Heavy metal pollution in sediments of a typical mariculture zone in South China

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Abstract

The heavy metal inventory and the ecological risk of the estuarine sediments in Hailing Bay, an important maricultural zone along the southern coast of China, were investigated. Results show that the surface sediments were mainly polluted by As (2.17–20.34 mg/kg), Ni (1.37–42.50 mg/kg), Cu (1.21–58.84 mg/kg) and Zn (11.69–219.22 mg/kg). Furthermore, the aquafarming zone was significantly more polluted than the non-aquafarming zone, and cluster analysis suggested additional sources of heavy metal input in the aquafarming zone. As, Cr, Cu, Ni, Pb and Zn were mainly present in the non-bioavailable residual form in the surface sediments, whereas Cd was predominantly in the highly mobile acid soluble and reducible fractions. The ecological risk of the polluted sediments stemmed mainly from Cd, and from As, Cu and Pb to less degrees. The highest potential risks occurred near the aquaculture base, indicating the need to control heavy metal inputs from aquafarming activities.

Highlights

► The sediments in Hailing Bay, a key maricultural zone, were polluted by heavy metals. ► The aquafarming zone was significantly more polluted than the non-aquafarming zone. ► Most metals in the sediments, except Cd, were mostly present in the residual fraction. ► The ecological risk of the polluted sediments stemmed mainly from Cd, As, Cu and Pb. ► Aquafarming activities were one of the major sources of heavy metals in Hailing Bay.

Introduction

Sediments are effectively the sink for trace metals in marine and estuarine ecosystems, but also act as a source of metals for aquatic organisms (Chapman et al., 1998, Breslin and Sanudo-Wilhelmy, 1999, Dural et al., 2007, Qiu et al., 2011). Arsenic (As), cadmium (Cd), chromium (Cr), copper (Cu), nickel (Ni), lead (Pb) and zinc (Zn) are some of the most common heavy metal pollutants (Hakanson, 1980, Chen et al., 1991, Wong et al., 2001). These metals can enter estuaries and coastal waters through the discharge of industrial and municipal wastewaters, storm run-off, dust deposition, mine discharge, waste incineration, and other diffuse sources (Tanner et al., 2000, Dai et al., 2007, Meng et al., 2008, Zhang et al., 2008, Cheng et al., 2009, Besser et al., 2009, Cheng and Hu, 2010a, Cheng and Hu, 2010b, Hosono et al., 2010, Hosono et al., 2011). Sediment-bound heavy metals have a tendency to adsorb and accumulate on fine-grained particles that eventually move into the depositional areas (Zhang et al., 2001, Morillo et al., 2002, Jain, 2004, Man et al., 2004, Qiu et al., 2005, Singh et al., 2005, Mendiguchía et al., 2006). Sediment pollution by heavy metals has been regarded as a critical problem in marine environment because of their toxicity and bioaccumulation (Chapman et al., 1998, Islam and Tanaka, 2004, Singh et al., 2005, Todd et al., 2010). Many studies have shown that heavy metals in sediments could significantly impact the health of marine ecosystem (Snodgrass et al., 2008, Zheng et al., 2008, Besser et al., 2009). The toxicity and mobility of heavy metals in sediments vary greatly among different chemical forms (Perin et al., 1985, Cuong and Obbard, 2006, Fan et al., 2008, Yu et al., 2010). Thus, the simple measurement of heavy metal content cannot provide sufficient information about their mobility and bioavailability, and consequently the risk to the marine ecosystem. In contrast, heavy metal speciation offers a more realistic evaluation of their actual environmental impact (Perin et al., 1985, Cuong and Obbard, 2006).

Hailing Bay, located in Yangjiang city, Guangdong Province, is a major culture fishery base and a well-known tourist attraction in South China (Wen, 2011). Aquaculture and tourism industries are the main drivers of economic growth in Yangjiang, and its gross domestic product (GDP) per capita has grown by 2.3 times from 2005 to 2010. Fish farming activities in Hailing Bay have been growing fast to meet the demands for seafood from the Pearl River Delta and other regions of China over the past two decades. Trash fish and fish meals are mainly used for marine fish farming, which usually contribute to fecal mass and food residues, and raise the loading of heavy metals (Chang and Chen, 2006, Mai et al., 2006). Deteriorations of sediment quality around fish farming zones have been reported in several studies (Wong et al., 2001, Zhang et al., 2007, Meng et al., 2008, Yu et al., 2008, Qiu et al., 2011). Pollution of marine sediment in aquacultural zones and the subsequent bioaccumulation of heavy metals pose a potential risk to the public health (Dural et al., 2007, Man et al., 2010).

A comprehensive study on both the status of heavy metal pollution and the bioavailability (and mobility) of heavy metals in the sediment environment of Hailing Bay is important for the sustainable development of the regional economy and for the long-term improvement of public health. Qiu and co-workers had measured the total contents of heavy metals in the surface sediments from Hailing Bay in 2001, 2002 and 2007, and found that they were slightly polluted by Cd, Cu, Zn and Pb (Qiu and Zhu, 2004, Qiu et al., 2005, Qiu et al., 2011). This study was conducted to further investigate whether the fast growth in aquafarming in Hailing Bay had accelerated the heavy metal pollution, and to assess the potential ecological risk of the sediment pollution caused by heavy metals. Specifically, the objectives of this study were: (1) to determine the levels of heavy metals (As, Cd, Cr, Cu, Ni, Pb and Zn) in the sediments from the non-aquafarming zone and the aquafarming zone and to identify the possible sources of these metals via cluster analysis; (2) to infer the bioavailability (and the mobility) of heavy metals in the sediments by analyzing their chemical speciation using the modified BCR (Community Bureau of Reference) sequential extraction procedure; and (3) to assess the potential ecological risk of heavy metal pollution in the sediments through calculating the relevant ecological risk indices. It is noted that chemical speciation of heavy metals and assessment of their ecological risks had not been addressed in any previous studies focusing on Hailing Bay (Qiu and Zhu, 2004, Qiu et al., 2005, Qiu et al., 2011).

Section snippets

Materials and methods

Hailing Bay, one of the largest and most important estuaries along the southern coast of China, is a subtropical drowned valley bay covering an area of ∼880 km2, with an average tidal range (irregular semidiurnal tide) of 1.4–1.6 m (Qiu et al., 2006). Sediment sampling was carried out in January 2010. The sampling locations are shown in Fig. 1. Stations 1–17 were surface sediment sampling sites, where undisturbed top ∼5 cm sediments were sampled by a box grab sampler and placed in acid-rinsed

Heavy metals in surface sediments

Table 1 shows that the ranges of Al, Fe, Cd, Ni, Cu, Zn, As, Pb and Cr levels measured in this study were comparable to those reported in earlier studies (Qiu and Zhu, 2004, Qiu et al., 2005, Qiu et al., 2011). Furthermore, the ranges of these metal contents were relatively low compared to the sediments in other polluted estuaries in China, such as Jiaozhou Bay (Dai et al., 2007), Jinzhou Bay (Fan et al., 2008) and Quanzhou Bay (Yu et al., 2010). Qiu et al. (2011) reported one sample with Pb

Conclusion and recommendation

The aquafarming zone showed more significant sediment heavy metal pollution than the non-aquafarming zone in Hailing Bay, suggesting that aquafarming activities were partially responsible for the heavy metal pollution. The contents of several metals (As, Cu and Zn) in the surface sediments exceeded the Chinese standards for marine sediment, although most metals (As, Cr, Cu, Ni, Pb and Zn) were mainly present in the less bioavailable residual form except for Cd. The levels of Cd in the surface

Acknowledgement

The authors are grateful to the anonymous reviewers for helpful comments. This work was supported in parts by the Natural Science Foundation of China (Grant No. 41121063 and 41073079), the SRF for ROCS, SEM, and the “One Hundred Talents” program of the Chinese Academy of Sciences. This is contribution No. IS-1438 from GIGCAS.

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