›› 2020, Vol. 32 ›› Issue (9): 1672-1682.DOI: 10.3969/j.issn.1004-1524.2020.09.16

• Environmental Science • Previous Articles     Next Articles

Growth and arsenic enrichment characteristics of Typha angustifolia L. under different arsenic pollution levels

CHEN Tian1, BAO Ningying1, DU Chongxuan1, LIU Yungen1,2,*   

  1. 1. College of Ecology and Environment, Southwest Forestry University, Kunming 650224, China;
    2. Water Science and Engineering Center, Southwest Forestry University, Kunming 650224, China
  • Received:2020-02-04 Online:2020-09-25 Published:2020-10-10

Abstract: To investigate the growth status of typical wetland emergent plant Typha angustifolia L. and its characteristics of arsenic (As) accumulation and migration, As0, As50, As150 and As600 (corresponding to 0, 50, 150 and 600 mg·kg-1 As of sediment) were set up to study the growth and development, As accumulation characteristics of T. angustifolia L. during the life cycle (growth period, maturity period and yellow wilting period) and the effect of As extraction from soil. The result showed that T. angustifolia L. could complete its life cycle and formed seed stigma under four levels of As stress. In the growth stage, the root tolerance index (IT) of T. angustifolia L. under As50 treatment was the highest, reached to 132.38%, and the biomass of T. angustifolia L. under As150 treatment was 19.12 g, 34.08% higher than that under As0 treatment, the biomass accumulation under As600 treatment was 12.35 g, which was 13.39% less than that under As0 treatment, at this time, typha IT was the smallest, which was 65.23%; In the mature stage, the biomass accumulation of typha under As50 treatment was the highest, reaching 72.23 g, 28.70% higher than that under As0 treatment, at this time, IT of typha was the highest, reached to 149.25%; The biomass accumulation and IT under As600 treatment were the lowest. In the yellow wilting stage, the biomass accumulation and IT of typha under As50 treatment were the highest, reached to 79.23 g and 119.28%, respectively; The biomass accumulation under As600 treatment was the lowest, 13.47% lower than that under As0 treatment. In the three stages, GSH activity of typha was the highest when As content was 0-50 mg·kg-1 in the sediment, and Fv/Fm in As50 and As150were higher than that in As0; Fv/Fm in A600 was the lowest, and SOD activity and MDA content were the highest in the leaves; The bioaccumulation coefficient (BCF) of As in the underground part of typha was higher than that in the aboveground part, the transfer coefficient (TF) between plants was 0.09-1.10. The As fixed rate (ER) in the sediment of typha was higher than the removal rate (RR), and there was a significant positive correlation between the amount of extraction (EA), the amount of migration per unit area (MPUA) and the amount of As in the sediment. Typha culd endure high concentration As stress and grow normally, and had good remediation effect on the sediment of As polluted wetland. It could be planted as a wetland plant establishment species in As polluted wetland, and could increase the number of harvest and replacement of typha before the yellow wilting stage to obtain better remediation effect.

Key words: wetland, As pollution, emergent plant, growth, enrichment characteristic

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