Physiological and molecular responses to heavy metal stresses suggest different detoxification mechanism of Populus deltoides and P. x canadensis
Introduction
Poplars (Populus spp.) are increasingly used as experimental plant material for the research of tree physiology and genetics because of their ease of cloning, transformation, and relatively small genome size. Moreover, the genome sequence of P. trichocarpa is known (Tuskan et al., 2006), which facilitates the use of molecular methods. Beyond the scientific importance, poplar species are highly valued by the forestry, timber and paper industries for their rapid growth, high biomass and good fiber quality. As the demand for renewable energy rises, poplars are frequently grown as bioenergy plants. In addition to their importance in timber and bioenergy production, there is increasing interest in using poplar species for phytoremediation (Marmiroli et al., 2011). Phytoremediation, however, requires considerable tolerance to contaminated soil, which frequently contains heavy metals. Understanding the cellular and molecular responses to heavy metals in poplars is therefore essential to develop new varieties and hybrids better suited for phytoremediation.
Several metals from the transition group (e.g. iron, cobalt, nickel, copper and zinc) are essential micronutrients for plants, functioning as cofactors of a number of enzymes and proteins. However, their excess in the soil and groundwater can cause growth inhibition and toxicity symptoms. Copper (Cu) is a structural element in certain metalloproteins such as Cu/Zn-superoxide dismutase, cytochrome c, ascorbate and polyphenol oxidases, which are involved in electron transport, oxidative stress response and cell wall metabolism. As a redox-active heavy metal, copper can catalyze the formation of hydroxyl radicals (OḢ) from superoxide radical (O2.−) and hydrogen peroxide (H2O2) in the Haber-Weiss reaction (Yruela, 2009), resulting in oxidative stress, lipid peroxidation, and further degradation of macromolecules (Valko et al., 2005). Zinc plays an important role in all living organisms as cofactor of hundreds of enzymes represented in all enzyme classes, zinc finger proteins, WRKY family transcription factors and 40 S ribosomal protein S27 (McCall et al., 2000, Broadley et al., 2007). In excess, zinc can inhibit plant growth and seed germination (Mrozek and Funicelli, 1982, Wang et al., 2009), change root development (Lingua et al., 2008), cause loss of membrane integrity (Stoyanova and Doncheva, 2002) or lead to cell death (Chang et al., 2005). The lack of zinc can lead to micronutrient deficiency in various crops, while excess zinc in soil is a common environmental problem in agro-ecosystems. Both excess copper and zinc can induce the formation of reactive oxygen species (ROS) and free radicals, which leads to an imbalance between antioxidant defense and accumulation of ROS (Moran et al., 1994).
In order to prevent the deleterious effects of heavy metals, plants can reduce their uptake, increase efflux pumping, chelate them in the cytosol or compartmentalize them in the vacuole (Hall, 2002). The two major groups of intracellular chelators involved in metal detoxification of plants are the phytochelatins and the metallothioneins. Phytochelatins are glutathione oligomers, their biosynthesis interacts closely with the glutathione pool, and their synthesis show heavy metal inducibility (Cobbett, 2000, Wójcik and Tukiendorf, 2004). Metallothioneins are small, cysteine-rich proteins, ubiquitous in eukaryotes and presumably widely distributed in prokaryotes as well. In Populus species six metallothioneins were identified and characterized by Kohler et al. (2004).
Plants have developed versatile detoxification systems to counter the toxicity of the wide variety of natural and synthetic chemicals present in the environment. These processes can also eliminate the damaged molecules originating from enhanced oxidative stress. One important detoxification mechanism is chemical modification by covalent binding to glutathione. The reaction is catalyzed by glutathione transferases (GST), a divergent group of enzymes, which are ubiquitous in all living organisms. The plant-specific tau and phi subfamilies are the most common ones in plants, but numerous smaller subfamilies are known (Dixon et al., 2002b, Dixon and Edwards, 2010). In Populus trichocarpa, 81 GST genes have been identified (Lan et al., 2009). While some of these genes have subsequently been characterized (Gaudet et al., 2011, Choi et al., 2013), the functions of most members of the family are still unknown. After the GST catalyzed conjugation steps, the resulting glutathione conjugates are exported from the cytosol to the vacuole by ATP-dependent tonoplast transporters (ABC transporters). While plant ABC transporters have been described in numerous species (for review see Kang et al., 2011), few experimental data are available on the role of ABC transporters in the adaptation to heavy metals (Ariani et al., 2015).
The aim of our study was to investigate the copper and zinc stress responses of three bred poplar lines, to identify such transcripts of genes involved in the detoxification mechanisms, which could play an important role in protection against xenobiotic by-products of these metals. Furthermore, we aimed to monitor the changes of a wide variety of physiological and biochemical parameters of the poplar clones under one week of heavy metal stresses, in order to provide some indication of the suitability for phytoremediation of metal contaminated sites.
Section snippets
Plant material and treatments
Three poplar clones were used in these studies: Populus deltoides clones B-229 and PE 19/66, and P. x canadensis clone M-1. Woody cuttings were rooted for four weeks in tenth strength Hoagland nutrient solution (composition of undiluted nutrient solution: 5 mM Ca(NO3)2, 5 mM KNO3, 2 mM MgSO4, 1 mM KH2PO4, 10 μM Fe-EDTA, 10 μM H3BO3, 1 μM MnSO4, 0.5 μM CuSO4, 0.5 μM ZnSO4, 0.1 μM (NH4)6Mo7O24, 0.1 μM CoCl2, pH 5.8), following two weeks in half-strength solution. Plants were grown in a growth chamber with a
Accumulation of copper and zinc in the tested poplar clones
To reveal possible differences in heavy metal uptake, the copper and zinc accumulation in the treated poplar plants was monitored. Statistical analysis revealed a significant interaction of the genotype and treatment on the metal accumulation of poplar leaves and roots. A similar concentration-dependent copper accumulation was observed in all organs of the P. deltoides clones B-229 and PE 19/66, while 15% and 60% higher copper content was detected in leaves and roots of P. x canadensis clone
Discussion
Poplar is extensively used as bioenergy plant, to produce wood for different industrial purposes as well as for phytoremediation. Use of poplar for phytoremediation purposes can have several advantages: Populus species have very high transpiration and water uptake rates compared to other woody plants, they are among the fastest growing trees and can clean up pollution in water and soil including various organic pollutants and heavy metals (Marmiroli et al., 2011). Short rotation coppicing is a
Conflict of interest
Zsuzsanna Kolbert is member of the Journal’s Editorial Board.
Funding
This research was supported by Hungary-Serbia IPA Cross-border Co-operation Programmes (HUSRB/1002/214/036 and HUSRB/1203/221/173), and by the Hungarian National Research, Development and Innovation Office (grant number: OTKA K 105956).
Acknowledgement
Authors would like to express their thanks to Saša Orlović and Zoran Galić, from the Institute of Lowland Forestry and Environment, Novi Sad, Serbia, for providing poplar cuttings as a kindly gift.
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