Abstract

Stable isotope analyses of food webs have been used in previous decades to determine trophic sources and food web structures. The use of stable isotope models to estimate consumption contributions is based on a type of multivariate beta distribution called the Dirichlet distribution. The Dirichlet distribution does not conclude the pi = 0 and pi = 1 situation. Thus, scientists have previously assumed that every potential trophic source contributes to consumption in stable isotope models. However, animals have dietary preferences and some trophic resources may not contribute to consumption. Less is known about the effects of species-specific dietary processes on stable isotope analyses, especially in regard to trophic contribution estimation. In this study, we develop methods to determine consumers’ “real potential trophic sources” and “discrimination factors” using lab-based observations and lab-based discrimination experiments. We describe a dietary process-based stable isotope mixing model (D-SIMM) that integrates lab-based dietary preference observations and the stable isotope mixing model (SIMM) to estimate trophic contributions. Then, we present the application of D-SIMM on three representative macroinvertebrate species in our study area (sea urchin: Anthocidaris crassispina (A. crassispina); gastropod: Turbo cornutus (T. cornutus); and mussel: Septifer virgatus (S. virgatus)) to re-evaluate source-consumer contributions. Thus, we compare the differences between the source contribution estimation results of SIMM and D-SIMM by calculating the standardized convex hull area (TA) of species-specific trophic sources and the consumer standard ellipses area (SEA) of the potential trophic source group. Three examples illustrate significant differences in species-specific dietary preferences between consumers, resulting in systematic difference for TA, SEA and trophic source contribution estimation results between SIMM and D-SIMM. As such, D-SIMM explains pi = 0 of certain trophic sources, which often causes uncertainty and is ignored in previous SIMM research. In addition, species-specific discrimination factors should be noticed during trophic source estimation. For estimation of the trophic contribution of source-consumers, our findings imply that the dietary preferences of consumers should be fully considered before SIMM analysis, and that D-SIMM is a more ecological process and robust measure. Additionally, we found high macroalgae (MAC) coverage in seaweed beds and a high detritus contribution of MAC to sedimentary organic matter (SOM). These findings, combined with the high contributions of MAC and SOM to consumers, suggest that MAC and its debris are the basal trophic sources for gastropods, sea urchins and mussels in seaweed bed habitats. The conservation of seaweed beds should be fully considered to ensure sustainable utilization of shellfish.

Highlights

  • Understanding the structure and function of habitats requires information on trophic interactions, energy and material flow patterns [1,2,3]

  • In MixSIAR, estimations of the contribution of posterior probability sources to macroinvertebrates were simulated by Markov chain Monte Carlo sampling (e.g., Markov Chain Monte Carlo (MCMC) sampling, chain length = 1,000,000, burn in = 50,000, thin = 500, chains = 3) and the following isotopic information was incorporated into the model: Firstly, means and standard deviations of sources based on previous stable isotope mixing model (SIMM) hypotheses and the diet selection experiment were included

  • Following the dietary observation experiment, three representative macroinvertebrates were classified into two functional groups: sea urchins and gastropods are semi-mobile jawed surface omnivores and mussels are sessile filter-feeders (Table 2)

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Summary

Introduction

Understanding the structure and function of habitats requires information on trophic interactions, energy and material flow patterns [1,2,3]. Large amounts of detritus produced by primary producers are transported by hydrodynamic forces and the sedimentation-resuspension effect, leading to a complex composition of sedimentary organic matter (SOM) and suspended particulate organic matter (SPOM) This provides more attractive trophic sources for the detritus food chain [7,8]. In view of the trophic complexity and the lack of description of material and energy flow patterns in seaweed bed habitats, it is clear that alternative and quantitative procedures are needed to estimate the relationship between trophic sources and different functional groups of consumers. )(.C()CS)oSuorucrecee eisisininsisdideeththeeccoonnvveexxppoollyyggoonn bboouunndd bbyy aallll ootthheerr ssoouurrcceess;; iiff ssoouurrccee ee ddooeess nnoott ccoonnttrriibbuuttiioonn,, iitt wwiillll yyiieelldd aa ddiiffffuussee ssoolluuttiioonn,, eessppeecciiaallllyy tthhee eessttiimmaattiioonn ooff ccoonnttrriibbuuttiioonnffrroommssoouurrcceebb..(D(D))IfIfssoouurcrceebbaannddeeddoonnoot tcocnontrtirbiubutitoino,nt,htehemmixitxutruerehahsaas acocnosntrsatrinaiendesdolsuotliuotnio. OInMthainsdstBuPdOy,MMwAeCre, SaOssMum, SePdOtoMbaenpdotBePnOtiaMl fwooedresaosusrucmeseidn ttohebestpuodtyenatrieaal.food sources in the study area

Potential Food Sources
Consumers
Species-Specific Diet Selection Observation
Estimation of Discrimination between Diets and Macroinvertebrates
Stable Isotope Analysis
Data Analysis
Dietary Observations
Stable Isotope Analysis and Source Contribution Evaluation
Discussion
Diet Estimation of Representative Macroinvertebrate Species in Seaweed Beds
Conclusions
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