Removal of aluminium by constructed wetlands with water hyacinth (Eichhornia crassipes (Mart.) Solms) grown under different nutritional conditions
dc.contributor.author | Jayaweera, MW | |
dc.contributor.author | Kasturiarachchi, JC | |
dc.contributor.author | Kularatne, RKA | |
dc.contributor.author | Wijeykoon, SLJ | |
dc.date.accessioned | 2013-10-21T02:28:31Z | |
dc.date.available | 2013-10-21T02:28:31Z | |
dc.description.abstract | This article reports the phytoremediation efficiencies of water hyacinth (Eichhornia crassipes (Mart.) Solms) grown under different nutritional conditions for Al rich wastewaters in batch type constructed wetlands (floating aquatic macrophyte-based plant treatment systems). This study was conducted for 15 weeks after 1 week acclimatization by culturing young water hyacinth (average height of 20 ± 2 cm) in 590 L capacity fiberglass tanks under different nutrient concentrations of 2-fold [56 and 15.4 mg/L of total nitrogen (TN) and total phosphorous (TP), respectively], 1-fold, 1/2-fold, 1/4-fold and 1/8-fold with synthetic wastewaters containing 5.62 Al mg/L. A control set-up of hyacinths comprising only Al with no nutrients was also studied. A mass balance was carried out to investigate the phytoremediation efficiencies and to identify the different Al removal mechanisms from the wastewaters. Chemical precipitation of Al(OH)3 was a dominant contribution to Al removal at the beginning of the study, whereas adsorption of Al3+ to sediments was observed to be a predominant Al removal mechanism as the study progressed. Phytoremediation mainly due to rhizofiltration was also an important mechanism of Al removal especially during the first 4 weeks of the study in almost all the set-ups. However, chemical precipitation and sediment adsorption of Al3+ was a dominant contribution to Al removal in comparison with phytoremediation. Plants cultured in the control set-up showed the highest phytoremediation efficiency of 63% during the period of the 4th week. A similar scenario was evident in the 1/8-fold set-up. Hence we conclude that water hyacinth grown under lower nutritional conditions are more ideal to commence a batch type constructed wetland treating Al rich wastewaters with a hydraulic retention time of approximately 4 weeks, after which a complete harvesting is recommended. | |
dc.identifier.issue | 2 | |
dc.identifier.journal | Journal of Environmental Science and Health Part A: Toxic/Hardous substance & environmental engineering | |
dc.identifier.pgnos | 185-193 | |
dc.identifier.uri | http://dl.lib.mrt.ac.lk/handle/123/8483 | |
dc.identifier.volume | 42 | |
dc.identifier.year | 2007 | |
dc.language | en | |
dc.subject | Al | |
dc.subject | phytoremediation | |
dc.subject | rhizofiltration | |
dc.subject | wastewaters | |
dc.subject | water hyacinth (Eichhornia crassipes (Mart.) Solms) | |
dc.title | Removal of aluminium by constructed wetlands with water hyacinth (Eichhornia crassipes (Mart.) Solms) grown under different nutritional conditions | |
dc.type | Article-Abstract |
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