In a cryptic habitat such as soil, trophic relationships are difficult to address and are further restricted by the small size of the fauna. The last decade has seen advances in biochemical ecology, particularly in the use of fatty acids as biomarkers for defining feeding strategies of the soil fauna under field conditions1,2,3. This is based on the fact that fatty acids from resources can be incorporated in consumer tissue as entire molecules, a process termed dietary routing4. Transfer of fatty acids has been reported over three trophic levels, i.e., from fungi to nematodes to Collembola5. Recently, the predatory fauna was considered6,7 and the first reviews on fatty acids as trophic markers in soil food webs have been published8,9.
More detailed information on trophic interactions is attained by fatty acid stable isotope probing (FA-SIP). The determination of 13C/12C ratios in fatty acids in diets and consumers can ascribe binary links and estimate the associated carbon flow, and has been employed in terrestrial, fresh water, and marine food webs10,11,12,13. The basic assumption is that dietary routed fatty acids are not subject to enzymatic processes; therefore, their 13C signal, i.e., the 13C/12C ratio of the fatty acid, in the consumer is similar to that in the diet1. However, a gradual depletion of the 13C signature up the food chain has been reported in aquatic systems, thereby hindering broad application of FA-SIP in trophic studies14,15,16. Moreover, knowledge in the lipid metabolism in most invertebrates in terrestrial food webs is still limited.
An understanding of the lipid metabolism pathways in consumers is essential for the usage of trophic marker fatty acids as means for the determination of the quantitative carbon flow in food web ecology. With this in mind, 13C-isotopologue profiling, which in principle can be applied for investigation of the carbon metabolism of any biological system17, is a promising method. Following the introduction of a 13C-labelled carbon substrate, the distribution of the 13C in the metabolic network is traceable since the generated metabolic products in the consumer show a specific isotopologue distribution. This can be assessed by quantitative nuclear metabolic resonance spectroscopy18,19 or mass spectrometry20,21, with the latter favored in biological samples with low biomass due to its higher sensitivity.
Although isotopologue profiling has been successfully applied to amino acids and provided insight into the in vivo carbon metabolism of bacterial pathogens17,22,23, its implementation in fatty acids has lagged behind. The first detailed analysis on the fate of a stable isotope labelled precursor fatty acid, its dietary routing or degradation via β-oxidation, in soil invertebrate consumers, was recently performed by Menzel et al.24. Here, the methodological basics for incorporation experiments with 13C labelled fatty acids followed by isotopologue analysis of key descendants in frequent soil invertebrates, the Collembola, are provided. These microarthropods are a good model group as they form important components of the soil food web and are well investigated for their trophic marker fatty acids8,25.
An understanding of the lipid metabolism pathways in consumers is essential for the usage of trophic marker fatty acids as means for the determination of the quantitative carbon flow in food web ecology. The present protocol gives the design and set up for a laboratory feeding experiment, and the biochemical procedures for extraction and methylation of dominant lipids fractions (neutral lipids, phospholipids) from Collembola. It demonstrates how the isotopologue composition of fatty acids is analyzed by mass spectrometry and describes the related formula and calculations. This procedure results in: (i) the ratios of isotopologues exceeding the mass of the parent ion (i.e., the fatty acid molecular ion M+) by one or more mass units (M+1, M+2, M+3, etc.) and (ii) the overall 13C enrichment in fatty acids derived from the 13C labelled precursor. Although used for Collembola, this approach can generally be applied to any other predator-prey interaction on the premise that these are culturable in sufficient quantity under controlled conditions to ensure a successful label uptake and subsequent verification.