Geochemical Distribution, Enrichment, and Potential Toxicity of Trace Metals in the Surface Sediments of Okinawa Mangrove, Southwest Japan

Abstract

Surface sediments along the coast of Okinawa Island were analyzed to determine their geochemical compositions, and to assess sediment quality and the potential for ecological harm, based on comparison with established international sediment quality guidelines. The Contamination factor (CF) and the geoaccumualtion index (Igeo) of As, Pb, Zn, Cu, Ni, and Cr were computed to determine the pollution status of the mangrove and foreshore sediments. The lowest effect level (LEL) and the severe effect level (SEL) established by the New York State Department of Environmental Conservation (NYSDEC), and the threshold effect level (TEL) value and the probable effect level (PEL) developed by the Canadian Council of Ministers of the Environment (CCME) were the benchmarks applied to assess the potential for ecological harm. Among the sampling set, the highest average concentration of Pb (22 mg/kg), Zn (82 mg/kg), Ni (26 mg/kg), and Cr (81 mg/kg) occurred in the Ohura mangrove sediments, that of As (17 mg/kg) in the Gesashi mangrove, and that of Cu (22 mg/kg) in the suspended solids. The loss on ignition values of the foreshore sediments (20.32%) are nearly two and three times greater than that of the Gesashi mangrove and the Ohura mangrove, respectively. On average, the CFs of As, Pb, Zn, Cu, Ni, and Cr in the suspended solids, those of Pb, Zn, Cu, Ni, and Cr in the Gesashi mangrove and foreshore sediments, and those of Ni and Cr in the Ohura mangrove display low contamination (CF≤1), whereas the average CF of As in the three sampling areas show moderate enrichment (CF:1-3). The average Igeo values indicate that among the selected trace metals, only As in the Gesashi and Ohura mangroves show significant values, but even these are rated as unpolluted to moderately polluted (Igeo:0-1). The average concentrations of As in the Gesashi and Ohura mangroves and the foreshore sediments exceed both the LEL and TEL, but fall below the SEL and PEL, suggesting that this metal may moderately impact biota health. This is also the case for Cu and Ni in the Ohura mangrove and the suspended solids, and for Cr in the Ohura mangrove.

Quantifying the influence of urban land use on mangrove biology and ecology: A meta‐analysis

“…Furthermore, any potential influence in nutrient dynamics, as indicated by stable isotope tracers, is likely to extend to regional trophic levels owing to the high connectivity between mangroves and surrounding marine habitats (Kwon, ). Additionally, urban mangrove soils seem particularly prone to accumulating heavy metal and Polycyclic aromatic hydrocarbon (PAH) contaminants, often to toxic levels for some floral and faunal species (Diallo & Ishiga, ; MacFarlane, ; Ventura & da Cunha Lana, ). Although there is some field‐based evidence for the effect these contaminants have in driving the composition of benthic faunal assemblages, mostly laboratory experiments have shown direct impacts on mangrove floral physiology, indicating a need for more in situ experiments.…”

“…Municipal sewage has also been a frequent topic of urban mangrove studies, many of which have reported anthropogenic nitrogen enrichment in these systems, as evident in higher foliar and detrital δ 15 N isotopes (Cifuentes et al, ; Dehairs et al, ; Fry & Cormier, ; Jones, O'Donohue, Udy, & Dennison, ; Mohamed et al, ; Wolters, Gillis, Bouma, Katwijk, & Ziegler, ) and lower foliar carbon to nitrogen ratios (C:N; Mohamed et al, ; Wolters et al, ). Many studies also report high heavy metal contamination in urban mangrove sediments, attributable not only to increased metal inputs associated with urban land use, but also to the high metal affinity of the mangrove benthos (Bayen, ; Cavalcante, Sousa, Nascimento, Silveira, & Freire, ; Defew, Mair, & Guzman, ; Diallo & Ishiga, ; Harris & Santos, ; Inglis & Kross, ; Lai et al, ; Li, Xu, Chai, & Qiu, ; Oliveira, Souza‐Santos, Silva, & Macedo, ; Pagliosa & Barbosa, ; Shriadah, ; Tam & Wong, ; Wasserman, Freitas‐Pinto, & Amouroux, ). These metals are assimilated by mangroves and partitioned throughout their biomass (MacFarlane, Koller, & Blomberg, ), with some reported influences on their physiology and morphology (Liu et al, ; MacFarlane, ; MacFarlane & Burchett, ).…”

Evaluation of Present Lake Environment from Geochemistry of Bottom Sediment of Hartbeespoort Dam, North-West Province, South Africa

“…These enrichments in the central zone can be attributed to Fe-rich clay deposit in the deepest part of the impoundment. Fe -oxide is considered an excellent trapper of trace metals (Diallo & Ishiga, 2016).…”