Abstract

In a pot experiment, we assessed the potential of purslane (Portulaca oleracea) as a phytoremediation species in Cr(VI)-contaminated soils. We focused on the evaluation of phytotoxic Cr(VI) effects at concentrations reaching 150 mg Cr(VI) kg−1 and the possible stress amelioration effect of nitrogen on Cr(VI)-stressed plants. Treatments were T-0 (control), T-1 (25 mg Cr(VI) kg−1), T-2 = 50 mg kg−1, T-3 = 100 mg kg−1, and T-4 = 150 mg kg−1. We measured Cr(VI) concentration in aerial and root tissues, a series of parameters related to photosynthesis and plant growth, phosphorus aerial plant tissue content, and we also calculated indices (ratios) related to leaf growth and above ground tissue water content. Cr(VI) almost exclusively was found in root tissues; all physiological and growth parameters studied were severely affected and plants selectively accumulated phosphorus in aerial plant tissues with increasing Cr(VI) soil concentrations. On the other hand, N amendment resulted in improved plant features in some of the measured parameters: chlorophyll index was improved with added N at T-2, plant height was significantly higher at T-0, T-1, and T-2, and aerial dry weight and leaf area was higher at T-0; these effects indicate that added N did increase P. oleracea potential to ameliorate Cr(VI) toxic effects. We conclude that purslane showed a potential as a possible species to be successfully introduced to Cr(VI)-laden soils, but more research is certainly necessary.

Highlights

  • Metal ions can be introduced to surface soils by natural or anthropogenic processes and their environmental impact is greatly affected by their mineralogical and geochemical form [1]

  • In root tissue Cr(VI) concentration and nitrogen addition had no significant effect on root in root tissue Cr(VI) concentration and nitrogen addition had no significant effect on root tissue Cr(VI) content (p = 0.109)

  • Cr(VI) levels in root tissues were orders of magnitude higher compared to Cr(VI)

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Summary

Introduction

Metal ions can be introduced to surface soils by natural or anthropogenic processes and their environmental impact is greatly affected by their mineralogical and geochemical form [1]. Cr is mainly found in two valence states, namely +3 (chromite (Cr(III)) and. In natural soil conditions trivalent chromium Cr(III) is the predominant state [2]. Hexavalent Cr compounds are found in wastes of numerous industrial activities (i.e., chromic acid and Cr-pigment production, leather tanning, cement production, metal plating, and stainless-steel production), and its anionic form results in increased possibility of Cr(VI) pollution dispersal [2,3,4]. Hexavalent chromium (Cr(VI)) is of much higher toxicity (10 to 100 times) compared to Cr(III) for both acute and chronic exposure, posing serious health hazards for humans.

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