2016
DOI: 10.1016/j.ecoleng.2015.10.031
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Improvement of water quality by sediment capping and re-vegetation with Vallisneria natans L.: A short-term investigation using an in situ enclosure experiment in Lake Erhai, China

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Cited by 35 publications
(9 citation statements)
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“…We also found that WT was negatively correlated with Planktothrix and Microcystis, indicating that their excessive growth may lower WT and inhibit the growth of other bacterioplankton. M. spicatum and C. demersum improved WT to some extent; however, since submerged plants need a certain time to grow, their effect on WT was not significant, implying that single submerged macrophytes only slowly improve water quality slightly [36]. It has been shown that Rhodobacter and Novosphingobium were negatively correlated with TN and TP, which is because Rhodobacter is an aerobic denitrifier that can degrade TN in water [37], while Novosphingobium can degrade TP in water and possesses an algicidal effect [38].…”
Section: Relationships Between Environmental Factors and Bacterioplan...mentioning
confidence: 91%
“…We also found that WT was negatively correlated with Planktothrix and Microcystis, indicating that their excessive growth may lower WT and inhibit the growth of other bacterioplankton. M. spicatum and C. demersum improved WT to some extent; however, since submerged plants need a certain time to grow, their effect on WT was not significant, implying that single submerged macrophytes only slowly improve water quality slightly [36]. It has been shown that Rhodobacter and Novosphingobium were negatively correlated with TN and TP, which is because Rhodobacter is an aerobic denitrifier that can degrade TN in water [37], while Novosphingobium can degrade TP in water and possesses an algicidal effect [38].…”
Section: Relationships Between Environmental Factors and Bacterioplan...mentioning
confidence: 91%
“…The enclosures were placed 25 m off the north shore at a water depth of 1.5 m and the experimental period was June 11-July 23, 2013. The tops and bottoms of the enclosures were open to maintain light intensity and free exchange of nutrients [ 32 ]. The lower end of the enclosure frames were fixed with rocks and buried to a depth of 20 cm in the sediment and the frame tops extended 30 cm above the water surface.…”
Section: Methodsmentioning
confidence: 99%
“…The lower end of the enclosure frames were fixed with rocks and buried to a depth of 20 cm in the sediment and the frame tops extended 30 cm above the water surface. Prior to treatment, the PVC sheeting was pulled down near, but not touching, the sediment for 5 days [ 32 ] to allow the water quality and plankton community to stabilize. After stabilization, the PVC was fastened to the steel tube frame, creating an enclosure volume of ~13.5 m 3 .…”
Section: Methodsmentioning
confidence: 99%
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“…However, dredging effects varying by season and high cost, and increasing the risk of spreading contaminants made it more strictly apply this method [9,10]. On the contrary, there are many in-situ approaches employed in sediment treatment such as sediment capping [3,11], phytoremediation [12,13], and chemical reagents [14,15]. Among these, sediment capping is an effective and low-cost way that places adsorption materials over sediment.…”
mentioning
confidence: 99%