Department of Plant Sciences, Quaid-i-Azam University, Islamabad, 45320, Pakistan.
Department of Soil Science and Plant Nutrition, Cukurova University, 1150, Adana, Turkey.
Environ Sci Pollut Res Int. 2019 Jul;26(20):20689-20700. doi: 10.1007/s11356-019-05323-7. Epub 2019 May 18.
Cadmium (Cd) toxicity in agricultural crops is a widespread problem. Little is known about biochar and arbuscular mycorrhizal fungi (AMF) effect on Cd concentration in maize plant either applied separately or in combination. Current study was performed to demonstrate effects of biochar and Rhizophagus clarus on plant growth, photosynthesis activity, nutrients (P, Ca, Mg, Fe, Cu, and Mn), and Cd concentration in maize grown in Cd-spiked soil. The alkaline soil was spiked by Cd factor at three levels: 0 (Cd 0), 5 (Cd 5), and 10 (Cd 10) mg/kg; biochar factor at two levels: 0 and 1%; and mycorrhizal inoculum factor at two levels: MF0 and MF1 (R. clraus). Plants were harvested after 70 days of seed germination, and various morphological and physiological parameters, as well as elemental concentration and root colonization, were recorded. Addition of biochar increased plant biomass by 21% (Cd 5) and 93% (Cd 10), MF1 enhanced by 53% (Cd 0) and 69% (Cd 10), while biochar + MF1 enhanced dry plant biomass by 70% (Cd 0) and 94% (Cd 10). Results showed maximum increase of 94% (Cd 10) in plant biomass was observed in Cd-spiked soil. Root colonization decreased proportionally by increasing Cd concentration and at Cd 10, colonization was 36.7% and 31.7% for MF1 and biochar + MF1 treatments, respectively. Besides that, addition of biochar enhanced root attributes (root length, volume, and surface area) by 34-58% compared to control in Cd 10. The MF1 increased these attributes by 11-78% while biochar + MF1 enhanced by 32-61% in Cd-spiked soil. However, biochar + MF1 neutralized Cd stress in maize plant for gaseous attributes (assimilation rate, transpiration rate, intercellular CO, and stomatal conductance). The MF1 enhanced Cd concentration in plant as it was 3.32 mg/kg in Cd 5 and 6.73 mg/kg in Cd 10 treatments while addition of biochar phytostabilized Cd and reduced its concentration in plants by 2.0 mg/kg in Cd 5 and 4.27 mg/kg in Cd 10. The biochar + MF1 had 2.9 mg/kg and 4.8 mg/kg Cd concentration in Cd 5 and Cd 10 plants, respectively. Phosphorus concentration was augmented in shoots (up to 26%) and roots (up to 20%) of maize plant in biochar-amended soil than control plants. In biochar + MF1, concentration of P was 1.01% and 0.73% in Cd 5 and Cd 10, respectively. It is concluded that biochar + MF1 treatment enhances plant biomass while addition of sole biochar reduced Cd uptake, slightly indifferent to earlier treatment.
镉(Cd)在农作物中的毒性是一个普遍存在的问题。人们对生物炭和丛枝菌根真菌(AMF)对玉米植株中镉浓度的影响知之甚少,无论是单独应用还是联合应用。本研究旨在证明生物炭和亮隔孢囊霉对生长在镉污染土壤中的玉米的植物生长、光合作用活性、养分(P、Ca、Mg、Fe、Cu 和 Mn)和镉浓度的影响。碱性土壤用 Cd 因子在三个水平上进行了接种:0(Cd 0)、5(Cd 5)和 10(Cd 10)mg/kg;生物炭因子在两个水平上:0 和 1%;和菌根接种因子在两个水平上:MF0 和 MF1(R. clarus)。在种子发芽 70 天后收获植物,记录各种形态和生理参数以及元素浓度和根定植。添加生物炭使植物生物量增加 21%(Cd 5)和 93%(Cd 10),MF1 分别增加 53%(Cd 0)和 69%(Cd 10),而生物炭+MF1 使植物干生物量分别增加 70%(Cd 0)和 94%(Cd 10)。结果表明,在 Cd 污染土壤中,植物生物量最大增加了 94%(Cd 10)。根定植随着 Cd 浓度的增加而成比例减少,在 Cd 10 时,MF1 和生物炭+MF1 处理的定植率分别为 36.7%和 31.7%。此外,与对照相比,生物炭在 Cd 10 中使根属性(根长、体积和表面积)增加了 34-58%。MF1 分别将这些属性提高了 11-78%,而生物炭+MF1 在 Cd 污染土壤中提高了 32-61%。然而,生物炭+MF1 使玉米植株的气体属性(同化速率、蒸腾速率、胞间 CO2 和气孔导度)的 Cd 胁迫得到了中和。MF1 增加了植物中的 Cd 浓度,在 Cd 5 处理中为 3.32mg/kg,在 Cd 10 处理中为 6.73mg/kg,而添加生物炭则使 Cd 得到了植物固定,并使植物中的 Cd 浓度降低了 2.0mg/kg在 Cd 5 处理中,Cd 10 处理中为 4.27mg/kg。生物炭+MF1 在 Cd 5 和 Cd 10 植物中的 Cd 浓度分别为 2.9mg/kg 和 4.8mg/kg。磷在生物炭处理的玉米植株的地上部分(最高增加 26%)和地下部分(最高增加 20%)中的浓度高于对照植株。在生物炭+MF1 中,P 的浓度在 Cd 5 中为 1.01%,在 Cd 10 中为 0.73%。综上所述,生物炭+MF1 处理可提高植物生物量,而单独添加生物炭则可降低 Cd 的吸收,对早期处理的影响则相对较小。