2021
DOI: 10.1016/j.scitotenv.2021.148800
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Metal pollutant pathways in cohesive coastal catchments: Influence of flocculation and biopolymers on partitioning and flux

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Cited by 11 publications
(5 citation statements)
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“…Currently, a large amount of manpower and material resources is invested in dredging projects for reliable navigation conditions, heavy metal‐contaminated sediment remediation, and ecological habitat restoration (Liss et al., 2004; Shen et al., 2018). The transportation and downward flux of SPM in aquatic environments are essential to address those engineering and environmental problems, which are controlled, to a large extent, by the settling velocity of the aggregate (Izquierdo–Ayala et al., 2021; Schindler et al., 2021). Moreover, the settling velocity of widespread biomineral flocs is altered significantly due to the colonizing microorganisms, and thus leads to an obstacle for the accurate prediction of sediment and organic carbon fluxes (Bungartz et al., 2006; Larsen, Harvey, & Crimaldi, 2009, Larsen, Harvey, Noe, & Crimaldi, 2009).…”
Section: Discussionmentioning
confidence: 99%
“…Currently, a large amount of manpower and material resources is invested in dredging projects for reliable navigation conditions, heavy metal‐contaminated sediment remediation, and ecological habitat restoration (Liss et al., 2004; Shen et al., 2018). The transportation and downward flux of SPM in aquatic environments are essential to address those engineering and environmental problems, which are controlled, to a large extent, by the settling velocity of the aggregate (Izquierdo–Ayala et al., 2021; Schindler et al., 2021). Moreover, the settling velocity of widespread biomineral flocs is altered significantly due to the colonizing microorganisms, and thus leads to an obstacle for the accurate prediction of sediment and organic carbon fluxes (Bungartz et al., 2006; Larsen, Harvey, & Crimaldi, 2009, Larsen, Harvey, Noe, & Crimaldi, 2009).…”
Section: Discussionmentioning
confidence: 99%
“…The maximum was frequently found at site F6 where the boundary of tidal river reach is located, probably as a result of the flocculation effect [30,31]. The salinity of river water serves as an important controlling factor for the partitioning of heavy metals to sediments, particularly the flocculation process in the lower reaches and estuary of rivers affected the distribution of heavy metals in the river sediments [31]. The concentration at the river mouth (F7) slightly decreased compared with site F6, probably because of resuspension and transportation of contaminated sediments seaward.…”
Section: Spatial and Seasonal Variations In Heavy Metalsmentioning
confidence: 99%
“…where CF i and n are the contamination factor of each heavy metal obtained using the Equation ( 2) and the number of heavy metals studied, respectively. Based on the mCd value, the sediment heavy metal contamination level can be categorized into ultra-high degree (mCd > 32), extremely high degree (16)(17)(18)(19)(20)(21)(22)(23)(24)(25)(26)(27)(28)(29)(30)(31)(32), very high degree (8)(9)(10)(11)(12)(13)(14)(15)(16), high degree (4-8), moderate degree (2-4), low degree (1.5-2), and nil to very low degree of contamination (<1.5) [24].…”
Section: Modified Degree Of Contamination (Mcd)mentioning
confidence: 99%
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“…Large fluvial systems drain the continental surface, gathering erosion products and anthropogenic agents, and form huge deltas that result from transport of sand, but mainly silt and clay [1][2][3]. These fine cohesive sediments (mud) host pollutants and bind important portions of nitrogen (N) and phosphorus (P) and organic carbon (OC) [4][5][6][7][8][9]. Because particles smaller than 32 µm tend to form aggregates (or flocs) [10][11][12], freshwater flocculation likely dictates sediment dynamics in large lowland rivers [13][14][15][16], and thereby, the dispersed particle approach does not appropriately represent the suspended load [17].…”
Section: Introductionmentioning
confidence: 99%