Carbon isotopic fractionation was investigated in fatty acids (FA) of adipose tissue and blood serum of threatened Steller's eiders (Polysticta stelleri) and spectacled eiders (Somateria fischeri) relative to the FA in their diets. Captive eiders were fed a known diet for 180 days with serum sampled at 60, 120 and 180 days immediately after a 12 fast; adipose was collected at 180 days. Essential FA (EFA) in the adipose showed varying degrees of isotope fractionation (0–4‰), depending on FA structure. The δ13C values of long-chain FA 20:5n-3 and 22:6n-3 did not differ from those in the diet, while those of 18:2n-6 and 18:3n-3 were ∼2‰ greater than in the diet. The δ13C values of free FA (FFA) in serum were not consistent within individuals or sampling dates; fractionation varied randomly, suggesting that FFA were arising from diet, rather than mobilization from adipose tissue. Discrimination factors were used in combination with a mixing model incorporating FA and lipid concentrations to estimate the diet of eiders fed a binary mixture with contrasting isotopic signatures. Diet estimates varied with FA but mean values closely approximated the actual proportions consumed. By tracking EFA, this study avoided the complications in interpretation arising from isotopic routing of carbon in bulk isotope analyses and serves as a basis for the development of compound-specific isotopic methods to trace dietary input in wild eiders. However, our understanding of the processes contributing to the variation in isotopic signatures of FA in nature is currently limited, and we recommend that future research directions focus on elucidating these mechanisms.

The spectacled eider, Somateria fischeri (Brandt 1847), and the Alaskan breeding population of the Steller's eider, Polysticta stelleri (Pallas 1769), have experienced precipitous population declines of breeding birds in Alaska and are currently listed as threatened under the provisions of the US Endangered Species Act (Federal Register, 1993; Federal Register, 1997). Reasons for the declines remain largely unknown, but changes in the marine ecosystem leading to variation in the availability of food resources have been listed as potential causes and threats to the recovery of both species (US Fish and Wildlife Service, 1996; US Fish and Wildlife Service, 2002). Both Steller's and spectacled eiders use a range of marine habitats in the Bering Sea for staging, molting and wintering, and are thought to forage on a variety of prey items, including bivalves, crustaceans and snails (Petersen, 1980; Petersen, 1981; Petersen et al., 1998). Both eider species nest in tundra habitats along the coastal Bering and Beaufort Seas, and feed on insects, insect larvae, seeds and plant materials in tundra ponds (Petersen et al., 2000; Fredrickson, 2001). Reproductive problems and low productivity have been documented for both species (Grand et al., 2002; Rojek, 2008). In Steller's and spectacled eiders, the relative importance of marine and terrestrial nutrients for reproduction is unknown, but there is evidence to suggest that some sea duck species acquire nutrients for successful breeding from both the terrestrial nesting and marine staging grounds (Bond et al., 2007; Sénéchal et al., 2011). A better understanding of diet sources and timing of nutrient acquisition for these eiders will provide information to help identify important pre-breeding habitats of threatened eider populations in Alaska.

There are several well-known challenges and biases associated with traditional methods of estimating marine bird diets (reviewed in Barrett et al., 2007). New techniques using minimally invasive sampling methods and biochemical signatures in stored fat (Iverson et al., 2007; Wang et al., 2010), blood (Käkelä et al., 2009; Federer et al., 2010), stomach oil (Connan et al., 2005; Wang et al., 2007), feathers (Hobson and Clark, 1992) or eggs (Hobson, 1995; DeVink et al., 2011) provide promising alternatives for diet assessments in avian populations. These biomarker techniques typically involve either stable isotope or fatty acid (FA) analysis. For instance, stable isotopic analyses of carbon have been used to determine the relative contributions of sources of diet items (i.e. marine versus terrestrial, benthic versus pelagic), while stable nitrogen isotope analyses can indicate an animal's trophic level (Hobson and Welch, 1992; Hobson et al., 2002). However, there are limitations to the bulk isotope (i.e. measurement of the isotopic composition of total organic carbon or nitrogen in a sample) approaches, including isotopic routing and fractionations from diet to tissue that can complicate interpretation (Federer et al., 2010). As an alternative, FA signature analysis has been used to investigate diets of higher predators (e.g. Thiemann et al., 2007; Williams et al., 2008; Cooper et al., 2009), including captive eiders (Wang et al., 2010). FA are the primary components of most lipids and have a variety of structures. Because of biochemical restrictions, many dietary polyunsaturated FA (PUFA) are incorporated into marine animals with little modification to structure, making these FA valuable as indicators, or biomarkers, of their source. However, these biomarker techniques can only offer general information on temporal and spatial variation in consumer diets; much more complex models (i.e. quantitative fatty acid signature analysis, QFASA) (Iverson et al., 2004) are necessary to estimate proportions and types of prey species in predator diets using FA.

Recently, we demonstrated the use of stable carbon isotopes of individual FA to trace carbon flow from prey to predator across multiple trophic levels in the Arctic (Budge et al., 2008). This approach tracks the stable carbon isotopes of specific FA structures that can only arise from diet and has two clear advantages over the bulk isotope technique. First, this technique avoids the problem of isotopic routing encountered with bulk isotope analyses. Isotopic routing occurs when the carbon associated with a dietary component (protein, carbohydrate or lipid) is routed to a specific tissue component. For instance, dietary protein carbon is likely to be routed to body muscle tissue. Difficulties arise, however, when a dietary component, such as carbohydrate or lipid, is catabolized and used as a carbon source to synthesize another component, such as protein. The extent of routing can be influenced by nutrient content and digestibility of diets (Focken, 2004; Codron et al., 2011) and environmental factors (Bloomfield et al., 2011), and techniques such as lipid removal before isotopic analysis attempt to minimize its impact; however, it remains a complication in the interpretation of bulk carbon isotope analysis (Gannes et al., 1997; Wolf et al., 2009). Analysis of essential dietary FA that cannot be synthesized by animals thus avoids some of the difficulties associated with isotopic routing. Second, this technique acquires δ13C data of several FA within each sample near-simultaneously; when combined with mixing models to estimate source contributions, this allows several independent assessments of diet to be made, each based on an individual FA, thereby increasing the accuracy of the results. Thus, the combination of these features in the analysis of stable carbon isotopes of essential FA (EFA) offers clear benefits compared with the analysis of isotopes of bulk carbon.

While several studies have reported the stable carbon isotope composition (expressed as δ13C values) of FA in members of various food webs (Hammer et al., 1998; Ruess et al., 2005; Budge et al., 2008) and provided evidence to suggest that essential dietary FA δ13C values are preserved in the predator's tissues (Stott et al., 1997; Howland et al., 2003), none of these have adequately addressed the issue of molecular fractionation, or change in δ13C values during metabolism of dietary FA. The basic processes involved in avian lipid digestion, transport and deposition are fairly well understood (Klasing, 1998). In the simplest case, dietary lipids are predominantly triacylglycerols (TAG) consisting of three FA esterified to a glycerol backbone. FA in TAG molecules undergo a number of enzymatic processes (e.g. lipolysis and re-esterification) before being deposited in the adipose for storage. During periods of fasting, FA in the adipose are mobilized for energy and transported in the blood, bound to proteins, as free FA (FFA). FA may also be catabolized for energy in the liver or, in some situations, elongated or desaturated. These processes all involve enzyme-catalyzed reactions and introduce the potential for isotopic fractionation of the FA. Such fractionation may have a substantial impact on the interpretation of the FA δ13C values; thus, the extent of fractionation must be known before attempting to relate consumers' stable carbon isotope compositions to their diets.

Our objective was to determine the extent of molecular carbon isotopic fractionation that dietary FA experience during fat deposition and mobilization through controlled feeding studies with captive Steller's and spectacled eiders. Specifically, we measured the δ13C values of several essential and non-essential FA in diet, adipose and serum to create a mixing model incorporating information from molecular fractionation in the eider tissues, and proportions and δ13C values of specific FA in dietary end-members. We then tested this model on samples preserved from a previous captive feeding experiment (Wang et al., 2010) in which eiders were switched from a diet based on terrestrial material to experimental diets spiked with a different marine food item.

Controlled feeding studies

Feeding trials were conducted during the non-breeding season with eight male Steller's eiders and eight male spectacled eiders housed at the Alaska SeaLife Center in Seward, Alaska. Research was conducted under Institutional Animal Care and Use protocol number 09-008. For 2 years, these birds had been consistently fed a diet based on Mazuri© sea duck formula (Purina Mills, St Louis, MO, USA), which consisted of approximately 6.5% lipid, 21.6% protein, 8.4% fiber, 10.9% ash and 46.6% nitrogen-free extract along with vitamins (http://www.mazuri.com; accessed 15 March 2006). This was supplemented with ≤5% of other diet items, including Antarctic krill (Euphausia superba), Atlantic silverside (Menidia menidia), Atlantic surf clam (Spisula solidissima) and blue mussel (Mytilus edulis) (diet 1). This diet was also supplied throughout the 180 days of this experiment, with the intake of diet items recorded daily by species so that the actual diet could be calculated. Blood serum was sampled between 09:00 h and 12:00 h at 60, 120 and 180 days immediately after a 12 h fast. Up to 3 ml of whole blood was collected from the jugular vein using a 23 gauge needle and a 5 ml syringe, transferred to collection tubes (BD Vacutainer SST Plus Blood Collection Tubes, Franklin Lakes, NJ, USA) and allowed to clot at 4°C. Adipose tissues were collected from all birds at the end of the 180 days. A biopsy technique was used to obtain approximately 0.1 g of synsacral adipose tissue samples from individuals via a 1 cm skin incision (Iverson et al., 2007; Wang et al., 2010). The area was disinfected prior to biopsy with a betadine swab and lidocaine spray. Lidocaine was also injected subcutaneously. After surgery, the biopsy site was sealed with Vet-bond© (3M, St Paul, MN, USA). The adipose tissue sample was placed in a vial of chloroform with 0.01% butylated hydroxytoluene added as an antioxidant.

For comparison, samples from a previous controlled feeding experiment (Wang et al., 2010) were also analyzed. In that study, eiders were fed a consistent diet of predominantly Mazuri© (88%), supplemented with the same diet items as in diet 1 described above. After 69 days, the diets of the Steller's and spectacled eiders were switched to diet 2 which consisted of only Mazuri© and krill, at proportions of 66% and 34%, and 56% and 44%, respectively. These diets were maintained for 21 days and synsacral adipose tissue was collected as described above. For both experiments, samples of the Mazuri© and diet supplements were collected each month to monitor the consistency of FA level and isotopic composition (N=25; 5 samplings × 5 diet types consisting of Mazuri© and supplements of krill, silverside, clam and mussel). Samples were frozen intact and stored at –20°C until extracted.

Isolation of blood lipids, lipid extraction and FA analyses

Whole-blood samples were centrifuged to isolate serum at 1500 g for 10 min in a Clay Adams® TRIAC® centrifuge (Becton Dickinson Company, Franklin Lakes, NJ, USA) within 1–2 h of the blood draw. Lipids were extracted from all sample types (serum, adipose, diet samples) using a modified Folch extraction (Folch et al., 1957; Budge et al., 2006) with 2:1 chloroform:methanol. Thin-layer chromatography using a developing solvent of 85:15:1 hexane:diethyl ether:acetic acid was used to isolate FFA in fasting blood samples. FA methyl esters (FAME) were prepared directly from ≤100 mg of the extracted and isolated lipid using H2SO4 in methanol. FAME were then extracted into hexane and concentrated to 50 mg ml–1.

FAME were quantified using temperature-programmed gas chromatography (GC) as described previously (Budge et al., 2006), using a Perkin Elmer Autosystem II (Perkin Elmer, Boston, MA, USA) flame ionization detector (FID) gas chromatograph fitted with a 30 m×0.25 mm i.d. column coated with 50% cyanopropyl polysiloxane (0.25 μm film thickness; J&W DB-23; Folsom, CA, USA) and operating in split injection mode. For all sample types, 1.0 μl of a 50 mg ml–1 solution of FAME in hexane was injected. FA were identified using known standard mixtures (Nu Check Prep., Elysian, MN, USA) and GC-mass spectrometry (Thermo Finnigan Polaris Q; Thermo Finnigan, Austin, TX, USA). All sample chromatograms and FA identifications were individually checked, corrected, and reintegrated as necessary. Each FA was described using the shorthand nomenclature of A:Bn-X, where A represents the number of carbon atoms, B the number of double bonds and X the position of the double bond closest to the terminal methyl group.

The δ13C values of FAME sub-samples were determined by routing the effluent from a GC through a combustion interface (IsoLink; www.isolink.com) to an isotope ratio mass spectrometer (IRMS) (Thermo Finnigan Delta V). FAME were separated using the same GC column and temperature program as described above. The GC was operated in splitless injection mode and for adipose and serum samples, 1.0 μl of a 1.0 mg ml–1 FAME solution in hexane was injected. For diet samples, the concentration was reduced to 0.5 mg ml–1. Monounsaturated FAME isomers were adequately resolved by GC-FID but co-eluted with GC-IRMS so 16:1 and 18:1 represent the sum of those monounsaturated FAME species. FAME analyzed here differed from the FA present in the source material because of the addition of a methyl group derived from the methanol used in transesterification. To correct for the contribution from this extra carbon, we transesterified individual FFA standards 16:0 and 18:0 with the same reagents described above. The δ13C values for FFA and FAME derived from those were determined using an elemental analyzer (Costech ECS4010; Valencia, CA, USA) routed to the IRMS. The difference between the δ13C values for FFA and FAME with the same chain length was due to the added methyl group. The proportional contribution of this methyl group to a given FA depends on the chain length; an average δ13C value for this added methyl group was therefore calculated using the following equation:
(1)
where n is the number of C atoms in the FFA (Abrajano et al., 1994). The methyl C had an average value of –49.0±0.3‰. All FAME data were corrected for the contribution of this methyl group by rearranging the above equation. Analytical precision throughout the runs was tracked using an 18:0 standard and was ≤0.3‰. All δ13C values are reported relative to Vienna Pee Dee Belemnite using delta notation. These values were calibrated using a standard mixture consisting of ethyl and methyl esters of 14:0, 16:0, 18:0 and 20:0 supplied by Indiana University Stable Isotope Reference Materials, where r2 of the known versus expected relationship was >0.98.

Data analyses

A three-level one-way analysis of variance (ANOVA) was used to test for differences in δ13C values of each FA between species and diet 1. The δ13C values of FA of diet 1 were identical for the two species so were not compared. Post hoc testing was carried out using Tukey's test with an adjusted α-level of 0.017 (0.05/3). The δ13C values of FA of diet 2 were not identical so a four-level one-way ANOVA was conducted using an adjusted α-level of 0.013 (0.05/4) for post hoc testing. A two-level ANOVA was used to compare δ13C of FA of diet and the third serum sample, while repeated-measures ANOVA was used to test for differences between adipose and serum. All analyses were performed using SPSS 11. Stable isotopic discrimination factors (Δ) between FA in diet (D) and adipose (A) were calculated by subtracting the isotopic value of diet for each FA and individual eider from the corresponding value in the adipose tissue, so that ΔA–D=A–D. Similarly, discrimination factors were calculated between adipose (A) and serum (S) following the same equation (ΔS–A=S–A).

To test the efficacy of FA-specific isotope analysis in estimating dietary contributions, a two-end member mixing model was used to determine the relative contributions of Mazuri© and krill (diet 2) (Wang et al., 2010) to carbon in the FA examined:
(2)
where †13Ceider,j is the δ13C of the eider adipose for j, the FA of interest, Δj is the discrimination factor for diet to adipose transfer for j, xj is the proportion of Mazuri© carbon contribution to j, δ13CM is the δ13C of the Mazuri© FA and δ13Ck is the δ13C of the krill FA. To determine the contribution of Mazuri© carbon to all FA in general in the eider adipose tissue, the relative amounts of lipid and FA in the diet items must be taken into account:
(3)
where xFA is the proportional contribution of Mazuri© to all FA in the eider adipose, FAj,M is the average proportion of FAj in the Mazuri©, FAj,k is the average proportion of FAj in the krill, LM is the average lipid content of the Mazuri© and Lk is the average lipid content of the krill.

The major FA in all diet items were similar, with 16:0, 18:0 and 18:1 generally dominating the profiles (Table 1). The Mazuri© contained 18:2n-6 at 38% by mass of total FA and was distinct from the other diet items, all of which had 18:2n-6 levels <2%. Except for the mussel, levels of 18:3n-3 were also much greater in Mazuri© (4% versus <1%) than in the diet supplements. Conversely, clam, krill, mussel and silverside contained the marine FA 20:5n-3 and 22:6n-3 at levels 3–10 times greater than Mazuri©. The FA compositions in adipose and serum were similar for both Steller's and spectacled eiders. The adipose FA of both eider species were broadly similar to that of Mazuri©, the major component in diet 1, with 16:0, 18:1 and 18:2n-6 dominating both profiles; however, relative proportions in adipose and Mazuri© differed (Tables 1 and 2). For example, the ratio of 18:2n-6 to 18:1 in Mazuri© was approximately 2:1 but only 1:2 in the adipose. Serum FFA also showed variation in proportions relative to the adipose from which they were mobilized. For instance, serum consistently contained greater amounts of 16:0 and 18:0, and lower levels of 18:1 and 18:2n-6 than adipose.

Table 1.

Mass percent and δ13C values of FA in diet items for diet 1 (this study) and diet 2 (Wang et al., 2010)

Mass percent and δ13C values of FA in diet items for diet 1 (this study) and diet 2 (Wang et al., 2010)
Mass percent and δ13C values of FA in diet items for diet 1 (this study) and diet 2 (Wang et al., 2010)
Table 2.

FA composition in adipose tissue and blood serum of Steller's and spectacled eiders fed diet 1

FA composition in adipose tissue and blood serum of Steller's and spectacled eiders fed diet 1
FA composition in adipose tissue and blood serum of Steller's and spectacled eiders fed diet 1

The δ13C values of individual FA were generally similar in the Mazuri©, clam, mussel and silverside in diet 1 (Table 1). For instance, the δ13C values of 18:2n-6 ranged from –29.2‰ to –28.6‰ in the four diet items, while 22:6n-3 ranged from –26.5‰ to –24.3‰. Krill FA were all much more isotopically depleted, with δ13C values in the six FA analyzed varying from –39.2‰ to –31.9‰. Similar patterns were evident in the Mazuri© and krill of diet 2. Based on the known lipid contents (data not shown), concentrations and δ13C values of FA in individual diet items (Table 1), and proportions of each diet item consumed (Table 1), a δ13C value of each FA in the total diet was calculated (Fig. 1). For all FA except 20:5n-3 and 22:6n-3, a consistent and significant (P<0.017) isotopic enrichment in carbon of 1–4‰ was evident in the adipose of both eider species relative to diet 1 (Fig. 1). In general, this enrichment was less for EFA (18:2n-6, 18:3n-3, 20:5n-3 and 22:6n-3) than for non-EFA, with the exception of 16:1 (Fig. 1); this FA had a ΔA–D of ∼1, similar to that of the EFA. Values for δ13C of 20:5n-3 and 22:6n-3 in the adipose of both species were not significantly different from diet 1. There was also a very limited species effect for eiders fed diet 1; only δ13C of 16:0 showed a subtle but significant difference (P<0.017) between the two species (–23.7±0.2‰ and –24.4±0.2‰, for Steller's and spectacled eiders, respectively). Isotopic enrichment of the FA in eider adipose was less consistent between species for eiders fed diet 2 (Fig. 2); however, no significant differences in δ13C values of each FA in adipose between species were found, due to the large variance (up to ∼2‰) associated with the measurements. Isotopic values were more similar between diet 2 and adipose, with 16:0, 18:0 and 18:3n-3, in addition to 20:5n-3 and 22:6n-3, showing similarity (P>0.013) in δ13C values in both species.

Fig. 1.

δ13C values (means and s.e.) of diet, adipose and serum fatty acids (FA) for (A) Steller's eider and (B) spectacled eider fed diet 1 for 180 days. The same letters indicate statistically similar values. All other comparisons are significantly different (P<0.017).

Fig. 1.

δ13C values (means and s.e.) of diet, adipose and serum fatty acids (FA) for (A) Steller's eider and (B) spectacled eider fed diet 1 for 180 days. The same letters indicate statistically similar values. All other comparisons are significantly different (P<0.017).

Mean stable isotopic discrimination factors of FA in adipose and diet varied from –0.5‰ to +4‰ within a species (Table 3); within a FA, there was not a significant difference between species (Table 3). The estimated proportions of Mazuri© consumed in diet 2 were calculated based on the discrimination factors of strictly dietary FA (18:2n-6, 18:3n-3, 20:5n-3 and 22:6n-3; Table 3), the measured FA δ13C value in the adipose (Fig. 2), and the lipid content (not shown), FA proportion and FA δ13C value of each of the two diet items (Table 1), following Eqns 2 and 3. Estimated proportions varied widely among the FA but estimates based on 20:5n-3 were closest to actual in both species (Table 3). However, the errors associated with estimates that included contributions from 20:5n-3 and 22:6n-3 were large because of the large uncertainty associated with the discrimination factors for those two FA. Accurate estimates with much lower errors were obtained when means were calculated using only 18:2n-6 and 18:3n-3 (estimates of 42±9% and 41±10% versus actual of 34% and 44% in Steller's and spectacled eiders, respectively).

Table 3.

Discrimination factors calculated from comparison of δ13C values in adipose and diet 1

Discrimination factors calculated from comparison of δ13C values in adipose and diet 1
Discrimination factors calculated from comparison of δ13C values in adipose and diet 1
Fig. 2.

δ13C values (means and s.e.) of diet and adipose FA for (A) Steller's eider and (B) spectacled eider fed diet 2 for 21 days. The same letters indicate statistically similar values. All other comparisons are significantly different (P<0.013).

Fig. 2.

δ13C values (means and s.e.) of diet and adipose FA for (A) Steller's eider and (B) spectacled eider fed diet 2 for 21 days. The same letters indicate statistically similar values. All other comparisons are significantly different (P<0.013).

With the exception of 16:1 in the Steller's eiders and 18:3n-3 in both species, δ13C values of serum FA were all significantly depleted (P<0.05) relative to adipose, and were much more similar to dietary isotopic values (Fig. 1). Discrimination factors for the mobilization of FA from adipose to serum varied widely and showed little consistency within individuals and FA (Fig. 3). The most extreme example of variability among serum collections in one individual occurred for 18:3n-3 in spectacled eider 016, where discrimination factors ranged from a low of –7.1 to a high of +5.6. In many individuals, the isotopic values of two of the three serum samples agreed quite well (Fig. 3); however, there was no regularity in the pattern and the dissimilar sample was not associated with a particular blood collection.

Diet to adipose isotopic discrimination factors

Potential explanations for the variation in discrimination factors with FA structure require consideration of the metabolic pathways that FA can follow after consumption (see Stevens, 1996; Klasing, 1998; Price, 2010). Dietary lipids, after crossing through the epithelial cells in the intestine, are first transported in the blood as portomicrons, the avian equivalent of mammalian chylomicrons, and routed directly to the liver. There they can be reassembled into very low-density lipoproteins (VLDL) for transport to other tissues (e.g. muscle and adipose), elongated/desaturated, stored or catabolized for energy (Stevens, 1996). If dietary lipids are in excess, some proportion is transported as VLDL to adipose tissue for storage. In a fasting state, FFA (or non-esterified FA) are mobilized from adipose for transport to tissues where they are catabolized as fuel. Within this context, a number of mechanisms could explain our results.

Fig. 3.

Discrimination factors for the mobilization of free FA (FFA) from adipose to serum. Data are displayed for each individual at each of three collection periods (circle, 60 days; square, 120 days; triangle, 180 days).

Fig. 3.

Discrimination factors for the mobilization of free FA (FFA) from adipose to serum. Data are displayed for each individual at each of three collection periods (circle, 60 days; square, 120 days; triangle, 180 days).

De novo synthesis of the saturated and monounsaturated FA could be occurring and would explain some of the observed fractionation. Similarly, elongation and desaturation of precursors could also occur to form saturates and monounsaturates, likely resulting in fractionation (Monson and Hayes, 1982). However, the birds were fed nutritionally sound diets with an excess of lipids and in that situation, enzymes associated with these processes are commonly down-regulated so it is unlikely that either biosynthesis or modification of FA was occurring (Stevens, 1996; Gurr, 1997). Synthesis of the n-3 and n-6 PUFA is impossible, as vertebrates do not possess the necessary enzymes to do so.

When FA are packaged into portomicrons for transport in the blood or deposited in the liver for storage, they must first be hydrolyzed, or cleaved, from a glycerol backbone to cross the cell membrane of epithelial and endothelial cells and then re-esterified into an intact TAG. The hydrolysis and re-esterification reactions are mediated by enzymes and therefore are subject to kinetic fractionation. However, both hydrolysis and re-esterification involve breaking or forming a bond between a carbon atom in the glycerol backbone and an oxygen atom in the fatty acyl chain; there is no reasonable mechanism for a FA with an isotopically lighter carbon atom to be selected, as only the oxygen atom on the FA chain takes part in the reaction. Thus, portomicron formation and FA deposition in the liver can be eliminated as causes of the observed fractionation. In fact, all lipid-transport processes supplying TAG to tissues involve these processes of hydrolysis and re-esterification and can be eliminated as sources of fractionation. Similarly, selective mobilization of isotopically lighter FA from the adipose tissue during fasting proceeds through hydrolysis of TAG and is unlikely to result in fractionation for the same reason.

The only probable explanation that remains for fractionation is catabolism of FA for energy. Catabolism of FA in the liver before deposition in adipose could lead to these results if enzymes associated with β-oxidation discriminate FA substrates according to their masses and favor those with lighter masses. This selection would result in more rapid oxidation of the isotopically lighter FA, leaving a greater proportion of isotopically heavier FA to be routed to the adipose for deposition, and offers a reasonable explanation for the enrichment in 13C found in most FA in the adipose relative to the diet. Such a process also agrees with the original data of Deniro and Epstein where respired CO2 was found to be isotopically lighter than that of either diet or tissue, likely the result of catabolism (Deniro and Epstein, 1978).

McMahon and colleagues found variable carbon isotopic fractionation in non-essential amino acids between diet and muscle tissue in a fish species, but practically no fractionation of essential amino acids (McMahon et al., 2010); similar results have also been reported for amino acids in insects (O'Brien et al., 2005). Here, we present data for four FA that would normally be considered essential, based on an inability of the eiders as vertebrates to synthesize these FA de novo: 18:2n-6, 18:3n-3, 20:5n-3 and 22:6n-3 (Stevens, 1996; Klasing, 1998; Cunnane, 2003). We found no discrimination of 20:5n-3 and 22:6n-3 between diet and adipose (Figs 1 and 2); however, we found substantial variation in the discrimination factors of 18:2n-6 and 18:3n-3 (∼2‰ and 1.5‰, respectively). This seemingly differential fractionation of EFA may be tied to the criteria used to define essentiality. Vertebrates lack the enzymes necessary to form 18:2n-6 and 18:3n-3 from precursors so these FA are normally considered essential because they cannot be synthesized de novo. However, it is the longer chain PUFA, 20:4n-6, 20:5n-3 and 22:6n-3, rather than 18:2n-6 and 18:3n-3, that have important physiological functions, such as nervous system development and hormone signaling (Gurr, 1997; Ackman and Cunnane, 1992). Although 18:2n-6 and 18:3n-3 themselves have no known essential functions, they can serve as precursors for the synthesis of the longer chain PUFA through elongation and desaturation, and eliminate symptoms of EFA deficiency (Ackman and Cunnane, 1992; Cunnane, 2003), so they are therefore also considered EFA [see Cunnane (Cunnane, 2003) for full discussion of criteria for essentiality]. There is evidence from fish (Tocher, 2003) that the enzymes responsible for elongation and desaturation of precursors are much less active in marine environments where long chain essential PUFA are plentiful. Similar arguments have been proposed to explain the inability of most humans in Western society to form long chain PUFA from precursors when consuming diets high in PUFA (Siguel and Maclure, 1987; Ackman and Cunnane, 1992). If the ‘essential’ function of 18:2n-6 and 18:3n-3 is to serve as precursors for synthesis of 20:5n-3, 20:4n-6 and 22:6n-3 but those long chain PUFA are not being formed by elongation and desaturation, then 18:2n-6 and 18:3n-3 would not have a direct essential function. In that situation, there would be no need to spare them from oxidation and we might then expect discrimination of these FA. However, this line of reasoning fails for 18:3n-3 when diet 2 is considered. For diet 2, 18:3n-3 showed no net fractionation from diet to adipose, despite the presence of even larger amounts of 20:5n-3 and 22:6n-3 in diet 2 than in diet 1 (Table 4). If 18:3n-3 were being catabolized because it was not essential as a result of sufficient levels of long chain PUFA in the diet, one would expect catabolism to continue in eiders fed diet 2, which contains even higher levels of those PUFA.

Table 4.

Approximate concentrations of FA consumed with each diet

Approximate concentrations of FA consumed with each diet
Approximate concentrations of FA consumed with each diet

Catabolism of specific FA may also be driven by dietary excess of those FA. Essentiality implies that there is some absolute dietary intake of a FA that must be met. Amounts consumed in excess of that minimum amount could simply be used as a substrate for oxidation, like a ‘non-essential’ FA. The major FA in diet 1 was 18:2n-6 (Table 4), at approximately 39% of total FA. Free-ranging eiders would not normally consume such high levels of 18:2n-6, with that FA typically present in proportions <12% in most marine bivalve species (Table 1) (Joseph, 1982), as well as aquatic insects (Goedkoop et al., 2000; Sushchik et al., 2003) and plants (e.g. Copeman et al., 2009). Known diet items for free-ranging eiders would also be expected to have low lipid contents, so that 18:2n-6 would make very little contribution to total FA consumed. In captive eiders fed high quality diet ad libitum, it is possible that the 18:2n-6 in the diets is in excess of their dietary needs. Such an excess is likely to be catabolized for energy, as with any other FA. In fact, it might be that 18:2n-6 is being preferentially catabolized simply because of this potential excess in the diet. Ackman and Cunnane proposed the same explanation for the preferential oxidation of 18:2n-6 in Western human diets (Ackman and Cunnane, 1992); the effect is also well known in aquaculture fish species (Turchini et al., 2009). A similar scenario could also be true with 18:3n-3. The amount of that FA consumed by the eiders is far less than that of 18:2n-6 but it might remain in excess of some unknown minimum, thus resulting in selective catabolism and the observed fractionation when diet 1 is consumed. For diet 2, the levels of 18:3n-3 consumed dropped substantially so that amounts of 18:3n-3 were much less than those of 20:5n-3 and 22:6n-3 and there was no net fractionation between diet and adipose. It may be that amounts of 18:3n-3 had fallen below some minimum dietary threshold so there was no excess to oxidize, while 20:5n-3 and 22:6n-3 remained below their minimum necessary levels, suppressing catabolism of those FA. A similar explanation may apply to the discrimination factor observed for 16:1. This FA was present at amounts <150 mg 100 g–1 in diet 1, levels similar to 18:3n-3, 20:5n-3 and 22:6n-3; these relatively low levels may make it a poor substrate for oxidation. In diet 2, the concentration of 16:1 increased almost 4-fold, and showed fractionation more similar to the other abundant FA.

Finally, our results may also be influenced by turnover times of FA in the adipose tissue. If one accepts the idea that fractionation is due to oxidation of excess FA, one might expect that less fractionation would be observed with a drop in levels of dietary 18:2n-6 and 18:3n-3. Certainly, the result for 18:3n-3 in diet 2 agrees with this; however, very similar isotopic enrichment was observed for 18:2n-6 in the two diets, despite the drop in intake. Eiders were only fed diet 2 for 21 days; that period of time may not have been sufficient to fully replace the large amount of 18:2n-6 originally deposited in the adipose tissue. Indeed, the proportions of 18:2n-6 did not fall to match dietary levels, unlike most other FA including 18:3n-3, 20:5n-3 and 22:6n-3 [data in Wang et al. (Wang et al., 2010)]. Thus, it is likely that the δ13C value for adipose after 21 days on diet 2 was still heavily influenced by the δ13C of the previously fed diet, rather than the new diet.

All of this discussion raises important questions about fractionation of FA that should be addressed before FA-specific isotope analysis is used to estimate diets of consumers. Based on the above arguments, only PUFA that cannot be synthesized de novo would be useful in tracking diet and it seems reasonable to conclude that eiders foraging in their natural environment would experience little fractionation in 18:3n-3, 20:5n-3 and 22:6n-3. However, from the present data, it is difficult to assign a reliable discrimination factor to 18:2n-6. More experimentation, using diets that are more similar to those consumed by free-ranging eiders, is needed to address these questions.

Adipose to serum isotopic discrimination factors

During fasting, FA are mobilized from adipose and transported in the blood to other tissues where they can be catabolized for energy (Stevens, 1996; Price, 2010). Thus, it is reasonable to expect that the δ13C values of serum FFA would resemble the adipose lipids that they were derived from. Analysis of serum FFA therefore represented a much less invasive manner to indirectly measure adipose FA δ13C values. The process of mobilization involves hydrolysis of FA from TAG molecules in the adipose and, as described above, does not involve the cleavage of a bond involving a carbon atom in the FA chain. There is also no opportunity during this mobilization for synthesis or modification of FA so all six FA measured in serum, including saturated and monounsaturated FA, could be compared between the tissues without concern for biosynthetic modification of δ13C of FA. Because of these restrictions, we did not expect to observe fractionation arising from the mobilization of FA from adipose to serum. Instead, we found fractionation for that transfer and it appeared to be random (Fig. 3), which suggests some challenges associated with the methodology.

Fasting, as well as strenuous exercise, results in increased mobilization of FFA from adipose stores into the bloodstream in both humans (Cortright et al., 1997) and birds (Lien et al., 1999; Price et al., 2008) but there are few data available to indicate the minimum time period necessary to promote this mobilization. Lien and colleagues (Lien et al., 1999; Lien and Jan, 2003) used a fasting period of 3 days with Tsaiya ducks (Anas platyrhynchos var. domestica), a larger species, while Käkelä and colleagues (Käkelä et al., 2006; Käkelä et al., 2007; Käkelä et al., 2009) used a period of 24 h to ensure that portomicrons derived directly from diet were eliminated from circulation in several seabird species. Eiders in this study were fasted for a shorter period of 12 h prior to blood sampling. We used thin-layer chromatography to isolate FFA from other lipid classes in the serum samples, so that the δ13C data would only reflect those of FFA mobilized from adipose. However, FFA can also arise through natural hydrolysis of lipids, such as TAG and phospholipids, during sample collection and analysis (Christie, 2003), so the FFA that were isolated in eider serum may have represented degradation products of either dietary lipids in the form of portomicrons or lipids present in blood lipoproteins. Typical fasting levels of FFA seem to vary by species and likely by body mass but are generally of the order of 20–50% that of TAG. For instance, Lien and collegues found FFA at ∼25% of TAG after a 3 day fast in ducks (Lien et al., 1999). With much smaller body masses of <30 g, white-throated sparrows (Zonotrichia albicollis) also had FFA levels ranging from 25% to 50% that of TAG after an overnight fast of unspecified duration (Smith et al., 2007). In contrast, analysis of lipid class data showed FFA at trace levels (<5% of TAG) in all eider serum samples, suggesting that the FFA were derived from the breakdown of circulating lipids, rather than mobilized from TAG in adipose. The δ13C values of serum FFA were intermediate between those of diet and adipose (Fig. 1) and, for 16:1 and 18:2n-6, were not significantly different from diet in both eider species. This suggests a strong dietary influence; if portomicrons were still circulating after a 12 h fast, hydrolysis of the dietary TAG carried within them would likely result in the similarity in δ13C values of the two FA. It is likely that a longer fasting period is necessary to reduce levels of circulating TAG and to promote mobilization of FFA from adipose.

Because it was not possible to sample adipose at all three time points when blood was collected, it was necessary to make the assumption that the δ13C of FA in adipose did not vary from day 60 to day 180 so that discrimination factors calculated at 60 and 120 days incorporated δ13C from adipose at 180 days. The diets fed for the duration of the experiment were very similar to the maintenance diets fed prior to and after the study, consisting of ∼95% Mazuri© with supplementation with other diet items. Thus, it is likely that the δ13C values of FA in adipose were quite similar at all time points.

Regardless of the cause of the variance in discrimination factors for mobilization of FFA from adipose to blood, there is clearly a need for further research. A first essential step is to determine the minimum time necessary to promote mobilization of FFA from adipose. This could be accomplished by simple tracer experiments where a dietary pulse of FA that is not present in the regular diet is provided. For instance, 23:0 could be fed in a large dose to the eider and the time required for its clearance from the blood determined by periodic analysis of serum FFA. With that time frame established, it would be relatively simple to repeat the serum and adipose collections to initially establish consistency of discrimination factors for FA within individuals and likely within species, assuming a constant diet was maintained.

Diet estimation

The development of an additional technique to estimate diet in eiders was the ultimate goal of this work. A necessary criterion for this application is the presence of distinct isotopic signatures of FA in different sources. Marine FA would be expected to follow the same trend as observed with bulk carbon analysis and be enriched in 13C relative to terrestrial plant material produced via C3 photosynthesis. However, Mazuri© is based primarily on corn, a C4 plant that is typically enriched in 13C relative to C3 plants, and such enrichment in C4 plants can lead to isotopic signatures that are very similar to marine values. We clearly saw this effect in our data with little consistent variation in the δ13C values of FA among Mazuri©, clam, mussels and silverside. Conversely, the δ13C values of Antarctic krill analyzed here were more depleted by at least 6‰ compared with the Mazuri© in the four PUFA used in the diet estimates (Table 1); such depletion is typical of Antarctic krill (Schmidt et al., 2003) and provided a convenient opportunity to test our mixing model. Estimates using all four PUFA allowed an accurate mean to be calculated. In the wild, our interest in eider diets is to differentiate between terrestrial/aquatic and marine sources but it is unlikely in that application that 20:5n-3 and 22:6n-3 will provide useful estimates. Terrestrial plants will contain very little, if any, of those two FA (Gunstone et al., 1986), and it will be necessary to rely on FA with limited synthesis pathways common to both systems, such as 18:2n-6 and 18:3n-3. In the present study, if only those two FA are used, estimates for diet 2 for both species would be ∼41±10% Mazuri© (Table 3), despite very different estimates for individual birds, suggesting that the results would remain accurate with fewer FA analyzed.

No significant difference was found between the δ13C values of diet 1 and adipose for 20:5n-3 and 22:6n-3 because of their high variance, implying that ΔA–D=0. However, when such a value was used in the diet calculation as the discrimination factor for 20:5n-3, estimates of proportions of Mazuri© consumed for Steller's eiders had a meaningless, negative value (Table 3). Thus, non-zero discrimination factors were calculated and applied. Earlier discussion has offered explanations to support the similarity in δ13C values in adipose and diet for those FA, and highlighted the implications; the need to use non-zero ΔA–D does not necessarily contradict this and arises because of the high variance in the measurements rather than a clear dissimilarity in values.

While the mean of the individual estimates did provide an accurate assessment of proportions, the error associated with 20:5n-3 and 22:6n-3 was large. Although only three individuals of each species were available to test diet estimates, the large errors were not a consequence of variation due to low sample number; rather, they were derived from the discrimination factors calculated in the initial experiment where eight individuals were analyzed. Both 20:5n-3 and 22:6n-3 were present at low concentrations (<0.5% of total FA), resulting in lower sample precision. These errors were then propagated through the calculation, generating the high variation in the individual estimates for those FA. Conversely, 18:2n-6 and 18:3n-3 were present at higher concentrations (∼22% and 1.5% for 18:2n-6 and 18:3n-3, respectively) and variations in the resulting estimates were small. When only those two FA were used to estimate diet, the associated errors were much more reasonable at 9% and 10% for Steller's and spectacled eiders, respectively (Table 3), demonstrating that it is possible to achieve diet estimates with low variation. However, none of the estimates based solely on individual FA were accurate. Clearly, in this application, the accuracy of an estimate is not necessarily linked to its reproducibility.

Implications and recommendations

This study establishes a starting point for estimating predator diets using stable isotopes of FA, and highlights several key considerations. Perhaps the most important issue in the application of this technique is the research question to be addressed. Like analyses of bulk isotopes, this technique can yield information about the origin of material in predator diets but only sources with distinct isotopic values can be differentiated. Thus, we would expect this method to be useful in situations similar to those in which bulk isotope values are commonly used. For instance, we have previously demonstrated the potential utility of the compound-specific approach in differentiating between ice algal and phytoplankton carbon (Budge et al., 2008), and it is likely to also be useful in addressing questions that differentiate between benthic and pelagic sources, and marine and terrestrial material. In more complicated situations, with more than two distinct sources, simple mixing models will not suffice and much more complex statistics will be required to assign sources (e.g. Ward et al., 2010). It may also be possible to combine information from proportional FA composition (e.g. Iverson et al., 2004; Wang et al., 2010) with δ13C values of FA so that more reliable diet estimates can be made.

Several issues remain to be addressed before this technique can be used to reliably trace carbon sources in free-ranging birds. For instance, nutritional quality and digestibility of food is known to influence discrimination factors at the bulk level (Codron et al., 2011) and the subjects in our captive study showed differential catabolism, depending upon the amounts of EFA in their diets. In free-ranging birds, it would be impossible to know the levels of dietary FA consumed and therefore difficult to assign appropriate discrimination factors. More controlled feeding studies, with diets of varying FA concentrations similar to wild diets, would help resolve this issue. Specifically, we must understand the variation in discrimination factors with changing dietary FA levels. This also relates to a second issue concerning the period of feeding represented by dietary FA in adipose tissues, as well as their turnover times. Both are poorly understood in birds and will also influence the accuracy of diet estimates. In fact, we suspect that the variation in our diet estimates was linked to a failure in equilibration of adipose tissue FA with the new diet. Turnover time will depend on the concentrations of FA in the diet and would also best be established by feeding ecologically relevant diets. Thus, we recommend that carefully designed feeding studies be used to address both issues of differential catabolism and turnover time.

Another hurdle is simply demonstrating the utility of this compound-specific approach compared with bulk stable carbon isotope analyses. We believe the advantages associated with isotopic routing of EFA and the ability to obtain multiple diet estimates from several FA in a single sample make the FA-specific approach superior to analyses of bulk stable carbon isotopes. However, this technique requires more involved sample preparation and expensive instrumentation; it also relies on information from lipids, a dietary component that is usually removed before bulk analysis is conducted (Post et al., 2007). A clear advantage, either in accuracy or reproducibility of diet estimates generated with FA stable carbon isotopes, is required. We therefore recommend that future studies also determine bulk stable carbon isotopes of the same lipid-extracted material as analyzed with the FA-specific technique, so that diet estimates derived from the two methods based on different dietary components can be compared.

While some questions do remain concerning the application of this FA-specific stable carbon isotope technique, we believe the study of EFA will allow us to ultimately derive accurate discrimination factors because we will be able to focus on the specific pathways involved, rather than relying only on empirical factors. Analyses of bulk δ13C values have been used since the 1970s in ecological studies but many uncertainties remain concerning fractionation of isotopes (Hussey et al., 2010; Wessels and Hahn, 2010). We hope that the limited metabolic pathways that EFA can follow will allow faster progress to be made in the compound-specific area. Because our understanding of the processes contributing to the variation in isotopic signatures of FA in nature is currently limited, we recommend that future research directions focus on elucidating these mechanisms.

FUNDING

Financial support was provided by the North Pacific Research Board [NPRB project 912] and the US Fish and Wildlife Service. This is North Pacific Research Board publication no. 299. The National Science Foundation provided partial support [grant ARC-0902177 to M.J.W. and S.M.B.] for a tailored GC-IRMS training course (organized by ISOMASS and conducted by Dr Gilles St Jean at the University of Alaska Fairbanks) attended by S.W.W. and M.J.W. This study was also supported by the National Science Foundation [grant DBI-0821856 to M.J.W.].

We thank two anonymous reviewers for their constructive and detailed comments that helped us in the production of this paper. Tim Howe and Norma Haubenstock at the Alaska Stable Isotope Facility and Anne Timmins at the Canadian Institute of Fisheries Technology provided assistance during sample analyses. We thank Heidi Cline, Tasha DiMarzio and the eider husbandry team at the Alaska SeaLife Center for care of the birds and assistance with our study. We also thank Ann Riddle and Jennifer Curl for laboratory assistance, and Dr Pam Tuomi and Jane Belovarac for veterinary assistance.

Abrajano
T. A.
Jr
,
Murphy
D. E.
,
Fang
J.
,
Comet
P.
,
Brooks
J. M.
(
1994
).
13C/12C ratios in individual fatty acids of marine mytilids with and without bacterial symbionts
.
Org. Geochem.
21
,
611
-
617
.
Ackman
R. G.
,
Cunnane
S. C.
(
1992
).
Long-chain polyunsaturated fatty acids: sources, biochemistry and nutritional/clinical applications
. In
Advances in Applied Lipid Research
(ed.
Padley
F. B.
), pp.
161
-
215
.
London
:
Jai Press
.
Barrett
R. T.
,
Camphuysen
K. C. J.
,
Anker-Nilssen
T.
,
Chardine
J. W.
,
Furness
R. W.
,
Garthe
S.
,
Hüppop
O.
,
Leopold
M. F.
,
Montevecchi
W. A.
,
Veit
R. R.
(
2007
).
Diet studies of seabirds: a review and recommendations
.
ICES J. Mar. Sci.
64
,
1675
-
1691
.
Bloomfield
A. L.
,
Elsdon
T. S.
,
Walther
B. D.
,
Gier
E. J.
,
Gillanders
B. M.
(
2011
).
Temperature and diet affect carbon and nitrogen isotopes of fish muscle: can amino acid nitrogen isotopes explain effects?
J. Exp. Mar. Biol. Ecol.
399
,
48
-
59
.
Bond
J. C.
,
Esler
D.
,
Hobson
K. A.
(
2007
).
Isotopic evidence for sources of nutrients allocated to clutch formation by harlequin ducks
.
Condor
109
,
698
-
704
.
Budge
S. M.
,
Iverson
S. J.
,
Koopman
H. N.
(
2006
).
Studying trophic ecology in marine ecosystems using fatty acids: a primer on analysis and interpretation
.
Mar. Mamm. Sci.
22
,
759
-
801
.
Budge
S. M.
,
Wooller
M. J.
,
Springer
A. M.
,
Iverson
S. J.
,
McRoy
C. P.
,
Divoky
G. J.
(
2008
).
Tracing carbon flow in an arctic marine food web using fatty acid-stable isotope analysis
.
Oecologia
157
,
117
-
129
.
Christie
W. W.
(
2003
).
Lipid Analysis
.
Dundee
:
Oily Press
.
Codron
D.
,
Codron
J.
,
Sponheimer
M.
,
Bernasconi
S. M.
,
Clauss
M.
(
2011
).
When animals are not quite what they eat: diet digestibility influences 13C-incorporation rates and apparent discrimination in a mixed-feeding herbivore
.
Can. J. Zool.
89
,
453
-
465
.
Connan
M.
,
Mayzaud
P.
,
Boutoute
M.
,
Weimerskirch
H.
,
Cherel
Y.
(
2005
).
Lipid composition of stomach oil in a procellariiform seabird Puffinus tenuirostris: implications for food web studies
.
Mar. Ecol. Prog. Ser.
290
,
277
-
290
.
Cooper
M. H.
,
Budge
S. M.
,
Springer
A. M.
,
Sheffield
G.
(
2009
).
Resource partitioning by sympatric pagophilic seals in Alaska: monitoring effects of climate variation with fatty acids
.
Polar Biol.
32
,
1137
-
1145
.
Copeman
L. A.
,
Parrish
C. C.
,
Gregory
R. J.
,
Jamieson
R. E.
,
Wells
J.
,
Whiticar
M. J.
(
2009
).
Fatty acid biomarkers in coldwater eelgrass meadows: elevated terrestrial input to the food web of age-0 Atlantic cod Gadus morhua
.
Mar. Ecol. Prog. Ser.
386
,
237
-
251
.
Cortright
R. N.
,
Muoio
D. M.
,
Dohm
G. L.
(
1997
).
Skeletal muscle lipid metabolism: a frontier for new insights into fuel homeostasis
.
J. Nutr. Biochem.
8
,
228
-
245
.
Cunnane
S. C.
(
2003
).
Problems with essential fatty acids: time for a new paradigm?
Prog. Lipid Res.
42
,
544
-
568
.
Deniro
M. J.
,
Epstein
S.
(
1978
).
Influence of diet on carbon isotopes in animals
.
Geochim. Cosmochim. Acta
42
,
495
-
506
.
DeVink
J.-M.
,
Slattery
S. M.
,
Clark
R. G.
,
Alisauskas
R. T.
,
Hobson
K. A.
(
2011
).
Combing stable-isotope and body-composition analyses to assess nutrient-allocation strategies in breeding white-winged scoters (Melanitta fusca)
.
Auk
128
,
166
-
174
.
Federal Register
(
1993
).
Final rule to list the spectacled eider as threatened
.
Fed. Regist.
58
,
27474
-
27480
.
Federal Register
(
1997
).
Endangered and threatened wildlife and plants; threatened status for the Alaska breeding population of the Steller’s eider
.
Fed. Regist.
62
,
31748
-
31757
.
Federer
R. N.
,
Hollmén
T. E.
,
Esler
D.
,
Wooller
M. J.
,
Wang
S. W.
(
2010
).
Stable carbon and nitrogen isotope discrimination factors from diet to blood plasma, cellular blood, feathers, and adipose tissue fatty acids in spectacled eiders (Somateria fischeri)
.
Can. J. Zool.
88
,
866
-
874
.
Focken
U.
(
2004
).
Feeding fish with diets of different ratios of C3- and C4-plant-derived ingredients: a laboratory analysis with implications for the back-calculation of diet from stable isotope data
.
Rapid Commun. Mass Spectrom.
18
,
2087
-
2092
.
Folch
J.
,
Lees
M.
,
Sloane-Stanley
G. H.
(
1957
).
A simple method for the isolation and purification of total lipids from animal tissues
.
J. Biol. Chem.
226
,
497
-
509
.
Fredrickson
L. H.
(
2001
).
Steller’s eider (Polysticta stelleri)
. In
The Birds of North America
(ed.
Poole
A.
,
Gill
F.
),
number 571
.
Philadelphia, PA
:
The Birds of North America Inc.
Gannes
L. Z.
,
O’Brien
D. M.
,
Martinez del Rio
C.
(
1997
).
Stable isotopes in animal ecology: assumptions, caveats and a call for more laboratory experiments
.
Ecology
78
,
1271
-
1276
.
Goedkoop
W.
,
Sonesten
L.
,
Ahlgren
G.
,
Boberg
M.
(
2000
).
Fatty acids in profundal benthic invertebrates and their major food resources in Lake Erken, Sweden: seasonal variation and trophic indications
.
Can. J. Fish Aquat. Sci.
57
,
2267
-
2279
.
Grand
J. B.
,
Franson
J. C.
,
Flint
P. L.
,
Petersen
M. R.
(
2002
).
Concentrations of trace elements in eggs and blood of spectacled and common eiders on the Yukon-Kuskokwim Delta, Alaska, USA
.
Envir. Tox. Chem.
21
,
1673
-
1678
.
Gunstone
F. D.
,
Harwood
J. L.
,
Padley
F. B.
(
1986
).
The Lipid Handbook
.
Cambridge
:
Chapman and Hall
.
Gurr
M. I.
(
1997
).
Lipids and nutrition
. In
Lipid Technologies and Applications
(ed.
Gunstone
F. D.
,
Padley
F. B.
), pp.
79
-
112
.
New York
:
Marcel Dekker
.
Hammer
B. T.
,
Fogel
M. L.
,
Hoering
T. C.
(
1998
).
Stable carbon isotope ratios of fatty acids in seagrass and redhead ducks
.
Chem. Geol.
152
,
29
-
41
.
Hobson
K. A.
(
1995
).
Reconstructing avian diets using stable-carbon and nitrogen isotope analysis of egg components: patterns of isotopic fractionation and turnover
.
Condor
97
,
752
-
762
.
Hobson
K. A.
,
Clark
R. G.
(
1992
).
Assessing avian diets using stable isotopes. II. Factors influencing diet–tissue fractionation
.
Condor
94
,
189
-
197
.
Hobson
K. A.
,
Welch
H. E.
(
1992
).
Determination of trophic relationships within a high Arctic marine food web using δ13C and δ15N analysis
.
Mar. Ecol. Prog. Ser.
84
,
9
-
18
.
Hobson
K. A.
,
Fisk
A.
,
Karnovsky
N.
,
Holst
M.
,
Gagnon
J.-M.
,
Fortier
M.
(
2002
).
A stable isotope (δ13C, δ15N). model for the North Water food web: implications for evaluating trophodynamics and the flow of energy and contaminants
.
Deep Sea Res. Part II
49
,
5131
-
5150
.
Howland
M. R.
,
Corr
L. T.
,
Young
S. M. M.
,
Jones
V.
,
Jim
M. S.
,
Van Der Merwe
N. J.
,
Mitchell
A. D.
,
Evershed
R. P.
(
2003
).
Expression of the dietary isotope signal in the compound-specific δ13C values of pig bone lipids and amino acids
.
Int. J. Osteoarchaeol.
13
,
54
-
65
.
Hussey
N. E.
,
Brush
J.
,
McCarthy
I. D.
,
Fisk
A. T.
(
2010
).
δ15N and δ13C diet–tissue discrimination factors for large sharks under semi-controlled conditions
.
Comp. Biochem. Physiol.
155A
,
445
-
453
.
Iverson
S. J.
,
Field
C.
,
Bowen
W. D.
,
Blanchard
W.
(
2004
).
Quantitative fatty acid signature analysis: a new method of estimating predator diets
.
Ecol. Monogr.
74
,
211
-
235
.
Iverson
S. J.
,
Springer
A. M.
,
Kitaysky
A. S.
(
2007
).
Seabirds as indicators of food web structure and ecosystem variability: qualitative and quantitative diet analyses using fatty acids
.
Mar. Ecol. Prog. Ser.
352
,
235
-
244
.
Joseph
J. D.
(
1982
).
Lipid composition of marine and estuarine invertebrates. Part II: Mollusca
.
Prog. Lipid Res.
21
,
109
-
153
.
Käkelä
A.
,
Crane
J.
,
Votier
S. C.
,
Furness
R. W.
,
Käkelä
R.
(
2006
).
Fatty acid signatures as indicators of diet in great skuas Slercorarius skua, Shetland
.
Mar. Ecol. Prog. Ser.
319
,
297
-
310
.
Käkelä
A.
,
Furness
R. W.
,
Kelly
A.
,
Strandberg
U.
,
Waldron
S.
,
Käkelä
R.
(
2007
).
Fatty acid signatures and stable isotopes as dietary indicators in North Sea seabirds
.
Mar. Ecol. Prog. Ser.
342
,
291
-
301
.
Käkelä
R.
,
Furness
R. W.
,
Kahle
S.
,
Becker
P. H.
,
Käkelä
A.
(
2009
).
Fatty acid signatures in seabird plasma are a complex function of diet composition: a captive feeding trial with herring gulls
.
Funct. Ecol.
23
,
141
-
149
.
Klasing
K. C.
(
1998
).
Comparative Avian Nutrition
.
Wallingford, UK
:
CAB International
.
Lien
T.-F.
,
Chou
R.-C. R.
,
Chen
S.-Y.
,
Jeng
Y.-I.
,
Jan
D.-F.
(
1999
).
Lipid metabolism of Tsaiya ducks: plasma and liver related traits under ad libitum and fasting
.
J. Sci. Food and Agric.
79
,
1413
-
1416
.
Lien
T.-F.
,
Jan
D.-F.
(
2003
).
Enzyme activities related to lipid metabolism in the liver and adipose tissue of Tsaiya ducks under fasting and ad libitum feeding conditions
.
Asian-Aust. J. Anim. Sci.
16
,
403
-
408
.
McMahon
K. W.
,
Fogel
M. L.
,
Elsdon
T. S.
,
Thorrold
S. R.
(
2010
).
Carbon isotope fractionation of amino acids in fish muscle reflects biosynthesis and isotopic routing from dietary protein
.
J. Animal Ecol.
79
,
1132
-
1141
.
Monson
K. D.
,
Hayes
J. M.
(
1982
).
Biosynthetic control of the natural abundance of carbon 13 at specific positions within fatty acids in Saccharomyces cerevisiae: isotopic fractionations in lipid synthesis as evidence for peroxisomal regulations
.
J. Biol. Chem.
257
,
5568
-
5575
.
O’Brien
D. M.
,
Boggs
C. L.
,
Fogel
M. L.
(
2005
).
The amino acids used in reproduction by butterflies: a comparative study of dietary sources using compound specific stable isotope analysis
.
Physiol. Biochem. Zool.
78
,
819
-
827
.
Petersen
M. R.
(
1980
).
Observations of wing-feather moult and summer feeding ecology of Steller’s eiders at Nelson Lagoon, Alaska
.
Wildfowl
31
,
99
-
106
.
Petersen
M. R.
(
1981
).
Populations, feeding ecology and molt of Steller’s eiders
.
Condor
83
,
256
-
262
.
Petersen
M. R.
,
Piatt
J. F.
,
Trust
K. A.
(
1998
).
Foods of spectacled eiders Somateria fischeri in the Bering Sea, Alaska
.
Wildfowl
49
,
124
-
128
.
Petersen
M. R.
,
Grand
J. B.
,
Dau
C. P.
(
2000
).
Spectacled eider (Somateria fischeri)
. In
The Birds of North America
(ed.
Poole
A.
,
Gill
F.
),
number 547
.
Philadelphia, PA
:
The Birds of North America Inc.
Post
D. M.
,
Layman
C. A.
,
Arrington
D. A.
,
Takimoto
G.
,
Quattrochi
J.
,
Montana
C. G.
(
2007
).
Getting to the fat of the matter: models, methods and assumptions for dealing with lipids in stable isotope analyses
.
Oecologia
152
,
179
-
189
.
Price
E. R.
(
2010
).
Dietary lipid composition and avian migratory flight performance: Development of a theoretical framework for avian fat storage
.
Comp. Biochem. Physiol. A
157
,
297
-
309
.
Price
E. R.
,
Krokfors
A.
,
Guglielmo
C. G.
(
2008
).
Selective mobilization of fatty acids from adipose tissue in migratory birds
.
J. Exp. Biol.
211
,
29
-
34
.
Rojek
N.
(
2008
).
Breeding Biology of Steller’s Eiders Nesting Near Barrow, Alaska, 2007
.
Technical Report
.
Fairbanks, AK
:
US Fish and Wildlife Service
.
Ruess
L.
,
Tiunov
A.
,
Haubert
D.
,
Richnow
H. H.
,
Häggblom
M. M.
,
Scheu
S.
(
2005
).
Carbon stable isotope fractionation and trophic transfer of fatty acids in fungal based soil food chains
.
Soil Biol. Biochem.
37
,
945
-
953
.
Schmidt
K.
,
Atkinson
A.
,
Stübing
D.
,
McClelland
J. W.
,
Montoya
J. P.
,
Voss
M.
(
2003
).
Trophic relationships among Southern Ocean copepods and krill: some uses and limitations of a stable isotope approach
.
Limnol. Oceanogr.
48
,
277
-
289
.
Sénéchal
E.
,
Bêty
J.
,
Gilchrist
H. G.
,
Hobson
K. A.
,
Jamieson
S. E.
(
2011
).
Do purely capital layers exist among flying birds? Evidence of exogenous contribution to arctic-nesting common eider eggs
.
Oecologia
165
,
593
-
604
.
Siguel
E. N.
,
Maclure
M.
(
1987
).
Relative activity of unsaturated fatty acid metabolic pathways in humans
.
Metabolism
36
,
664
-
669
.
Smith
S. B.
,
McWilliams
S. R.
,
Guglielmo
C. G.
(
2007
).
Effect of diet composition on plasma metabolite profiles in a migratory songbird
.
Condor
109
,
48
-
58
.
Stevens
L.
(
1996
).
Avian Biochemistry and Molecular Biology
.
Cambridge
:
Cambridge University Press
.
Stott
A. W.
,
Davies
E.
,
Evershed
R. P.
(
1997
).
Monitoring the routing of dietary and biosynthesised lipids through compound-specific stable isotope (δ13C). measurements at natural abundance
.
Naturwissenschaften
84
,
82
-
86
.
Sushchik
N. N.
,
Gladyshev
M. I.
,
Moskvichova
A. V.
,
Makhutova
O. N.
,
Kalachova
G. S.
(
2003
).
Comparison of fatty acid composition in major lipid classes of the dominant benthic invertebrates of the Yenisei river
.
Comp. Biochem. Physiol.
134B
,
111
-
122
.
Thiemann
G. W.
,
Iverson
S. J.
,
Stirling
I.
(
2007
).
Variability in the blubber fatty acid composition of ringed seals (Phoca hispida). across the Canadian Arctic
.
Mar. Mamm. Sci.
23
,
241
-
261
.
Tocher
D. R.
(
2003
).
Metabolism and functions of lipids and fatty acids in teleost fish
.
Rev. Fish. Sci.
11
,
107
-
184
.
Turchini
G. M.
,
Torstensen
B. E.
,
Ng
W.-K.
(
2009
).
Fish oil replacement in finfish nutrition
.
Rev. Aquacult.
1
,
10
-
57
.
US Fish and Wildlife Service
(
1996
).
Spectacled Eider Recovery Plan
.
Anchorage, AK
:
US Fish and Wildlife Service
.
US Fish and Wildlife Service
(
2002
).
Steller’s Eider Recovery Plan
.
Fairbanks, AK
:
US Fish and Wildlife Service
.
Wang
S. W.
,
Iverson
S. J.
,
Springer
A. M.
,
Hatch
S. A.
(
2007
).
Fatty acid signatures of stomach oil and adipose tissue of northern fulmars (Fulmarus glacialis). in Alaska: implications for diet analysis of procellariiform birds
.
J. Comp. Physiol. B
177
,
893
-
903
.
Wang
S. W.
,
Hollmén
T. E.
,
Iverson
S. J.
(
2010
).
Validating quantitative fatty acid signature analysis to estimate diets of spectacled and Steller’s eiders (Somateria fischeri and Polysticta stelleri)
.
J. Comp. Physiol. B
180
,
125
-
139
.
Ward
E. J.
,
Semmens
B. X.
,
Schindler
D. E.
(
2010
).
Including source uncertainty and prior information in the analysis of stable isotope mixing models
.
Environ. Sci. Technol.
44
,
4645
-
4650
.
Wessels
F. J.
,
Hahn
D. A.
(
2010
).
Carbon 13 discrimination during lipid biosynthesis varies with dietary concentration of stable isotopes: implications for stable isotope analyses
.
Funct. Ecol.
24
,
1017
-
1022
.
Williams
C. T.
,
Iverson
S. J.
,
Buck
C. L.
(
2008
).
Stable isotopes and fatty acid signatures reveal age- and stage-dependent foraging niches in tufted puffin
.
Mar. Ecol. Prog. Ser.
363
,
287
-
298
.
Wolf
N.
,
Carleton
S. A.
,
Martínez del Rio
C.
(
2009
).
Ten years of experimental animal isotopic ecology
.
Funct. Ecol.
23
,
17
-
26
.