Exploring the Potential of Crotalaria juncea L. for Phytoremediation: Insights from Gas Exchange, Pigment Quantification, and Growth Measurements under Copper Stress

Beatriz Silvério dos Santos, Gabriel Wanderley Mendonça, T. C. Ferreira, N. C. P. Bomfim, Isabella Fiorini de Carvalho, Jailson Vieira Aguilar, L. S. Camargos
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Abstract

Soil contamination by trace elements is a worldwide concern that can result from several sources, such as mining, smelting, car traffic exhaust, agriculture plant protection products such as fungicides, and fertilizers. Among the metals involved, copper can cause alterations in the photosynthetic, respiratory, and enzymatic processes of plants, leading to reduced growth of roots and shoots. An alternative to dealing with metals present in the soil is phytoremediation, which consists of using plants to extract or stabilize these elements. The leguminous Crotalaria juncea is widely used as a green manure and may be advantageous due to its capacity for biological nitrogen fixation and biomass accumulation. This research aimed to evaluate the growth and physiological behaviour of C. juncea in copper-contaminated soil and its potential use as a phytoremediation plant. For the fresh and dry mass of shoots and roots, compared with 30 mg.dm−3 of Cu, there was a decrease in values with the increase in concentrations up to a dose of 480 mg.dm−3. The roots were less sensitive to increased Cu concentrations than the shoots. The tolerance index decreased as copper concentrations in the soil increased. From 60 mg.dm−3, its vegetative growth decreased, but C. Juncea was able to tolerate and accumulate copper in the root system, presenting high potential as a phytostabilizing species.
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探索 Crotalaria juncea L. 植物修复的潜力:铜胁迫下气体交换、色素定量和生长测量的启示
微量元素对土壤的污染是一个全球关注的问题,污染源有多种,如采矿、冶炼、汽车尾气、农业植物保护产品(如杀真菌剂和化肥)等。在这些金属中,铜会改变植物的光合作用、呼吸作用和酶解过程,导致根和芽的生长减弱。处理土壤中的金属的另一种方法是植物修复,即利用植物提取或稳定这些元素。豆科植物 Crotalaria juncea 被广泛用作绿肥,由于其生物固氮和生物量积累的能力,可能具有优势。本研究旨在评估君子兰在铜污染土壤中的生长和生理特性,以及其作为植物修复植物的潜在用途。与 30 毫克/立方米-3 的铜相比,芽和根的新鲜质量和干质量的数值随着浓度的增加而降低,最高剂量为 480 毫克/立方米-3。根对铜浓度增加的敏感性低于芽。耐受指数随着土壤中铜浓度的增加而降低。从 60 毫克/立方米-3 起,君子兰的无性生长就开始下降,但它能够耐受铜并在根系中积累铜,具有很高的植物稳定潜力。
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