Phytostabilization of metals in mine soils using Brassica juncea in combination with organic amendments

Background and aims The high metal bioavailability and the poor conditions of mine soils yield a low plant biomass, limiting the application of phytoremediation techniques. A greenhouse experiment was performed to evaluate the effects of organic amendments on metal stabilization and the potential of Brassica juncea L. for phytostabilization in mine soils. Methods Plants were grown in pots filled with soils collected from two mine sites located in Central Spain mixed with 0, 30 and 60 tha?1 of pine bark compost and horse- and sheep-manure compost. Plant biomass and metal concentrations in roots and shoots were measured. Metal bioavailability was assessed using a rhizosphere-based method (rhizo), which consists of a mixture of low-molecular-weight organic acids to simulate root exudates. Results Manure reduced metal concentrations in shoots (10?50 % reduction of Cu and 40?80 % of Zn in comparison with non-amended soils), bioconcentration factor (10?50 % of Cu and 40?80 % of Zn) and metal bioavailability in soil (40?50 % of Cu and 10?30 % of Zn) due to the high pH and the contribution of organic matter. Manure improved soil fertility and was also able to increase plant biomass (5?20 times in shoots and 3?30 times in roots), which resulted in a greater amount of metals removed from soil and accumulated in roots (increase of 2?7 times of Cu and Zn). Plants grown in pine bark treatments and in non-amended soils showed a limited biomass and high metal concentrations in shoots. Conclusions The addition of manure could be effective for the stabilization of metals and for enhancing the phytostabilization ability of B. juncea in mine soils. In this study, this species resulted to be a potential candidate for phytostabilization in combination with manure, differing from previous results, in which B. juncea had been recognized as a phytoextraction plant

Highway increases concentrations of toxic metals in giant panda habitat

The Qinling panda subspecies (Ailuropoda melanoleuca qinlingensis) is highly endangered with fewer than 350 individuals inhabiting the Qinling Mountains. Previous studies have indicated that giant pandas are exposed to heavy metals, and a possible source is vehicle emission. The concentrations of Cu, Zn, Mn, Pb, Cr, Ni, Cd, Hg, and As in soil samples collected from sites along a major highway bisecting the panda's habitat were analyzed to investigate whether the highway was an important source of metal contamination. There were 11 sites along a 30-km stretch of the 108th National Highway, and at each site, soil samples were taken at four distances from the highway (0, 50, 100, and 300 m) and at three soil depths (0, 5, 10 cm). Concentrations of all metals except As exceeded background levels, and concentrations of Cu, Zn, Mn, Pb, and Cd decreased significantly with increasing distance from the highway. Geo-accumulation index indicated that topsoil next to the highway was moderately contaminated with Pb and Zn, whereas topsoil up to 300 m away from the highway was extremely contaminated with Cd. The potential ecological risk index demonstrated that this area was in a high degree of ecological hazards, which were also due to serious Cd contamination. And, the hazard quotient indicated that Cd, Pb, and Mn especially Cd could pose the health risk to giant pandas. Multivariate analyses demonstrated that the highway was the main source of Cd, Pb, and Zn and also put some influence on Mn. The study has confirmed that traffic does contaminate roadside soils and poses a potential threat to the health of pandas. This should not be ignored when the conservation and management of pandas is considered

Plant-induced changes in the bioavailability of heavy metals in soil and biosolids assessed by DGT measurements

Purpose: This study investigated the effects of plants on the available pools of heavy metals and their re-supply potential in contaminated substrates in a short-term experiment using five metal-accumulating willow and poplar species/cultivars and in a longer-term experiment for Salix x reichardtii. Material and methods: Five species of willow and poplar were grown in either soil or biosolids for short-term experiment (4 months). Further investigations of longer-term effects of plant on metal availability were conducted with S. x reichardtii grown in biosolids in a column (100 cm height and 37.5 cm diameter) experiment over a period of 12 months. Samples collected before and after experiments were determined for pH and bioavailability of metals using diffusive gradients in thin films (DGT). Various pools of metals in biosolids were determined by sequential extraction. Concentrations of heavy metals in plant material were determined. Results and discussion: The concentration of metals determined by DGT (C) and concentration of metals in pore water (C) of Ni, Cu, Zn, and Cd in soil and biosolids generally decreased significantly compared to the initial measurements and were usually lower than those of the controls. However, C and C were higher in planted soil compared to those in the controls. There was a negative correlation between Ni, Zn, and Cd in plant shoots and C in both soil and biosolids. The R values, the ratio of C/C calculated for Ni, Cd and Zn of planted substrates, were significantly higher than the corresponding R values of initial substrates. By contrast, R values for Cu showed little change. R values for Ni, Zn, and Cd were higher in planted biosolids compared to the unplanted biosolids. While S. x reichardtii leaf Cd, Ni, and Zn concentrations increased significantly over time, leaf Cu concentration declined. The patterns of plant uptake for the metals reflected the patterns observed by DGT and soil solution measurements of R. Sequential extraction of heavy metals from biosolids after 12 month's experimentation confirmed that Cu was predominantly in the organic fraction. Conclusions: The short-term effects of plants on the bioavailability of metals in soils and biosolids were different. The R values of cultivated treatments varied between species but were not significantly different from the control in most of the cases. The longer-term experiment indicated that both C and C of Ni, Zn, and Cd decreased significantly over time in both planted and unplanted treatments. The results of this study demonstrated that R values measured by DGT may be useful in assessing the potential bioavailability of heavy metals in soil and biosolids