Journal
SCIENCE OF THE TOTAL ENVIRONMENT
Volume 845, Issue -, Pages -Publisher
ELSEVIER
DOI: 10.1016/j.scitotenv.2022.157057
Keywords
Heavy metal exposure; Ecotoxicity; Photosynthesis and growth; Organ and subcellular accumulation; Autioxidant enzyme activities; Transcriptomics; Bioindicator; Phytoremediation; Seagrass
Categories
Funding
- National Key Research and Development Program of China [2019YFD0901301]
- National Natural Science Foundation of China [32000269/41606192]
- Natural Science Foundation of Shandong Province [ZR2020QD106]
- National Science & Technology Basic Work Program [2015FY110600]
- Key Research Project of Frontier Sciences of CAS [QYZDB-SSW-DQC041-1]
- Taishan Scholars Program (Distinguished Taishan Scholars)
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This study examined the toxic effects of copper and cadmium on eelgrass at multiple levels. The results showed that copper was more toxic to eelgrass than cadmium. High temperatures increased heavy metal damage, while low temperatures inhibited damage. Copper and cadmium had a synergistic effect on photosynthesis. Transcriptome analysis revealed severe damage to the photosynthetic system under cadmium stress, while copper stress resulted in up-regulation of genes related to glutathione metabolism. Recovery experiments showed that the damage caused by short-term copper and cadmium stress was reversible. These findings provide insights into the heavy metal toxic effects and resistance strategies of eelgrass, highlighting its potential for phytoremediation, especially for cadmium.
Seagrass beds are recognized as critical and among the most vulnerable habitats on the planet; seagrass colonize the coastal waters where heavy metal pollution is a serious problem. In this study, the toxic effects of copper and cadmium in the eelgrass Zostera marina L. were observed at the individual, subcellular, physiologically biochemical, and molec-ular levels. Both Cu and Cd stress significantly inhibited the growth and the maximal quantum yield of photosystem II (Fv/Fm); and high temperature increased the degree of heavy metal damage, while low temperatures inhibited damage. The half-effect concentration (EC50) of eelgrass was 28.9 mu M for Cu and 2246.8 mu M for Cd, indicating Cu was much more toxic to eelgrass than Cd. The effect of Cu and Cd on photosynthesis was synergistic. After 14 days of enrichment, the concentration of Cu in leaves and roots of Z. marina was 48 and 37 times higher than that in leaf sheath, and 14 and 11 times higher than that in rhizome; and the order of Cd concentration in the organs was root > leaf > rhizome > sheath. Heavy metal uptake mainly occurred in the organelles, and Cd enrichment also occurred to a certain extent in the cytoplasm. Transcriptome results showed that a number of photosynthesis-related KEGG enrichment pathways and GO terms were significantly down-regulated under Cd stress, suggesting that the photosynthetic system of eelgrass was severely damaged at the transcriptome level, which was consistent with the significant inhibition of Fv/Fm and leaf yellowing. Under Cu stress, the genes related to glutathione metabolic path-way were significantly up-regulated, together with the increased autioxidant enzyme activity of GSH-PX. In addition, the results of recovery experiment indicated that the damage caused by short-term Cd and Cu stress under EC50 was reversible. These results provide heavy metal toxic effects at multiple levels and information relating to the heavy metal resistance strategies evolved by Z. marina to absorb and isolate heavy metals, and highlight the phytoremediation potential of this species especially for Cd.
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