Abstract

Understanding the ecological patterns of invasive species and their habitats require an understanding of the species’ foraging ecology. Stable carbon (δ13C) and nitrogen (δ15N) isotope values provide useful information into the study of animal ecology and evolution, since the isotope ratios of consumers reflect consumer's dietary patterns. Nevertheless, the lack of species‐ and element‐specific laboratory‐derived turnover rates could limit their application. Using a laboratory‐based dual stable isotope tracer approach (Na15 NO 3 and NaH13 CO 3), we evaluated the δ15N and δ13C isotope turnover rates in full‐grown adult invasive Limnomysis benedeni from Lake Constance. We provide δ15N and δ13C turnover rates based on nonlinear least‐squares regression and posterior linear regression models. Model precisions and fit were evaluated using Akaike's information criterion. Within a couple of days, the δ15N and δ13C of mysids began to change. Nevertheless, after about 14 days, L. benedeni did not reach equilibrium with their new isotope values. Since the experiment was conducted on adult subjects, it is evident that turnover was mainly influenced by metabolism (in contrast to growth). Unlike traditional dietary shifts, our laboratory‐based dual stable isotope tracer approach does not shift the experimental organisms into a new diet and avoids dietary effects on isotope values. Results confirm the application of isotopic tracers to label mysid subpopulations and could be used to reflect assimilation and turnover from the labeled dietary sources. Field‐based stable isotope studies often use isotopic mixing models commonly assuming diet‐tissue steady state. Unfortunately, in cases where the isotopic composition of the animal is not in equilibrium with its diet, this can lead to highly misleading conclusions. Thus, our laboratory‐based isotopic incorporation rates assist interpretation of the isotopic values from the field and provide a foundation for future research into using isotopic tracers to investigate invasion ecology.

Highlights

  • Stable isotope analysis (SIA) has been a routine tool in animal ecology and evolution, especially for estimation of trophic positions: A key parameter to understand food web structure in natural ecosystems (Gannes, O’Brien, & Martínez del Rio, 1997; Martínez del Rio, Wolf, Carleton, & Gannes, 2009)

  • For individuals that demonstrated a shift in isotope values toward the tracer values and toward equilibrium during the feeding trial, tissue turnover rates were estimated by fitting a nonlinear least-­squares regression model using the following equation: δt = δeq +e−(λ)t, where δt isotopic value (‰) at time t; δo initial isotopic value (‰) at equilibrium with the “normal” diet; δeq isotopic value (‰) after equilibration with the enriched diet; t time and λ = turnover rate

  • L. benedeni is reported as one of the most widespread invaders in Central Europe (e.g., Wittmann & Ariani, 2009). It originates from the area of the Black Sea and the estuaries of the Danube (Audzijonyte et al, 2009; Băcescu, 1954) and has been a threat to several large lakes, including Lake Constance

Read more

Summary

| INTRODUCTION

Stable isotope analysis (SIA) has been a routine tool in animal ecology and evolution, especially for estimation of trophic positions: A key parameter to understand food web structure in natural ecosystems (Gannes, O’Brien, & Martínez del Rio, 1997; Martínez del Rio, Wolf, Carleton, & Gannes, 2009). SIA is used in nutrition studies and dietary reconstruction such as those that investigate temporal change in diet, to evaluate contribution of dietary nitrogen or carbon sources, tissue-­ specific protein turnover rate, and spatio-­temporal relationships. Changes in the isotope values with dietary treatment as a function of time are necessary for accurate estimation of mixing models and models that apply nutritional studies of invader mysids and functionally similar native and non-­native species. Direct study of their diet in wild and laboratory condition has been challenging, because L. benedeni are difficult to observe in the wild and they digest different types of prey at different rates; and accurate identification of stomach contents could be difficult (Fink & Harrod, 2013; Gergs, Hanselmann, Eisele, & Rothhaupt, 2008; Hanselmann, Hodapp, & Rothhaupt, 2013; Rothhaupt et al, 2014)

| METHODS
Isotope Type
Findings
| DISCUSSION
Full Text
Published version (Free)

Talk to us

Join us for a 30 min session where you can share your feedback and ask us any queries you have

Schedule a call