Purpose
The present study was carried out in Roro region, Chaibasa, Jharkhand, India, to assess the impact of chromite–asbestos mine waste (CMW) on a nearby agroecosystem. The role of metal-accumulating grass–legume association in facilitating phytoremediation was investigated.Materials and methods
Soil and plant samples were collected from (i) chromite–asbestos mine waste (CMW) with Cynodon dactylon, Sorghastrum nutans, and Acacia concinna; (ii) contaminated agricultural soil-1 (CAS1) from a foothill with Cajanus cajan; (iii) contaminated agricultural soil-2 (CAS2) distantly located from the hill, cultivated with Oryza sativa and Zea mays; and (iv) unpolluted control soil (CS). Total metal concentrations were quantified in both soils and plants by digesting the samples using HNO3, HF, HClO4 (5:1:1; v/v/v), and HNO3 and HClO4 (5:1; v/v), respectively, and analyzed under flame atomic absorption spectrophotometry. Metal grouping and site grouping cluster analysis was executed to group the metals and sampling sites. Translocation factor (TF) and bioconcentration factor (BCF) were calculated to determine the phytoremediation efficiency of grasses and legumes.Results and discussion
Results indicate that total metal concentrations in the CMW were in the order of Cr?>?Ni?>?Mn?>?Cu?>?Pb?>?Co?>?Zn?>?Cd. High concentrations of Cr (1983 mg kg?1) and Ni (1293 mg kg?1) with a very strong contamination factor were found in the CAS, which exceeds the soil threshold limits. Further, metal and site grouping cluster analysis also revealed that Cr and Ni were closely linked with each other and the CMW was the main source of contamination. Among all the metals, Cr and Ni were mainly accumulated in grasses (C. dactylon and S. nutans) and legumes (A. concinna and C. cajan) as compared to cereals (Z. mays and O. sativa). The TF of Cr was >1 for grasses. Except for Zn, the BCF for all the metals were <1 in roots and shoots of all the plants and cereals.Conclusions
The present study revealed that abandoned CMW is the source of contamination for agriculture lands. Phytoremediation relies on suitable plants with metal-scavenging properties. Grass–legume cover (C. dactylon, S. nutans, A. concinna, and C. cajan) has the ability to accumulate metals and act as a potential barrier for metal transport, which facilitate the phytoremediation of the CMW. Possibilities for enhancing the barrier function of the grass–legume cover need to be explored with other low-cost agronomic amendments and the role of rhizospheric organisms.Characterization of tannery sludge (TS) for its plausible use in amelioration and phytoremediation of heavy metal rich TS treated soil by growing economically important plants (Ricinus communis, Brassica juncea and Nerium oleander).
Materials and methodsTreatments were prepared by amalgamation of TS (0, 5, 10, 20, 30, 50, 75, 100 %) with garden soil (GS). All treatments were analysed for chemical properties, total and DTPA (Diethylene triamine pentaacetic acid) extractable heavy metals (Cr, Pb, Cu, and Mn). Seed germination experiment was conducted; unvarying saplings were selected and planted in concerned pots and allowed to grow for 90 days in green house. At harvest, plant samples were washed with distilled water and used for determination of growth parameters (biomass of root, shoot and total biomass on dry weight basis) and metal accumulation in different parts of the plant. Translocation factor (TF) and bioconcentration factor (BCF) have been calculated to check the phytostabilization capability of studied plants.
Results and discussionApplication of TS in fixed quantity as an amendment resulted in significant improvements of GS characteristics (alkaline pH with high electrical conductivity, organic carbon, available NPK and heavy metals) and in treatments. DTPA extractable heavy metal concentrations were found very low and total heavy metal concentrations were also found under allowable range in control and treated soil (T-I to T-VI). The maximum seed germination percentage, plant growth, biomass production for all plant species were observed in T-III treatment (20 % TS + 80 % GS) with majority of the metal accumulation in underground part (BCF >1) and meagre translocation in aerial part (TF <1). From T-IV to T-VII treatment, accumulation of heavy metals in plant parts has generally increased; however, biomass has been tremendously decreased.
ConclusionsTS was found rich in NPK content with significant concentration of heavy metals. Pot growth experiment suggested amelioration of GS with specific quantity of 20 % TS can tremendously enhance the plant growth, help in the utilization of TS and can act as a substitute of synthetic fertilizer. Majority of the metals was accumulated in root part (BCF >1) and meagre translocation (TF <1) in aerial part, concludes R. communis and B. juncea could be suitable plant species to be grown in heavy metal rich TS treated soil, vis-à-vis for phytostabilization of heavy metals. In addition, these oil yielding and medicinal plants can also be used for phytoremediation of moderately contaminated tannery soils.
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