Abstract

The increasing discharge of wastewater containing inorganic salts, sometimes accompanied by high pH, has been a worldwide environmental problem. Constructed wetlands (CWs) are considered a viable technology for treating saline and/or alkaline wastewater provided that saline-alkaline tolerant plant species are selected and applied. The influence of both saline and alkaline stress on four wetland plant species during their seed germination, early growth, vegetative propagation and continued growth stages was evaluated by three experiments. Principal component analysis (PCA) was conducted for selecting representative indicators for evaluating the saline and alkaline tolerance of plants during vegetative propagation and plant growth stages. The saline and alkaline stress inhibited the vegetative propagation and plant growth of all tested plant species to varying degrees, therein the influences of saline-alkaline stress on plants were more marked than saline stress. The length of new roots, Na+ accumulation in plant tissue, Na+/K+ ratios in aerial tissue and the total dry biomass were selected as most representative indicators for evaluating the saline and alkaline tolerance of plants. Iris sibirica and Lythrum salicaria showed better saline and alkaline tolerance ability among tested species and could be grown in CWs for treating saline and/or alkaline wastewater.

Highlights

  • Saline and/or alkaline wastewater usually contains both inorganic salts and other contaminants and maybe accompanied by high pH

  • The germination percentages of A. tatarinowii and T. orientalis were significantly (p < 0.05) reduced at Electrical conductivity (EC) treatments from 0 to 7.5 dS m−1 and there was no germination observed at EC of 10 and 15 dS m−1 treatments (Figure 2I)

  • The increasing saline-alkaline treatments significantly (p < 0.05) inhibited the germination percentages for all tested plant species and the germination of T. orientalis was completely inhibited by all saline-alkaline treatments

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Summary

Introduction

Saline and/or alkaline wastewater usually contains both inorganic salts and other contaminants and maybe accompanied by high pH. This type of wastewater is mainly produced by agriculture production, aquaculture and various industrial sections (e.g., agro-food, petrochemical and tanning industries) [1,2,3]. The salinity level of saline and/or alkaline wastewater varies with specific sources and has a wide range. The receiving water bodies have been negatively impacted by the direct discharge of saline and /or alkaline wastewater due to the presence of both salt and other contaminants, causing the destruction of aquatic ecosystems [6]. The treatment of saline and/or alkaline wastewater has been an urgent task in the present world

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