Biosystems and Environmental Engineering Research Group, Department of Soil Science and Agricultural Engineering, University of Zimbabwe, P.O. Box MP167, Mt. Pleasant, Harare, Zimbabwe.
Biosystems and Environmental Engineering Research Group, Department of Soil Science and Agricultural Engineering, University of Zimbabwe, P.O. Box MP167, Mt. Pleasant, Harare, Zimbabwe.
Ecotoxicol Environ Saf. 2019 Apr 15;170:750-762. doi: 10.1016/j.ecoenv.2018.12.047. Epub 2018 Dec 21.
Land application of coal ash is considered an environmentally friendly option to improve soil quality, but limited information exists on metal bioavailability and phytotoxicity of coal ash to sensitive plant species such as lettuce (Lactuca sativa L.). Germination and pot bioassay experiments were conducted at six coal application rates (0% (control), 5%, 15%, 25%, 50% and 75% v/v) to investigate the hypothesis that, coal ash will have a hormetic effect on germination, growth, metal uptake and biomass yield of lettuce, characterized by stimulatory and phytotoxicity effects at low and high application rates, respectively. Total concentrations (mg/kg) of metals in coal ash spanned several orders of magnitude, and decreased in the order: Fe (5150.5), Mn (326.0), Zn (102.6), Cu (94.7), Ni (74.7) and Pb (11.6). Bioavailable concentrations of metals were very low (0.0-14.1 mg/kg), accounting for less than 2% of the total concentrations. Coal ash had no significant effect on germination indices, but had hormetic effects on radicle elongation, evidenced by stimulatory and phytotoxicity effects at low (5-25%) and high (50-75%) application rates, respectively. Coal ash application at 50% and 75% significantly (p < 0.05) reduced lettuce growth and edible biomass yield, but lower application rates (5-25%) were similar to the unamended soil (control). Fe, Mn, Zn, Cu and Ni bioavailability and plant uptake generally decreased with increasing coal ash application rates particularly at 50% and 75%. Soil pH significantly increased (p < 0.05) from 6.5 for the control to about 8 for 75% coal ash, while electrical conductivity (EC) increased by 2-7 times to about 0.9 and 1.5 dS/m at 50% and 75% coal ash, respectively. Significant inverse linear relationship (p < 0.05; r = 0.80) were observed between edible and total biomass yields and EC, suggesting that increased salinity at high coal ash application rates could account for reduced growth and biomass. Partial elemental balances showed that plant uptake of metals was very low, accounting for just less than 2% of the bioavailable concentrations, while the bulk of the metals (98-99%) remained in the soil. In conclusion, the current findings show that coal ash may have hormetic and phytotoxic effects on sensitive plant species, an observation contrary to the bulk of earlier literature documenting beneficial effects of coal ash application to soils. Long-term field studies are required to confirm the current findings based on laboratory and pot bioassay experiments.
煤灰的土地应用被认为是改善土壤质量的一种环保选择,但关于煤灰对生菜(Lactuca sativa L.)等敏感植物物种的金属生物利用度和植物毒性的信息有限。在六个煤灰施用量(0%(对照)、5%、15%、25%、50%和 75%v/v)下进行了发芽和盆栽生物测定实验,以验证煤灰对生菜发芽、生长、金属吸收和生物量产量具有兴奋效应的假设,其特征是在低施用量和高施用量下分别表现出刺激和植物毒性效应。煤灰中金属的总浓度(mg/kg)跨越了几个数量级,顺序为:Fe(5150.5)、Mn(326.0)、Zn(102.6)、Cu(94.7)、Ni(74.7)和 Pb(11.6)。金属的生物可利用浓度非常低(0.0-14.1mg/kg),不到总浓度的 2%。煤灰对发芽指数没有显著影响,但对胚根伸长有兴奋作用,这表现在低(5-25%)和高(50-75%)施用量下分别表现出刺激和植物毒性效应。煤灰在 50%和 75%的应用显著(p<0.05)降低了生菜的生长和可食用生物量产量,但较低的施用量(5-25%)与未施肥土壤(对照)相似。Fe、Mn、Zn、Cu 和 Ni 的生物可利用性和植物吸收性通常随煤灰施用量的增加而降低,特别是在 50%和 75%煤灰时。煤灰施用量从对照的 6.5 显著增加(p<0.05)到 75%煤灰时约为 8,而电导率(EC)增加了 2-7 倍,分别在 50%和 75%煤灰时约为 0.9 和 1.5dS/m。在可食用和总生物量产量与 EC 之间观察到显著的负线性关系(p<0.05;r=0.80),这表明在高煤灰施用量下,盐分增加可能导致生长和生物量减少。部分元素平衡表明,植物对金属的吸收非常低,仅占生物可利用浓度的不到 2%,而大部分金属(98-99%)仍留在土壤中。总之,目前的研究结果表明,煤灰可能对敏感植物物种具有兴奋和植物毒性效应,这与大量早期文献记录煤灰对土壤有益影响的观点相反。需要进行长期田间研究来证实基于实验室和盆栽生物测定实验的当前发现。