Effect of lead (Pb) on antioxidation system and accumulation ability of Moso bamboo (Phyllostachys pubescens)
Introduction
The quality of soil environment reported by Chinese government revealed more than 16.1% contaminated soils in China which include 1.5% lead contaminated soils (Chen et al., 2016). Major sources of lead (Pb) in soils are mining activities, industrial emissions and pesticide application. Pb in soil has not only affected yield and quality of crops but it has also affected human health through food chain and mental development of children (Harguinteguy et al., 2015, Mazumdar and Das, 2015, Sosa et al., 2016). Pb pollution in soils has become one of the major environmental problems of the world (Liu et al., 2015, Mani et al., 2015b).
Pb is not an essential element for plants, it will harm plants due to high concentration level. Pb will destroy cell structure, metabolism and chlorosis of leaves (Elkhatib et al., 2014, Hu et al., 2012). Excessive Pb induces accumulation of reactive oxygen species (ROS) and increase the level of lipid peroxidation (Gupta et al., 2013, Tauqeer et al., 2015). However, under heavy metal exposure, antioxidant enzyme system, including superoxide dismutase (SOD), peroxidase (POD) and catalase (CAT), will effectively eliminate the plant excessive reactive oxygen free radicals to alleviate toxicity of heavy metal (Pb) in plants (Chen et al., 2015b, Gill and Tuteja, 2010).
Phytoremediation is a kind of green environmental, and economic remediation technology (Ahmadpour et al., 2012, Tangahu et al., 2011). The remediation species are mostly grown around the area of heavy metals pollution, and characteristics of these plants are mainly accumulation of heavy metals with high tolerant ability (Kamran et al., 2014, Salazar and Pignata, 2014). Several plants can grow in heavy metal contaminated soils because they use avoidance strategy, limiting heavy metal uptake by plant, e.g. by chelating metal ions in rhizosphere or binding in mycorrhizal fungi (Meier et al., 2012, Rajkumar et al., 2012). Growth of Moso bamboo (Phyllostachys pubescens (Pradelle) Mazel ex J.Houz.) was observed in old Pb/Zn mine area including surrounding Sedum alfredii H, Violaye doensis M, Juncus eflasus L etc. (Zhang et al., 2006), which has additional advantages such as quick growth, and its biomass production could reach 82 t hm−2 of dry weight compared to other plants (Chen, 1998, Song et al., 2013).
The purpose of this study was to evaluate relationship between activity of antioxidant enzymes and Pb toxicity on growth and chlorophyll concentrations of Moso bamboo. The transmission electron microscopy-energy dispersive X-ray detector (TEM-EDX) technology was employed to study organs of Moso bamboo cell accumulating Pb which will provide theoretical basis for further studies on mechanism of Pb toxicity in plants.
Section snippets
Hydroponics experiment
Plants were grown under glasshouse environment with natural light, day/night temperature of 25/30 °C, and day/night humidity of 70/90%. Seeds of Phyllostachys pubescens collected from Guilin of Guangxi Province, China were sown in special nutritional substrates containing perlite and vermiculite (3:1 v/v), moistened with distilled water. The nutrients solution was applied until seedlings had two leaves pairs. The composition of nutrients solution was as follows (mg L−1) (Chen et al., 2015a): 57.1
Effects of Pb on antioxidation system of leaves and Pb concentration of plants in hydroponics
The Pb was mostly concentrated in roots of Moso bamboo grown in hydroponics experiment (Fig. 1). The Pb concentration in Moso bamboo was in sequence of roots >leaves>stems with application of 20–100 μM Pb. Application of 400 μM Pb revealed Pb concentration sequence of roots >stems >leaves. Pb concentration in roots, stems and leaves has reached 1409 mg kg−1, 238 mg kg−1 and 179 mg kg−1 with application of 400 μM Pb compared with control.
The concentrations of TBARS and activities of SOD in leaves of Moso
Discussions
The reactive oxygen species were produced due to oxidative stress caused by variety of harmful effects in plant cells including lipid peroxidation when exposed to Pb (Mihailovic et al., 2014). TBARS concentrations was produced in plant tissues under stress caused by oxidative stress lipid over oxidation of the final product, and level of concentrations reflects plant victimization (Hu et al., 2015). The change of TBARS concentrations is often used to show how an organism can resist pressure (
Conclusions
All considered parameters suggested that Moso bamboo can tolerate stress of 1600 mg kg−1 of Pb. Moso bamboo has relatively strong absorption capacity for Pb. Our results showed improved POD activity with increased application of Pb. However, TBARS concentrations and SOD activity decreased with the increase of Pb. TEM-EDX analysis revealed, Pb accumulation mainly in cytoplasm and cell wall for reduced toxicity. Our results provided helpful reference for phytoremediation of Pb contaminated soils by
Acknowledgement
The study was financially supported through a grant from the Natural Science Foundation of China (31670617) and key research and development project of Science Technology Department of Zhejiang Province (2015C03G 4010004).
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These authors contributed equally to this work.