were: for duckweed fresh weight, frond area, chlorophyll content and number of fronds, and for algae cell count and cell volume. The 3d EC₁₀ and EC₅₀ values using cell counts of D. subspicatus were 142.7 and 529.1 mg/L for MCPA and 1.7 and 5.1 mg/L for CHD. The 7d EC₁₀ and EC₅₀ values using frond number of L. minor amounted to 0.8 and 5.4 mg/L for MCPA and 0.7 and 10.4 mg/L for CHD. Higher sensitivity of reproductive (number of cells/fronds) than growth processes (cell volume/frond area) to herbicides applied individually and in mixtures was especially pronounced in the responses of Desmodesmus. Herbicide interactions were assessed by the two-way ANOVA and Abbott's formula. Generally, an antagonistic interaction with Lemna was revealed by MCPA and chloridazon, whereas additive effect of both herbicides was observed for Desmodesmus. A significant stimulation of SOD and APX activity by binary mixtures was noted in algal cells mainly after 24 and 48 hours of exposure. The extremely high stimulation of the activity of both enzymes was induced by the combination EC₁₀CHD + EC₅₀MCPA (48 h). Presumably due to oxidative stress, the treatment with CHD at concentration EC₅₀ after 72 h was lethal for algae grown in aerated cultures, in contrast to standardized test conditions. Taking into account the consequences of risk assessment for herbicide mixtures we can state that a relatively low toxicity, as well as the lack of significant synergy between MCPA and CHD to non-target plants appears to be the most important result.
在这项研究中,我们评估了 MCPA(生长素类似生长抑制剂)、氯嘧磺隆(CHD)(PSII 抑制剂)及其混合物对漂浮植物和浮游藻类的毒性。我们首先在两项抑制生长测试中评估了 MCPA(4-氯-2-甲基苯氧基乙酸)和 CHD(5-氨基-4-氯-2-苯基-3(2H)-哒嗪酮)的毒性,使用浮萍(ISO/DIS 20079)和新月藻(ISO 8692)。接下来,使用与 EC 值相对应的除草剂混合物来评估它们的相互作用效应,生物标志物为:浮萍的鲜重、叶面积、叶绿素含量和叶数,藻类的细胞数和细胞体积。使用 D. subspicatus 的细胞计数,MCPA 的 3dEC₁₀ 和 EC₅₀ 值分别为 142.7 和 529.1mg/L,CHD 的 3dEC₁₀ 和 EC₅₀ 值分别为 1.7 和 5.1mg/L。使用 L. minor 的叶数,MCPA 的 7dEC₁₀ 和 EC₅₀ 值分别为 0.8 和 5.4mg/L,CHD 的 7dEC₁₀ 和 EC₅₀ 值分别为 0.7 和 10.4mg/L。与单独使用和混合使用除草剂相比,繁殖(细胞数/叶数)过程比生长过程(细胞体积/叶面积)对除草剂的敏感性更高,这在 Desmodesmus 的反应中尤为明显。通过双向方差分析和 Abbott 公式评估了除草剂的相互作用。一般来说,MCPA 和氯嘧磺隆与浮萍表现出拮抗作用,而这两种除草剂对 Desmodesmus 的作用则是相加的。在藻类细胞中,主要在暴露 24 和 48 小时后,二元混合物显著刺激了 SOD 和 APX 活性。在 48 小时的暴露后,组合 EC₁₀CHD + EC₅₀MCPA (48 小时)引起了这两种酶活性的极高刺激。由于氧化应激,在充气培养中生长的藻类在 72 小时后用 CHD 的 EC₅₀ 处理是致命的,与标准化测试条件形成对比。考虑到对除草剂混合物进行风险评估的后果,我们可以说,相对较低的毒性以及 MCPA 和 CHD 对非靶标植物之间没有显著的协同作用,这似乎是最重要的结果。