School of Life Sciences, Anhui Normal University, Wuhu 241000, China.
Int J Environ Res Public Health. 2022 Oct 17;19(20):13415. doi: 10.3390/ijerph192013415.
Heavy metal pollution and water eutrophication are still the main issues to be solved in the environmental field. To find a biological control method for Cd-contaminated water or combined eutrophication and Cd pollution water, the effects of salicylic acid on heavy metal Cd resistance in eukaryotic algae and and its mechanisms were studied. The results showed that the inhibition rates of 3.0 mg/L Cd stress group at 96 h were 67.0% on and 61.4% on and their uptake of Cd was 0.31 mg/g and 0.35 mg/g, respectively. When adding the different concentrations of salicylic acid while stressed by 3.0 mg/L Cd, the hormesis phenomenon of low dose stimulation and high dose inhibition could be seen, and the inhibition rates of 30 mg/L~90 mg/L salicylic acid addition groups were significantly lower than those of the Cd stress group alone, which were statistically significant ( < 0.05) and the absorption of Cd was dramatically improved. Except for the 120 mg/L salicylic acid addition group, the chlorophyll fluorescence parameters (Fv/Fm and YII), glutathione peroxidase (GSH-Px) and glutathione-S-transferase (GST) activities of all the other concentration groups were significantly higher than those of the Cd stress group alone, < 0.05.; the algal cell morphology in low concentration groups (30 mg/L and 60 mg/L) was also less damaged than those in the Cd stress group alone. These indicate that the low concentrations of salicylic acid can counteract or protect the algal cells from Cd attack, the mechanisms, on the one hand, might be related to the chelation of heavy metals by salicylic acid, resulting in the decrease of the toxicity of Cd; on the other hand, low concentrations of salicylic acid can stimulate the growth of these two algae, improve their photosynthetic efficiency and antioxidant capacity, as well as maintain the relative integrity of algal morphological structure.
重金属污染和水体富营养化仍然是环境领域需要解决的主要问题。为了寻找一种针对 Cd 污染水或富营养化与 Cd 复合污染水的生物修复方法,研究了水杨酸对真核藻类对重金属 Cd 抗性的影响及其作用机制。结果表明,在 3.0mg/L Cd 胁迫 96h 时,3.0mg/L Cd 胁迫组对 和 的抑制率分别为 67.0%和 61.4%,其 Cd 吸收量分别为 0.31mg/g 和 0.35mg/g。当在 3.0mg/L Cd 胁迫下添加不同浓度的水杨酸时,表现出低剂量刺激和高剂量抑制的兴奋效应,30mg/L~90mg/L 水杨酸添加组的抑制率显著低于单独 Cd 胁迫组,差异有统计学意义( < 0.05),且 Cd 吸收量显著提高。除 120mg/L 水杨酸添加组外,其余各浓度组的叶绿素荧光参数(Fv/Fm 和 YII)、谷胱甘肽过氧化物酶(GSH-Px)和谷胱甘肽-S-转移酶(GST)活性均显著高于单独 Cd 胁迫组,差异有统计学意义( < 0.05);低浓度组(30mg/L 和 60mg/L)的藻细胞形态也比单独 Cd 胁迫组受损程度小。这表明低浓度水杨酸可以减轻 Cd 对藻细胞的攻击,其作用机制一方面可能与水杨酸对重金属的螯合作用有关,从而降低 Cd 的毒性;另一方面,低浓度水杨酸可以刺激两种藻类的生长,提高其光合效率和抗氧化能力,同时维持藻形态结构的相对完整性。