a School of Forestry , Northeast Forestry University , Harbin , China.
Int J Phytoremediation. 2019;21(8):742-751. doi: 10.1080/15226514.2018.1556593. Epub 2019 Jan 18.
Trace metal contamination of soil is an increasing problem. Organic acid application can restore trace metal elements such as cadmium (Cd) in contaminated soil. Changbai larch ( A. Henry) is an economically important forestry species in northeast China; however, growth is inhibited by severe Cd contamination. We investigated the effects of different concentrations of exogenous succinic acid (SA) on Cd tolerance and physiological and morphological toxicity in seedlings. Seedlings were planted in pots containing Cd-contaminated or uncontaminated Haplic Cambisol. Seedlings in Cd-contaminated soil were treated daily with SA solution at 0, 0.04, 0.2, 1.0, and 2.0 mmol kg of soil for 10, 20 or 30 days. Cd treatment induced seedling damage and significantly increased the relative conductivity and malondialdehyde content of the leaves, inhibiting soluble protein and proline contents, superoxide dismutase and peroxidase activity, chlorophyl fluorescence and pigment content. Decreases in the length, surface area, volume of roots and leaves, and specific root length were also observed. Effects increased in control plants with time. SA treatment also reduced the Cd content of the fine roots and leaves and Mg, K, and Ca contents. Moreover, plant growth was significantly promoted and damage was reversed, especially at 5.0 and 10.0 mmol L SA for 30 days. SA therefore alleviated Cd-induced injury, improving tolerance to Cd stress. SA application combined with afforestation could therefore help restore Cd-contaminated soil in northeast China. Further studies aimed at determining the detoxification mechanism of seedlings are now required.
土壤中痕量金属的污染是一个日益严重的问题。施用有机酸可以使受污染土壤中的痕量金属元素(如镉(Cd))得到恢复。长白落叶松(A. Henry)是中国东北地区一种重要的经济林树种,但由于严重的 Cd 污染,其生长受到抑制。我们研究了不同浓度的外源琥珀酸(SA)对 Cd 耐性以及幼苗生理和形态毒性的影响。将幼苗种植在含有 Cd 污染或无污染的单粒片麻土的盆中。Cd 污染土壤中的幼苗每天用 SA 溶液处理,浓度分别为 0、0.04、0.2、1.0 和 2.0 mmol kg 的土壤,处理 10、20 或 30 天。Cd 处理诱导幼苗损伤,显著增加叶片的相对电导率和丙二醛含量,抑制可溶性蛋白和脯氨酸含量、超氧化物歧化酶和过氧化物酶活性、叶绿素荧光和色素含量。还观察到根和叶的长度、表面积、体积和比根长的减少。对照植物的这些效应随时间增加。SA 处理还降低了细根和叶片以及 Mg、K 和 Ca 的含量。此外,植物生长明显得到促进,损伤得到逆转,尤其是在 5.0 和 10.0 mmol L 的 SA 处理 30 天的情况下。因此,SA 缓解了 Cd 诱导的损伤,提高了 Cd 胁迫耐性。因此,SA 的应用结合造林可以帮助恢复中国东北地区的 Cd 污染土壤。现在需要进一步研究确定幼苗的解毒机制。