Hyperaccumulator

Summary

A hyperaccumulator is a plant capable of growing in soil or water with very high concentrations of metals, absorbing these metals through their roots, and concentrating extremely high levels of metals in their tissues. The metals are concentrated at levels that are toxic to closely related species not adapted to growing on the metalliferous soils. Compared to non-hyperaccumulating species, hyperaccumulator roots extract the metal from the soil at a higher rate, transfer it more quickly to their shoots, and store large amounts in leaves and roots. The ability to hyperaccumulate toxic metals compared to related species has been shown to be due to differential gene expression and regulation of the same genes in both plants. Hyperaccumulating plants are of interest for their ability to extract metals from the soils of contaminated sites (phytoremediation) to return the ecosystem to a less toxic state. The plants also hold potential to be used to mine metals from soils with very high concentrations (phytomining) by growing the plants, then harvesting them for the metals in their tissues. The genetic advantage of hyperaccumulation of metals may be that the toxic levels of heavy metals in leaves deter herbivores or increase the toxicity of other anti-herbivory metabolites. Metals are predominantly accumulated in the roots causing an unbalanced shoot to root ratio of metal concentrations in most plants. However, in hyperaccumulators, the shoot to root ratio of metal concentrations are abnormally higher in the leaves and much lower in the roots. As this process occurs, metals are efficiently shuttled from the root to the shoot as an enhanced ability in order to protect the roots from metal toxicity. Delving into tolerance: Throughout the research of hyperaccumulation, there is a conundrum with tolerance. There are several different understandings of tolerance associated with accumulation; however, there are a few similarities. Evidence has conveyed that the traits of tolerance and accumulation are separate to each other and are moderated by genetic and physiological mechanisms.

Official source

https://en.wikipedia.org/wiki/Hyperaccumulator

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Related publications (4)

Soil pollution is a major environmental problem actually in China and in the world. It increases environmental risks and can affect humans through the food chain. Like solutions to clean-up the soils are generally expensive and can have side effects on environment, phytoremediation, an environmental friendly technology is a good alternative to traditional remediation. Nevertheless, some improvements must be done to increase its efficiency and make it economically viable. The goal of this work is to study two strategies respectful of the environment to improve the efficiency of phytoremediation: the co-cropping and the addition of amendments. Two Chinese species, Sedum alfredii (hyperaccumulator of cadmium) and Ricinus communis (accumulator of DDT) were co-cropped in pots with a soil contaminated by cadmium and DDT, in which different amendments (rapeseed waste, pig manure, a bio-surfactant: tea saponin, one of its by-product, and sulfur) were added to observe if they increase the efficiency of the phytoremediation. Bacteria were also used to improve DDT degradation. If the ricinus grew fast and easily, sedum biomass was very low and seems not suitable for co-cropping in these conditions. The rapeseed waste inhibit the growth of plants, suggesting that the dose was probably to high. Other amendments allowed a relatively similar growth with sensitively the best for tea saponin and microbes do not affect significantly the biomass. After determined in laboratory that tea saponin enhance the desorption of DDT and Cd in soil, an other pot experiment was started with Ricinus communis in soil amended with different concentrations of saponin to see if it also improve the phytoremediation. In the future, if the addition of amendments can enhance the phytoremediation as expected, analysis of parameters such as the quantity of nutrients or pollutants bioavailable or the structure of dissolve organic matter (DOM) might be done to see if they can explain this phenomenon. Further analysis in field conditions and with optimal concentrations of amendments are needed to determine if and in which conditions these strategies can be applicable at large scale.

2011

Although phytoextraction using hyperaccumulating plants is seen as a promising technique, a lack of understanding of the basic physiological, biochemical, and molecular mechanisms involved in heavy metal hyperaccumulation prevents the optimization of the phytoextraction technique and its further commercial application. The best-long term strategy for improving phytoextraction is therefore to understand and exploit the biological processes involved in metal acquisition, transport and shoot accumulation in plants. In order to compare Cd allocation in leaves and the role of the leaf cells in hyperaccumulating and non hyperaccumulating plants, we used a wide range of techniques and approaches on contrasting ecotypes of Thlaspi caerulescens, Arabidopsis halleri, Arabidopsis thaliana and one high biomass crop Salix viminalis. As a first step, the extent of hyperaccumulation and tolerance was studied in different plants. Five Swiss T. caerulescens populations were compared for their tolerance and Cd hyperaccumulation to two well studied populations: T. caerulescens Ganges (France) and T. caerulescens Prayon (Belgium). We showed that the behaviour of the populations in hydroponics was linked to the characteristics of their soil of origin. However, growing plants in hydroponics with 1 μM Cd seemed to be adequate to discriminate the various populations tested for hyperaccumulation. Cadmium effect on morphological parameters and Cd accumulation in S. viminalis leaves was also monitored. Salix viminalis was surprisingly tolerant to Cd and high Cd concentration in shoots. Because it may give an indication of the tolerance mechanisms employed by the different plants, we studied the general Cd allocation in leaves of hyperaccumulating (Ganges) and non-hyperaccumulating plants (Prayon, S. viminalis). Surprinsingly, when grown in hydroponics the only differences found between Prayon and Ganges at the leaf level was concentration of Cd found in the storage sinks. Results also showed similarities between T. caerulescens and S. viminalis in Cd storage, although the Cd concentrations found in leaves differed greatly. Both point-like accumulation and accumulation at the edges of the leaves were observed. A link could be established with visible symptoms (necrosis). At last differences in Cd localization between young and mature leaves were observed. These differences were attributed to physiological differences between leaves. Salix viminalis and T. caerulescens were both able to reduce Cd toxicity by allocating Cd in less sensitive tissues. Cadmium was found inside the cells and in the cell walls of the leaves of T. caerulescens, but mainly in cell walls and to a lesser extent in the symplasm in S. viminalis. Metal allocation in both plants indicated that the plant general growth strategy governed metal accumulation. We further investigated the role of the leaf cells in allocating Cd in leaves of Ganges, A. halleri and Prayon by characterizing Cd uptake in mesophyll protoplasts. Results indicated that differences in metal uptake could not be explained by different constitutive transport capacities at the leaf protoplast level. However, pre-exposure of the plants to Cd induced an increase in Cd accumulation in protoplasts of Ganges, whereas it decreased Cd accumulation in A. halleri protoplasts. The experiment with competitors eventually showed that probably more than one single transport system are carrying Cd in parallel into the cell. Metal allocation indicates that the principle of metal storage in metabolically less sensitive plant parts governs metal accumulation. Vacuolar compartmentalization and cell wall binding in leaves could therefore both play a role in accumulation of heavy metals. Based on these various results, we suggested that metal storage in plant demands the involvement of more than one compartment. Further work is however needed to assess many steps of the trafficking of metals that remain enigmatic.

EPFL2004

Impacts of heavy metal contamination and phytoremediation on a microbial community during a twelve-month microcosm experiment

Fabienne Gremion

The effects of heavy metals and phytoextraction practices on a soil microbial Community were studied during 12 months using a hyperaccumulating plant (Thlaspi caerulcseens) grown in an artificially contaminated soil. The 16S ribosomal RNA genes of the Bacteria and the beta-Proteobacteria and the amoA gene (encoding the a-subunit of ammonia monooxygenase) were PCR-amplified and analysed by denaturing gradient gel electrophoresis (DGGE). Principal component analysis (PCA) of the DGGE data revealed that: (i) the heavy metals had the most drastic effects on the bacterial groups targeted, (ii) the plant induced changes which could be observed in the amoA and in the Bacteria 16S rRNA gene patterns, (iii) the changes observed during 12 months in the DGGE-patterns of the planted contaminated soil did not indicate recovery of the initial bacterial community present in the non-contaminated soil. The potential function of the microbial community was assessed recording community level physiological profiles (CLPP) and analysing them by PCA. The lower capability of the bacterial community to degrade the substrates provided in the BIOLOG plates, in particular the amino acids, amides and amines, as well as a delay in the average well colour development (AWCD) differentiated the bacterial community of the contaminated samples from that of the non-contaminated ones. However, the plant had a positive effect on substrate utilization as shown by the greater number of substrates used in all planted samples compared to implanted ones. Finally, the measurement of the potential ammonia oxidation indicated that ammonia oxidising bacteria were completely inhibited in the contaminated soil. The stimulation of ammonia oxidation by the plant observed in the non-contaminated samples was surpassed by the inhibitory effect of the heavy metals in the contaminated soil. This study emphasises the combined use of culture-independent techniques with conventional methods to investigate the ecology of bacteria in their natural habitats. (C) 2004 Federation of European Microbiological Societies. Published by Elsevier B.V. All rights reserved.

Blackwell Publishing Ltd, Oxford2004

Impacts of heavy metal contamination and phytoremediation on a microbial community during a twelve-month microcosm experiment

Fabienne Gremion

Blackwell Publishing Ltd, Oxford2004

EPFL2004

2011