ReviewEffect of activities associated with coastal reclamation on the macrobenthos community in coastal wetlands of the Yellow River Delta, China: A literature review and systematic assessment
Introduction
The macrobenthos is a particularly important part of the biocenosis in coastal wetlands because these organisms play a key role in transferring energy and materials within the food web (Covich et al., 2004, Dauvin et al., 2006). Due to its ecological importance, obvious presence, high sensitivity to disturbance, and direct contact with sediments, the macrobenthos of coastal ecosystems is widely used as a tool to detect the environmental impacts of pollution and other consequences of reclamation activity (Buschbaum et al., 2012, Li et al., 2016), and has therefore been used to support ecologically sustainable marine management (e.g., Borja et al., 2000, Naser, 2011, Crippa et al., 2013, Nishijima et al., 2015).
The Yellow River Delta is the largest and youngest coastal wetland in the warm temperate zone of China. However, in recent years, the demands of urbanization and economic development have led to serious impacts on the delta's wetlands due to intensive land reclamation activities, which include the construction of ports and tidal embankments, oilfield exploitation, and the development of aquaculture. Such seashore reclamation activities are typically associated with both short- and long-term impacts that affect the characteristics and patterns of the macrobenthos community (Airoldi and Beck, 2007).
The responses of the macrobenthos community to seashore reclamation have been studied in Yellow River Delta wetland by means of field surveys and a range of experimental approaches. Most of these studies have focused on the responses of the macrobenthos during a specific period or at specific sites (Wang et al., 2008, Mao et al., 2011). Some have assessed the qualitative or quantitative impacts of specific reclamation activities on the macrobenthos community, such as protection of the shoreline by establishing Spartina alterniflora communities (Shen et al., 2009) and ecologically risky activities oilfield exploitation (Chen et al., 2012). This information is useful, but is restricted to point observations at the sampling sites, and therefore cannot provide the benefits of a comparative analysis of long-term time-series data. Walker et al. (2008) used field surveys and detected increased spatial variation of species diversity and biomass after reclamation. Song and Liu (2013) reviewed the impacts of reclamation activities on the ecosystem of estuarine delta wetlands, but did not quantitatively assess the influence on the macrobenthos. Some comparative surveys have indicated that a high-intensity of coastal reclamation contributed to a pronounced decline in species diversity and biomass (e.g., Yan et al., 2015). The distinctiveness of each delta and of each part of a large delta makes it important to perform quantitative comparisons to reveal long-term changes in the macrobenthos associated with coastal reclamation in a specific delta wetland.
In this paper, we systematically assessed the impacts of reclamation activities in the Yellow River Delta based on a literature review. We identified 31 studies that considered the long-term impacts of seashore reclamation activities on the delta's macrobenthos. Our goal was to answer three main questions: (1) Have seashore reclamation activities changed the dominant taxa since 1980 (the earliest data available)? (2) Did the seashore reclamation activities decrease the biomass, abundance, and biodiversity of the macrobenthos community? (3) Which reclamation activities had the greatest impact? Based on the results of our literature review, we have also created a list of suggested criteria that future seashore reclamation researchers should use to design their research in order to increase the quantity and quality of the data available to support future meta-analyses.
Section snippets
Study area
The Yellow River Delta (37°35′N to 38°12′N, 118°33′E to 119°20′E) is located on the western coast of the Bohai Sea (Fig. 1), and is the largest and youngest coastal wetland in China. The delta is one of the most active regions of land-ocean interaction and among the largest river deltas in the world. The region has a temperate, semi-humid, continental monsoon climate. The average annual temperature is 12.1 °C, with monthly means ranging from a minimum of −1.3 °C in December to a maximum of
Literature review
We performed a systematic review of the scientific literature to identify studies of the Yellow River Delta that provided quantitative evidence of the impacts of seashore reclamation activities on the macrobenthos community. We used the ISI Web of Science database (http://wokinfo.com), which provides access to peer-reviewed studies, with no restriction on the publication date. We used the following search term combination: (Macrobenth* OR megalobenth* OR benth*) AND (Yellow River OR Huanghe)
Overall literature review
The survey and publication years covered the period from 1985 to 2013 and from 1989 to 2015, respectively, and most of the investigation of the macrobenthos community in the Yellow River Delta happened after 2000. The mean time lag between the year of the investigation and publication of the associated results was 3 years.
Eight types of human impacts, including land reclamation activities or activities associated with land reclamation, were described in the literature: aquaculture,
Discussion
Coastal reclamation activities and other human impacts alter wetland habitats and soil, thereby affecting the macrobenthos community (Baek et al., 2014). We found that the dominant species changed remarkably during the study period, from nematodes and polychaetes in the 1980s to gastropods, polychaetes, crustaceans, and insects in the 2000s and later. In the study area, tidal barriers, whose length increased from 54.3 km in the 1980s to 190.4 km in the 2010s (SBSP, 2015), contributed strongly
Conclusions
In this paper, we systematically reviewed the long-term impacts of seashore reclamation activities and other human impacts on the macrobenthos community using the coastal wetlands of the Yellow River Delta as a case study. We found that the dominant taxa have changed remarkably from the 1980s to the 2010s in response to changes in the available habitats and their quality in the study area (e.g., more polluted environments, a greater proportion of terrestrial environments). The changes in the
Acknowledgments
We thank the National Basic Research Program of China (973 Program, No. 2013CB430402), the National Science Foundation for Innovative Research Group (No. 51121003), the National Natural Science Foundation of China (No. 51279008 and 51579012), and the Fundamental Research Funds for the Central Universities (No. 2012CXQT02) for their financial support. We also thank Geoffrey Hart for providing language help during the writing of this paper.
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