2017
DOI: 10.1016/j.marenvres.2017.09.018
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Comparative trophic structures of macrobenthic food web in two macrotidal wetlands with and without a dike on the temperate coast of Korea as revealed by stable isotopes

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Cited by 21 publications
(10 citation statements)
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“…For herbivores/grazers, detritivores, filter feeders and omnivores, the mean TEFs are 0.4‰ AE 1.3‰ for δ 13 C and 2.2‰ AE 0.3‰ for δ 15 N (Park et al 2017, Carvalho et al 2020. For carnivores/predators, the mean TEFs are 0.96‰ AE 0.26‰ for δ 13 C and 3.3‰ AE 0.26‰ for δ 15 N (Park et al 2017, Wang et al 2021). The dietary proportions for this model were expressed as 2.5%, 25%, 50%, 75%, and 99% credible intervals.…”
Section: Statistical Analysis and Modelingmentioning
confidence: 99%
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“…For herbivores/grazers, detritivores, filter feeders and omnivores, the mean TEFs are 0.4‰ AE 1.3‰ for δ 13 C and 2.2‰ AE 0.3‰ for δ 15 N (Park et al 2017, Carvalho et al 2020. For carnivores/predators, the mean TEFs are 0.96‰ AE 0.26‰ for δ 13 C and 3.3‰ AE 0.26‰ for δ 15 N (Park et al 2017, Wang et al 2021). The dietary proportions for this model were expressed as 2.5%, 25%, 50%, 75%, and 99% credible intervals.…”
Section: Statistical Analysis and Modelingmentioning
confidence: 99%
“…The main advantage of using this framework is that it calculates the possible contribution of food sources to consumers by considering the mean and SD of stable isotopes and TEFs (Parnell et al 2010). For herbivores/grazers, detritivores, filter feeders and omnivores, the mean TEFs are 0.4‰ AE 1.3‰ for δ 13 C and 2.2‰ AE 0.3‰ for δ 15 N (Park et al 2017, Carvalho et al 2020. For carnivores/predators, the mean TEFs are 0.96‰ AE 0.26‰ for δ 13 C and 3.3‰ AE 0.26‰ for δ 15 N (Park et al 2017, Wang et al 2021).…”
Section: Statistical Analysis and Modelingmentioning
confidence: 99%
“…In the YRE, isotopic comparisons among the sites displayed no significant spatial differences in consumers and there much narrower ranges of δ 13 C values than those observed in the SRE. Despite the various feeding styles of macrobenthic consumers, such narrow δ 13 C ranges may reflect the utilization of similar dietary items (Park et al 2017). The δ 13 C values of most consumers at all of the sites were very similar to those of EPOM, which suggests a high contribution of phytoplankton-derived organic matter in their diets and very little contribution of RPOM or P. australis.…”
Section: Spatial and Seasonal Variability In Food Web Structure In The Diked And Natural Systemsmentioning
confidence: 99%
“…In addition, estuarine systems have diverse habitats resulting from the distribution zones of specific plant communities and are characterized by spatial heterogeneity of biotic and environmental factors (Bertness and Pennings 2000). The loss and fragmentation of diverse intertidal habitats caused by hydrological changes resulting from the construction of dikes or dams may lead to severe modification of carbon/energy flow and food web structure in estuarine systems (Talley 2000;Wissel and Fry 2005;Park et al 2017). In the YRE, the estuarine dikes have seriously modified coastal wetlands and greatly reduced habitats (by about 280 km 2 ) of bare intertidal flats and saltmarsh plant communities (Kim et al 2017b).…”
Section: Spatial and Seasonal Variability In Food Web Structure In The Diked And Natural Systemsmentioning
confidence: 99%
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