Abstract
Rationale
The sampling of sequential, annually formed bone growth layers for stable carbon (δ13C values) and nitrogen (δ15N values) isotope analysis (SIA) can provide a time series of foraging ecology data. To date, no standard protocol exists for the pre-SIA treatment of cortical samples taken from fresh, modern, bones.
Methods
Based on the SIA of historical bone, it is assumed that fresh bone samples must be pre-treated with acid prior to SIA. Using an elemental analyzer coupled to an isotope ratio mass spectrometer to measure stable carbon and nitrogen ratios, we tested the need to acidify cortical bone powder with 0.25M HCl prior to SIA to isolate bone collagen for the determination of δ13C and δ15N values. We also examined the need for lipid extraction to remove potential biases related to δ13C analysis, based on a C:N ratio threshold of 3.5.
Results
It was found that acidification of micromilled cortical bone samples from marine turtles does not affect their δ15N values, and the small effect acidification has on δ13C values can be mathematically corrected for, thus eliminating the need for pre-SIA acidification of cortical bone. The lipid content of the cortical bone samples was low, as measured by their C:N ratios, indicating that lipid extracting cortical bone samples from modern marine turtles is unnecessary.
Conclusions
We present a standard protocol for testing fresh, modern cortical bone samples prior to SIA, facilitating direct comparison of future studies. Based on the results obtained from marine turtle bones, pre-acidification and lipid removal of cortical bone are not recommended. This is especially useful as there is frequently not enough bone material removed via micromilling of sequential growth layers to accommodate both acid treatment and SIA.
Keywords: stable isotope analysis, collagen, acidification, protocol, marine turtles
Introduction
Stable carbon (δ13C values) and nitrogen (δ15N values) isotope analysis (SIA) of animal tissues is used in ecology to estimate the diets and movement patterns of multiple taxa (e.g. Hobson et al.,[1] Newsome et al. [2]). The δ15N values from animal tissues and other organic materials provide insight into trophic relationships, as they predictably increase with increasing trophic level.[3–6] Both δ15N and δ13C values can be used to estimate animal movement patterns as these values reflect the underlying nitrogen and carbon cycling processes that can be indicative of specific terrestrial or marine regions.[7–10] Findings from ecogeochemistry studies have addressed key ecological and life history questions critical to population conservation and management of multiple endangered and otherwise important species (e.g. Steller sea lions[11], gray wolves[12], humpback whales[13], yellowfin tuna[14], leatherback turtles[15], African elephants[16], and aquatic salamanders[17]).
Stable isotope analysis of multiple tissues from the same animal allows for the reconstruction of foraging and movement patterns at different time scales, as protein, and therefore isotopic, turnover varies depending upon the tissue sampled.[18–23] The hard, compact bone of the humerus, also called cortical bone, is formed during periosteal deposition and remains metabolically inert. As the humerus grows, outer compact layers are formed while the inner medullary cavity expands, resulting in the formation of new cortical bone and the resorption of some inner cortical layers. Once formed, cortical bone, a relatively inert tissue, does not have regular cellular turnover so SIA of cortical bone samples reflect an animal's diet during the time period from when that bone layer was produced. Sampling of an animal's whole bone can provide an integration of stable isotopes from multiple years, if not its entire lifetime. Alternatively, the inert layers of some structures such as teeth, or bones such as the humerus, are often formed sequentially, with each layer representing a different period of the animal's growth. Targeted sampling of these sequential inert layers allows SIA to provide a time series of isotopic data, reconstructing an animal's foraging ecology over time. [24–26]
Bone consists of two distinct components, collagen and bioapatite. Approximately 1/3 of bone by weight is collagen (∼45% nitrogen and ∼20% carbon, by collagen weight). Collagen is an organic matrix that makes up the protein component of bone and is assimilated from the carbon and nitrogen contained in the protein constituents of a consumer's diet.[27] The remaining 2/3 of bone by weight is composed of bioapatite (Ca10(PO4)OH2). An inorganic mineral, bioapatite can be ∼3% carbon (typical range 2-7%) by weight when carbonate (CO32-) substitutes for the phosphate (PO43-) or hydroxyl (OH-) group.[28–31] Bioapatite-based carbon is synthesized from a consumer's whole diet, which includes protein, carbohydrates, and lipids.[32,33] These two different bone components, collagen and bioapatite, have distinctive biosynthetic pathways. As a result, collagen and bioapatite experience differential isotopic fractionation and routing of dietary components during the biosynthesis of the bone tissue, and, when analyzed for their δ13C and δ15N values, reflect different portions of a consumer's diet.[27,34–37] For the best interpretation of an animal's foraging ecology from the stable carbon and nitrogen isotope ratios of bone, collagen is generally isolated from whole bone and targeted for SIA.[27,38] This allows for simultaneous sampling of carbon and nitrogen, while also avoiding the confusion of interpreting stable isotope ratio values from carbon bioapatite that are an amalgamation of stable carbon isotopes from multiple dietary components.[27,39–41]
For trophic studies utilizing SIA, collagen is typically isolated from whole bone with hydrochloric acid, and further processing beyond acidification is required for studies using whole bones and historical samples, to remove lipids, contaminants, and non-collagen protein remnants. [2,3, 27,38,42,43] However, these treatments require large amounts of sample, much more than can be removed from an individual annual growth layer, and they subject bone tissue to extensive chemical processing that could affect stable isotope (SI) values, especially in fresh, modern samples, where contamination and digenesis are not expected. Medieros et al. [44] recently tested the effect of lipid extraction on whole cross sections of marine turtle bone, which included the vascularized, lipid rich, central portion of bone where bone resorption and exchange of molecules with the blood occur. Our analyses are the first that we know of that focus solely on the need for acidification and lipid extraction on compact cortical bone. Our focus on cortical bone was for two reasons: 1) only the compact cortical bone contains the growth layers that allow for reconstruction of the sequential years of an animal's foraging ecology using SIA; and 2) the vascularized portion of bone, the medullary cavity, is different from cortical bone in its cellular structure and function, and therefore should be treated as a different type of bone tissue to avoid misinterpretation of bone SI values. [45] We developed standardized protocols to test for the effects of pre-SIA treatments on the SI values from bone growth layers to: 1) identify a simplified method to process cortical bone samples of modern, freshly collected bone, in order to obtain accurate, protein-based δ13C and δ15N values and 2) estimate potential SI correction factors that can be used when limited amounts of bone material prevent pre-SIA treatment. Our simplified and standardized protocol can be applied to test any vertebrate bone with growth layers, will facilitate more efficient bone SIA studies, and will enable more direct comparison of results among future studies. Specifically, we tested the effectiveness of a simplified acidification method to isolate collagen from whole cortical bone by comparing the δ13C and δ15N values, and the percentage carbon (%C), and percentage nitrogen (%N) between treated (collagen) and untreated (whole bone) samples. We also assessed the need to lipid extract cortical bone samples. While tested specifically on marine turtle bones, these techniques may be applied to assess the need to treat, and define corrections for, other vertebrate bones.
Methods
Marine turtle bone samples
We conducted experimental trials on cross sections of marine turtle humerus bones obtained following skeletochronology processes [46,47] [48] to test for the need for lipid extraction and the effects of demineralizing acidification treatment on the accurate measurement of the δ13C and δ15N values from bone material. We also developed methods to best sample sequential growth layers for SIA from humerus bone cross sections collected from marine turtles and those data are presented elsewhere (Tomaszewicz et al., in review[26]). Humerus bones were collected from dead-stranded east Pacific green sea turtles (Chelonia mydas) (n = 15), North Pacific loggerhead sea turtles (Caretta caretta) (n = 15), and Northwest Atlantic loggerhead turtles (n = 20). Samples collected from the Pacific were from juvenile and sub-adult turtles of similar size at stranding (between 53 and 73 cm curved carapace length, CCL), whereas the Atlantic turtles were of similar size at stranding, but ranged from sub-adult to adult sizes (between 70 and 96 cm CCL). For Atlantic turtles, we converted any straight carapace length (SCL) measurements to curved carapace length (CCL) based on the SCL:CCL relationship presented in Snover et al.[24] (CCL = (SCL – 0.189) / 0.923, R2 = 0.966). All Pacific turtles stranded between 2004 and 2011 at a 45-km stretch of beach, Playa San Lázaro, in Baja California Sur, Mexico, and the Atlantic turtles stranded between 1997 and 2011, primarily at beaches in North Carolina and Virginia, with three samples from Maryland and New Jersey.
Acidification of bone samples
We compared untreated bone samples with those that were treated with acid before SIA to isolate collagen by removing carbonate. For this study, we modified a method recommended by Chisholm et al.[42] and used in Godley et al.,[49] which uses hydrochloric acid (HCl), a weak acid, to isolate collagen. This method is similar to the preparation applied to the sampling of modern marine mammal teeth,[25] marine mammal cranial bone,[50] and chitonous and keratinized marine invertebrate tissues.[51–53] This method is notably simplified from the more complex protocols designed to prepare ancient and prehistoric bones for SIA which typically include steps for lipid extraction and the removal of decayed organic matter with sodium hydroxide. [3,36,41]
To test the effect of pre-SIA acidification on bone, we created two, paired treatment groups (n = 50) from milled bone dust: 1) untreated bone, and 2) bone treated with a weak HCl solution (Table 1). We cut the humerus bones to obtain 3mm cross sections where the bone is most dense, just below the insertion scar,[45] using an Isomet slow speed saw (Buehler, Lake Bluff, IL, USA) fitted with a diamond wafering blade (Buehler) (Fig. 1a). A diamond studded dremel tool (Black and Decker RTX-3, New Britain, CT, USA) was used to mill ∼15 mg of powdered bone material from cross sections (Fig. 1). We took care to avoid the outermost edge of the bone and the inner vascularized portion of the bone, the medullary cavity, to prevent contamination, and sampled only the central portion of the cortical bone. We homogenized this powdered sample, and weighed and loaded 1.5 mg of untreated powder into a tin capsule for SIA. Of the remaining powder, 10 mg was placed into a 2-mL plastic, flat-bottomed vial for acidification.
Table 1. Experiment set up and design.
Number of samples used for each experimental trial. Sample size is the number of sample pairs compared, and the number of samples with ×3 replicates used to assess within sample variation.
| Micromilled powder | |||
|---|---|---|---|
|
| |||
| Origin | Species | Turtle Sample size | Samples with ×3 Replicates |
| Pacific | Chelonia mydas | 15 | 5 |
| Caretta caretta | 15 | 5 | |
| Atlantic | Caretta caretta | 20 | 20 |
|
| |||
| Total sample size | 50 | 30 | |
Figure 1.

Green sea turtle (Chelonia mydas) humerus cross section, showing sampling location.
We added 0.5 mL of 0.25M HCl to the bone powder in the vial and stirred the contents with a flat spatula. Small amounts of CO2 bubbles formed as the acid reacted with the inorganic carbon, and we stirred the acidic solution intermittently for 30 minutes at room temperature, then refrigerated it for 1-2 hours. To ensure that the reaction was complete, the samples were stirred and, if no bubbles were observed, we centrifuged the contents for 2 minutes (5000 rpm, 2040 RCF Brinkmann Eppendorf Centrifuge 5415C, Hamburg, Germany). We pipetted off the HCl solution. The presence of a pale yellow to white precipitate was noted as an indication of pure collagen.[54] Precipitates with a brown coloration were also noted, as this could indicate possible contamination, impure collagen, or high lipid content.[54] The samples were rinsed with ultra-pure water three times by adding 0.5 mL of water, centrifuging the contents for 5 minutes (5000 rpm, 2040 RCF), then pipetting off the excess water. Following the third water rinse and centrifugation, we pipetted off only 0.25 mL of water, and the remaining water-collagen solution was mixed. We transferred this solution with a disposable plastic pipette directly into a pre-weighed tin capsule positioned in a 96-well plate. The samples were oven-dried at ∼50°C for 48 hours, then weighed and folded for SIA. The target sample weight was 0.6 mg for collagen. We analyzed three replicates each of 30 samples (10 Pacific, 20 Atlantic) to assess within-sample variation. The final analysis used single trial values, as no within-sample variation was observed (Fig. S1 and Table S1, Supplementary Material). Paired samples (untreated and acidified) were then directly compared to assess the effects of acidification on the δ13C and δ15N values (Tables 1 and 2, and Table S2, Supplementary Material).
Table 2. Acidification experiment effect.
Results of effect (difference) for both δ13C and δ15N values in permil (‰) units, from bone powder acidification experiment. The individual and mean (± SD) differences (e.g. δ15Nuntreated bone - δ15Ntreated bone and similar for δ13C) in stable isotope values (‰) between acidified (treated) and non-acidified (untreated) bone powder from marine turtles, separated by ocean basin, Pacific and Atlantic. Turtle species are denoted as “Cm” for Chelonia mydas, green turtles, and “Cc” for Caretta caretta, loggerhead turtles.
| Bone ID | Species | Effect on δ13C (δ13C untreated bone - δ13C treated bone) | Effect on δ15N (δ15N untreated bone - δ15N treated bone) | CCL (cm) | Stranding Year |
|---|---|---|---|---|---|
|
| |||||
| Pacific | |||||
| F | Cc | -0.16 | 0.78 | 53 | 2011 |
| G | Cc | -0.49 | -0.13 | 59 | 2009 |
| H | Cc | -0.36 | 0.66 | 73 | 2008 |
| I | Cc | -0.35 | 0.35 | 65 | 2009 |
| J | Cc | -0.34 | 0.06 | 69 | 2008 |
| K | Cc | -1.37 | -0.18 | 57 | 2008 |
| L | Cc | -0.55 | -0.38 | 53 | 2010 |
| M | Cc | -0.13 | -0.13 | 56 | 2011 |
| N | Cc | -1.43 | -0.47 | 64 | 2007 |
| O | Cc | -1.53 | 0.28 | 51 | 2009 |
| P | Cc | -0.62 | -0.21 | 58 | 2009 |
| Q | Cc | -0.63 | 0.17 | 63 | 2009 |
| R | Cc | -0.35 | 0.13 | 69 | 2008 |
| S | Cc | -0.75 | -0.21 | 72 | 2008 |
| T | Cc | -0.53 | -0.31 | 72 | 2008 |
| A | Cm | -0.09 | 0.22 | 53 | 2011 |
| B | Cm | -0.30 | 0.69 | 56 | 2011 |
| C | Cm | -0.26 | 0.56 | 73 | 2011 |
| D | Cm | -0.08 | -0.42 | 60 | 2009 |
| E | Cm | -0.04 | 0.33 | 64 | 2010 |
| U | Cm | -1.22 | -0.56 | 55 | 2010 |
| V | Cm | -0.91 | -0.43 | 54 | 2011 |
| W | Cm | -0.50 | -0.56 | 65 | 2011 |
| X | Cm | -0.67 | -0.42 | 61 | 2011 |
| Y | Cm | -0.61 | 0.39 | 53 | 2011 |
| Z | Cm | -0.49 | -0.16 | 62 | 2011 |
| AA | Cm | -0.47 | -0.10 | 59 | 2011 |
| BB | Cm | -0.51 | 0.27 | 62 | 2004 |
| CC | Cm | -0.37 | 0.06 | 52 | 2011 |
| DD | Cm | -0.83 | 0.10 | 62 | 2011 |
|
| |||||
| AVERAGE: | -0.56 | 0.01 | 60.83 | ||
| SD: | 0.39 | 0.38 | 6.75 | ||
|
| |||||
| Atlantic | |||||
| A | Cc | -0.84 | -0.05 | 90 | 2007 |
| B | Cc | -0.83 | 0.06 | 96 | 2008 |
| C | Cc | -1.17 | 0.07 | 91 | 2004 |
| D | Cc | -0.70 | 0.02 | 86 | 2005 |
| E | Cc | -0.60 | 0.17 | 94 | 2005 |
| F | Cc | -0.87 | 0.11 | 84 | 2005 |
| G | Cc | -0.66 | -0.28 | 87 | 2007 |
| H | Cc | -1.18 | -0.01 | 66 | 1997 |
| I | Cc | -0.84 | -0.05 | 94 | 2010 |
| J | Cc | -0.87 | 0.13 | 72 | 1998 |
| K | Cc | -0.72 | 0.10 | 92 | 2007 |
| L | Cc | -0.75 | 0.11 | 94 | 2003 |
| M | Cc | -1.07 | -0.11 | 70 | 2003 |
| N | Cc | -1.11 | 0.09 | 88 | 2007 |
| O | Cc | -1.07 | -0.29 | 85 | 1999 |
| P | Cc | -0.61 | 0.10 | 89 | 2010 |
| Q | Cc | -0.70 | -0.15 | 66 | 1997 |
| R | Cc | -0.90 | -0.21 | 78 | 1998 |
| S | Cc | -0.64 | 0.23 | 73 | 1997 |
| T | Cc | -0.59 | 0.16 | 93 | 2011 |
|
| |||||
| AVERAGE: | -0.84 | 0.01 | 84.46 | ||
| SD: | 0.19 | 0.15 | 10.00 | ||
Stable isotope analysis
All the samples were analyzed for their δ13C and δ15N values, percentage carbon (%C), and percentage nitrogen (%N). The Pacific samples were analyzed by combustion in a Carlo Erba NA 1500 CNS elemental analyzer (Thermo Scientific, Milan, Italy) interfaced via a ConFlo II device (ThermoFinnigan, Bremen, Germany) to a Thermo Electron DeltaV Advantage isotope ratio mass spectrometer (Thermo Scientific, Bremen, Germany) in the Stable Isotope Geochemistry Lab at the University of Florida, Gainesville (Gainesville, FL, USA). Atlantic samples were similarly analyzed using a Carlo Erba NA 1500 CNS elemental analyzer interfaced with a DeltaPlusXL continuous-flow isotope ratio mass spectrometer (ThermoFinnigan) at the College of Earth, Ocean, and Atmospheric Sciences Stable Isotope Lab at Oregon State University, Corvallis (Corvallis, OR, USA). A conventional delta (δ) notation in parts per thousand or permil (‰), was used to express the stable isotope ratios of the samples relative to the isotope standards:
where the corresponding ratios of heavy to light isotopes (13C/12]C and 15N/14]N) in the sample and standard are represented by Rsample and Rstandard, respectively. The standard for δ13C values was Vienna Pee Dee Belemnite and for δ15N values was atmospheric N2. Laboratory reference materials, USGS40 (L-glutamic acid, δ15N = -4.52‰, δ13C = -26.39‰, supplied by the U.S. Geological Survey, Reston, VA, USA)) for Pacific samples, and caffeine (IAEA-600, δ15N = +1.0‰, δ13C = -27.77‰, supplied by the International Atomic Energy Agency, Vienna, Austria) for Atlantic samples, were calibrated at regular intervals against the standards. The precision for these data was determined using the standard deviations around the means for a subset of the internal laboratory standards run at set intervals. The standard deviation of the USGS40 data was 0.05 ‰ for δ13C values and 0.08 ‰ for δ15N values, and the standard deviation for the IAEA-600 data was 0.06 ‰ for δ13C values and 0.07 ‰ for δ15N values. The %C and %N were used to calculate C:N ratios (%C divided by %N) as well as to assess protein purity and material composition for the micromilled bone powder, based on established characteristic values.
Statistical analysis
We applied a two-sample, paired t-test on the stable isotope values from bone powder samples that were not treated (control) vs those that were treated with acid to evaluate the effects of acidification on the δ13C and δ15N values of milled bone powder samples. Similarly, a non-paired t-test compared the effects of acidification between samples from the two different ocean basins (Pacific vs Atlantic), and between different turtle species (green turtle vs loggerhead) in the Pacific. We applied a linear mixed-effects model with individual turtle as a random effect to examine variation attributed to treatment group and ocean basin of origin for the turtles (Pacific vs. Atlantic). All the bone powder samples had C:N ratios of 3.5 or less. Therefore, in keeping with recommendations by Post[55] that samples from aquatic consumers with C:N ratios of 3.5 or less do not require lipid extraction, we included all samples in our analysis, resulting in a final paired sample size of n = 50 (Table 1). Finally, acidified milled bone powder samples from a total of 30 turtles (10 Pacific, 20 Atlantic) were run in triplicate to test for variation within the acidification treatment. The standard deviations between these triplicate samples were used to assess variation. We used the software program R for all analyses[56] and significance was tested at the α = 0.05 level.
Results
Effect of Acidification
The acidification process was effective in isolating collagen from whole bone. The %C and %N from the acidified samples in this study were near those characterizing collagen (mean ± SD, %C: 43.01 ± 6.0 and %N: 14.26 ± 2.7; Fig. S1 and Table S1, Supplementary Material). Whole bone, which is ∼1/3 collagen and ∼2/3 hydroxyapatite, is ∼15% carbon and ∼5% nitrogen and collagen is ∼45% carbon and ∼15% nitrogen by weight.[38] The C:N ratio of pure, unaltered protein, including collagen, ranges between 2.9 and 3.6,[38,54,57,58] and, while some of the untreated and acidified bone samples in the present study had C:N ratios less than 2.9, none were above 3.5 (Fig. S2 and Table S1, Supplementary Material).
For the 30 bones that had acidified milled bone powder samples compared in triplicate, the overall sample replicate variation for the δ13C and δ15N values was very low (mean SD: ± 0.08‰ and ± 0.07‰, respectively). This observed variation was well below the measured precision for all stable isotope samples (<0.24‰ for both δ13C and δ15N; Fig. S1 and Table S1, Supplementary Material). Therefore, we randomly chose one each of the δ13C and δ15N values from the replicate samples for use in the analyses.
When samples from both species collected from the two ocean basins were analyzed together (n = 50 pairs), the δ13C values were significantly different (paired t-test, t = -13.5, df = 49, p<0.01) between acidified and untreated bone powder (mean ± SD: -0.67 ± 0.35‰; Table S2, Supplementary Material). When examined by species, we found that the δ13C values from acidified bone samples from green and loggerhead turtles collected in the Pacific were less than those from the untreated samples by 0.49 ± 0.33‰ and 0.65 ± 0.46‰, respectively. These species-specific differences were not significantly different from one another (unpaired t-test, t = -1.03, df = 25.7, p = 0.31), indicating that there was no species-specific effect of acidification on the bone δ13C values from these two species. A basin-scale effect of acidification was detected, however. The δ13C values from acidified Pacific samples (n = 30) and Atlantic samples (n = 20) were less than those from the untreated samples by -0.56 ± 0.39 ‰, and -0.84 ± 0.19 ‰, respectively, and these values were significantly different (unpaired t-test, t = 3.2, df = 44.9, p <0.01). This suggests the potential for a differential effect of acidification depending on the location and/or size of the turtles. The Atlantic turtles in this study were larger (70-96 cm CCL vs 53-75cm CCL for Pacific turtles; unpaired t-test, t = -9.29, df = 30.6, p < 0.01) and had higher average δ13C values than the Pacific turtles (untreated means δ13C: Atlantic -14.3 ± 0.63 ‰ vs Pacific -16.0 ± 0.89 ‰; treated mean values δ13C: Atlantic -15.1 ± 0.70 ‰ vs Pacific -16.6 ± 1.10 ‰; Table S2, Supplementary Material). The observed effects of acidification on all sample groups are three to four times greater than the maximum measured precision associated with the SIA processing (max. 0.24‰; Fig. 2a) and therefore may be biologically significant.
Figure 2.

Effect of acidification treatment on micromilled bone powder on stable isotope a) δ13C, and b) δ15N values.
The effect of acidification treatment on δ13C values for all bone samples was consistent within ocean basins. The δ13C values from the treated and untreated Pacific samples were positively related to one another and were well described by a simple linear model (Fig. 2a; treated Pacific bone samples = 1.2 × untreated bone samples + 2.1; F1,28 = 230.4, p < 0.01, adj. R2 = 0.89), as were those from the Atlantic samples (Fig. 2a; treated Atlantic bone samples = 1.1 × untreated bone samples + 0.2; F1,18 = 232, p < 0.01, adj. R2 = 0.92).
There were no differences in the acidification effects on δ15N for the bone powder from the two species of Pacific turtles analyzed (t-test, t = 0.21, df = 27.7, p = 0.84) or for turtles collected between the Pacific and Atlantic oceans (t-test, t = 0.04, df = 40.6, p = 0.97). As a result, all samples were analyzed together (n = 50) and the δ15N values (mean ± SD) were not significantly different for the acidified (15.03 ± 2.03‰) vs the untreated (15.02 ± 2.05‰) samples, (paired t-test, t = -0.27, df = 49, p = 0.79; Table S2, Supplementary Material).
As expected, there was a significant effect of acidification treatment on δ13C values (p < 0.01), but no effect of acidification treatment on δ15N values (p = 0.97) when we applied the linear mixed-effect model (Table 3). There was a significant effect of ocean basin on both δ13C and δ15N values (p < 0.01 for both), but the linear mixed-effects model showed no interaction effect of ocean basin and treatment for either δ13C or δ15N values (p = 0.32 and 0.99, respectively; Table 3).
Table 3. Linear mixed effects models results.
Results from linear mixed effects models. Test effect of ocean basin and acidification treatment on micromilled bone powder (Model: lme(δ13C∼Ocean*trt, random=∼1|Bone_ID. Similar model applied for δ15N).
| Micromilled bone powder | ||||||
|---|---|---|---|---|---|---|
| CARBON | ||||||
| Value | Std. Error | DF1 | F-value2 | p-value3 | ||
| (Intercept) | -15.10 | 0.19 | 67 | 13894.82 | <.0001 | |
| Ocean Basin | -1.49 | 0.20 | 67 | 127.75 | <.0001 | |
| Treatment (Acidification) | 0.84 | 0.21 | 67 | 25.71 | <.0001 | |
| Interaction | -0.27 | 0.27 | 67 | 1.00 | 0.32 | |
| NITROGEN | ||||||
| (Intercept) | 13.62 | 0.38 | 67 | 3817.38 | <.0001 | |
| Ocean Basin | 2.32 | 0.41 | 67 | 61.73 | <.0001 | |
| Treatment (Acidification) | -0.01 | 0.43 | 67 | 0.00 | 0.97 | |
| Interaction | 0.00 | 0.56 | 67 | 0.00 | 1.00 | |
DF = degrees of freedom
F-value = F statistic from the linear mixed effects model
p-value = significant at < 0.05
Discussion
Stable isotope analysis
Effects of acidification on the δ13C and δ15N values
Acidification had a minimal effect on the δ13C values, reducing Pacific and Atlantic samples by <1‰ (average ± SD 0.56 ± 0.39 ‰, and 0.84 ± 0.19 ‰, respectively). This effect of acid treatment on the bone powder samples was modeled by a simple linear regression equation, each with high adjusted R2 values (Fig. 3a).
In situations where a difference of ∼1‰ in δ13C values may be biologically significant, application of the effect size as a constant offset (Pacific: -0.56 ‰; Atlantic -0.84 ‰) or the use of the equation (treated Pacific bone samples = 1.2 × untreated bone samples + 2.1; treated Atlantic bone samples = 1.1 × untreated bone samples + 0.2) will allow for the correction of the effect of acidification on the δ13C values from untreated bone powder of modern turtle bones. This allows for comparisons of acid-treated bone samples that are representative of pure collagen and non-treated bone powder samples that are a mix of collagen and apatite. In addition, these correction options facilitate a simpler, quicker, and less costly analysis of bone powder samples, the need to acidify each sample to remove bioapatite-bound carbonate is eliminated.
To ensure that lipids were not affecting the δ13C values from our bone samples, we used only samples with C:N ratios < 3.5,[55] which included all samples in this study. Medeiros et al.[44] found an effect of lipid extraction on the δ13C values from whole bone, but no effect on the bone δ15N values. It should be noted that he primary difference between this and the current study is that fundamentally different tissues are being tested: whole bone in Medeiros et al.[44] vs cortical bone in the present study. Whole humerus cross sections include the central, vascularized, lipid-rich section of bone, whereas cortical bone is limited to bone powder extracted from outer growth layers. As a result, these two studies are not directly comparable.
Acidification did not affect the δ15N values from the milled bone powder in the current study. This was expected because HCl should only react with bioapatite carbon, not with collagen-bound nitrogen. Therefore, the simplified acidification method, or no acidification treatment, are viable options for pre-SIA treatment of bone when performing stable nitrogen isotope analysis of bone powder.
Mechanisms affecting δ13C values
As expected with the isolation of collagen, the δ13C values were lower when acidification eliminated the 13C-enriched carbonate. The cause for this observed reduction in δ13C values with acidification is caused by two factors: 1) the difference in the discrimination factors for the two bone components, collagen and bioapatite (see below), and 2) variation in the bioapatite content, and therefore the bioapatite-bound carbonate content, of cortical bone from marine turtles.
Consumer δ13C values are generally higher than those from prey and the resulting difference is called a discrimination factor.[54,59] The carbon isotope discrimination factors are not known for either bioapatite or collagen from marine turtles, but these discrimination factors for other taxa (primarily mammals and birds) range from ∼9 to ∼14 ‰ and from ∼3 to ∼6 ‰, respectively, and are significantly larger than the commonly assumed 1‰ increase in δ13C values.[27,34,36,37,60] As a result, the δ13C values from collagen and bioapatite from the same individual would probably differ from one another by ∼3 to 11‰. Yet in the present study, the difference between δ13C values of collagen (acid treated bone) and whole (untreated) bone, was very small difference (< 1‰) for both Pacific and Atlantic samples. If the bioapatite content, and therefore carbonate content, of our marine turtle bones were significant, then, given that bones are ∼ 2/3 bioapatite by weight and the difference expected in the δ13C values from collagen and bioapatite could be ∼3 to 11‰, one would expect the difference in the δ13C values between these two bone components to be greater than the mean -0.67 ± 0.35‰ difference found in our study. Given this mean effect of less than 1‰, our results suggest that cortical bone from modern marine turtles contains very little bioapatite-bound carbonate. What small amount of bioapatite-bound carbonate is present, however, could account for the small difference in 13C content between treated and untreated samples.
Carbonate content is the other key factor controlling whether or not the δ13C values from bioapatite will contribute significantly to the δ13C values from whole tissues.[52,61] Bone carbonate content varies, but averages ∼3% by weight.[27–31] Recent studies using tissues with calcium-bound carbonate, but not specifically bone, have proposed using carbonate content, either measured directly or estimated by a “carbonate proxy”, to determine whether or not samples should be acidified prior to SIA.[52,53] There is agreement that tissues with low (3-9%) carbonate content (<5% in Serrano et al.,[53] <3-8% in Jacob et al.,[52] <9% in Mateo et al.[62]) do not warrant acidification treatment, as the effect of inorganic (i.e. bioapatite) 13C would be insignificant and acidification treatments could unintentionally alter the δ13C and δ15N values from the tissue being sampled.[52,53,61,63] While these carbonate proxy studies did not test bones specifically, the carbonate content of bones is nonetheless an important factor for understanding how δ13C values from inorganic carbonate might affect the δ13C values of untreated bone samples. The contribution of carbonate to δ13C values for modern marine turtle bones had not been previously tested, and confirmation of low carbonate content, and therefore effects on the δ13C values, was necessary prior to using the bone δ13C values to address ecological and biological questions about marine turtles. We note that measuring the actual carbonate content of cortical bone powder of marine turtles was beyond the scope of this study, and a future study focused on this would be valuable.
Our results suggest that the small differences in the δ13C values between whole bone and collagen observed in this study (< 1‰) are similar to results from other studies on samples with low carbonate content (reviewed in Schlacher and Connolly[63]). Therefore, we recommend that marine turtle cortical bone powder does not need acidification prior to SIA. Moreover, the δ13C values should be corrected mathematically using the presented regression equation for the appropriate ocean basin (Pacific or Atlantic). Because carbonate content and other mechanisms affecting δ13C values vary, the application of the method presented here may be used in future bone SI studies to test subsets of samples in order to asses the need for acidification and/or lipid extraction, as well as determine regionally-specific correction factors for different taxa.
Effect of turtle size, species, and ocean basin on δ13C and δ15N values
There were no differences in the effect of treatment on the δ13C and δ15N values between loggerhead and green turtles in the Pacific. There was a slight difference in the effect of treatment on the δ13C values from turtle bone between ocean basins (Pacific vs. Atlantic), but no difference in the δ15N values. Nutrient cycling and oceanographic characteristic unique to each ocean basin prevent the direct comparison of actual SIA values.[10,64,65] However, we note that there were distinct size differences between the turtles from the two ocean basins with the Atlantic turtles being larger than the Pacific turtles, and the differences observed in the δ13C values from turtles in the Pacific and Atlantic oceans could be related to this size differential. Size is directly related to growth rate in marine turtles and has been shown to affect fractionation and resulting turtle tissue isotope values.[20,66] In addition, differences in diet between turtles in the two regions may affect the metabolic routing and fractionation of stable carbon isotopes and are another possible source of this observed variation.[67,68] Therefore, to test the effect of acidification treatment on the δ13C and δ15N values of modern cortical bone, we focused only on the observed difference between whole bone (untreated) and bone collagen (acidified) that we measured in marine turtle samples in each of the two ocean basins. Further exploration of the mechanism driving the observed difference of the effect of acidification on δ13C values between samples from the two ocean basins was beyond the scope of this study, but warrants further investigation.
Despite potential sources of variation arising from ocean basin, species, or even turtle size, age, or sex, the high adjusted R2 values from the linear models for δ13C values from the Pacific and Atlantic turtle samples (R2 = 0.89, and 0.92, respectively) support applying regionally specific mathematical offsets (constant value or linear equation) to correct the δ13C values from unprocessed bone of marine turtles from the Pacific and Atlantic.
Sampling of bone for SIA and skeletochronology
Recent studies have attempted to combine SIA and skeletochronology on marine turtles (e.g. Snover et al.,[24] Avens et al.[69]), yet the lack of standardized protocols has limited the results. Only δ15N values were measured in Avens et al.[69] due to the uncertainty of the δ13C values that may result when collagen and bioapatite are analyzed together as whole bone. Snover et al.[24] presented δ13C values for whole bone, yet no acid treatment was tested and lipids were extracted using dichloromethane. The standard protocol presented in the current study allows for the reliable use of δ13C values, in addition to δ15N values, through the application of a δ13C correction value or the linear equation, and provides evidence to support eliminating lipid extraction for cortical bone. A standardized method for sequential sampling of annual bone growth layers is presented elsewhere[26] and, when used in conjunction with the recommended SIA processing and corrections in this paper, can produce a time series of SI patterns from individual animals.
Recommendations
The stable nitrogen isotope value of untreated whole bone reflects the δ15N value of the dietary protein consumed at the time of bone synthesis, whereas the δ13C value of untreated whole bone is slightly higher than that of the dietary protein alone due to the presence of small amounts of 13C-enriched bioapatite-bound carbonate. Despite the small effect (< 1‰) on δ13C values, we present linear regression equations to mathematically correct for the δ13C values from untreated bone samples from marine turtles collected in the Pacific and the Atlantic oceans. Future studies on other vertebrates should employ these techniques to test a subset of samples to 1) determine if lipid extraction is necessary, and 2) determine species- and location-specific correction regression equations. This is important for future studies, especially those utilizing samples from sequential growth layers where the amount of sample available is limited. To ensure that δ13C values are not lower than expected due to the presence of lipid-bound carbon, we recommend analyzing only samples that fall at or below the C:N threshold of 3.555 to confirm that lipid extraction is not necessary. This is the first study to present a simplified standardized method to sample cortical, modern bone tissue for stable isotope analysis. These techniques, used to test and model the effect of acidification on marine turtle cortical bone, can be applied to a wide variety of both marine and terrestrial vertebrates, and the application of the standardized protocol presented here enables direct comparisons among future studies.
Supplementary Material
Acknowledgments
We acknowledge H. Peckham, JM Rodriguez-Baron, V. de la Toba and C. Lucero, and the National Sea Turtle Stranding and Salvage Network for sample collection and preparation. Thank you to J. Shurin for assistance with data analysis. All SIA for Pacific samples conducted at University of Florida, Gainsville, thanks to J. Curtis, and thanks to J. McKay for processing Atlantic samples at the Oregon State University Stable Isotope Laboratory. Thank you to M. Schoeninger, M. Beasley, and N. Burt for collaboration and input on sample processing for SIA of collagen. Additional thanks to E. LaCasella, R. LeRoux, J. Schumacher, G. Serra-Valente, J. Hinke and M. Kinney, M. McCartha and E. Parks for assistance with CITES imports, sample processing, and publication prep. This work was supported by NOAA Fisheries, and C.T.T. was supported by the University of California San Diego (UCSD), NIH T32 GM007240 Cell and Molecular Genetics Training Program, Jeanne Messier Memorial Fellowship, ARCS Foundation Scholarship, and a Hearts de Vite Research Grant. M.R. was supported by the Living Marine Resources Cooperative Science Center as part of the NOAA Educational Partnership Program and the NSF Graduate Research Fellowship Program. Additional support provided by the US Fish & Wildlife Service, NMFS-SWFSC, Western Pacific Fisheries Management Council (NOAA Grant FNA05NMF4411092), the David and Lucile Packard Foundation. For samples originating in Mexico, all research activities and permits were authorized by the Mexican government through SEMARNAP and SEMARNAT permits 150496-213-03, 280597-213-03, 190698-213-03, 280499-213-03, 280700-213-03, SGPA/DGVS/002 4661, SGPA/DGVS/10358, SGPA/DGVS/03501/06, SGPA/DGVS/03406/07, SGPA/DGVS/03481/09, SGPA/DGVS/04990/10, and SGPA/DGVS/04568/11. All exported and imported CITES regulated samples were authorized by the Mexican government through export permit numbers MX-58124 and MX-64301, and the United States government through import permit numbers 11US844694/9 and 12US844694/9. Atlantic samples all originated from the US and samples were obtained under USFWS Permit # TE-676379-5.
References
- 1.Hobson KA, Barnett-Johnson R, Cerling T. In: Isoscapes: Understanding Movement, Pattern, and Processes on Earth Through Isotope Mapping. West JB, Bowen GJ, Dawson TE, Tu KP, editors. Springer; New York: 2010. pp. 273–298. [Google Scholar]
- 2.Newsome SD, Clementz MT, Koch PL. Using stable isotope biogeochemistry to study marine mammal ecology. Mar Mamm Sci. 2010;26:509. [Google Scholar]
- 3.DeNiro MJ, Epstein S. Influence of diet on the distribution of nitrogen isotopes in animals. Geochim Cosmochim Acta. 1981;45:341. [Google Scholar]
- 4.Minagawa M, Wada E. Stepwise enrichment of 15N along food chains: Further evidence and the relation between d15N and animal age. Geochim Cosmochim Acta. 1984;48:1135. [Google Scholar]
- 5.McClelland JW, Montoya JP. Trophic relationships and the nitrogen isotopic composition of amino acids in plankton. Ecology. 2002;83:2173. [Google Scholar]
- 6.Vanderklift MA, Ponsard S. Sources of variation in consumer-diet delta 15N enrichment: a meta-analysis. Oecologia. 2003;136:169. doi: 10.1007/s00442-003-1270-z. [DOI] [PubMed] [Google Scholar]
- 7.DeNiro MJ, Epstein S. Influence of diet on the distribution of carbon isotopes in animals. Geochim Cosmochim Acta. 1978;42:495. [Google Scholar]
- 8.Rau GH, Mearns AJ, Young DR, Olson RJ, Schafer HA, Kaplan IR. Animal 13C/12C correlates with trophic level in pelagic food webs. Ecology. 1983;64:1314. [Google Scholar]
- 9.Clementz MT, Koch PL. Differentiating aquatic mammal habitat and foraging ecology with stable isotopes in tooth enamel. Oecologia. 2001;129:461. doi: 10.1007/s004420100745. [DOI] [PubMed] [Google Scholar]
- 10.McMahon KW, Hamady LIL, Thorrold SR. Ocean Ecogeochemistry: A Review. Oceanography & Marine Biology: An Annual Review. 2013:327. [Google Scholar]
- 11.Kurle C, Gudmundson C. Regional differences in foraging of young-of-the-year Steller sea lions Eumetopias jubatus in Alaska: stable carbon and nitrogen isotope ratios in blood. Mar Ecol Prog Ser. 2007;342:303. [Google Scholar]
- 12.Semmens BX, Ward EJ, Moore JW, Darimont CT. Quantifying inter- and intra-population niche variability using hierarchical bayesian stable isotope mixing models. PloS One. 2009;4:e6187. doi: 10.1371/journal.pone.0006187. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 13.Witteveen BH, Worthy GAJ, Wynne KM, Roth JD. Population structure of North Pacific humpback whales on their feeding grounds revealed by stable carbon and nitrogen isotope ratios. Mar Ecol Prog Ser. 2009;379:299. [Google Scholar]
- 14.Olson RJ, Popp BN, Graham BS, López-Ibarra GA, Galván-Magaña F, Lennert-Cody CE, Bocanegra-Castillo N, Wallsgrove NJ, Gier E, Alatorre-Ramírez V, Ballance LT, Fry B. Food-web inferences of stable isotope spatial patterns in copepods and yellowfin tuna in the pelagic eastern Pacific Ocean. Prog Oceanogr. 2010;86:124. [Google Scholar]
- 15.Seminoff JA, Benson SR, Arthur KE, Eguchi T, Dutton PH, Tapilatu RF, Po BN. Stable isotope tracking of endangered sea turtles: validation with satellite telemetry and δ15N analysis of amino acids. PloS One. 2012;7:e37403. doi: 10.1371/journal.pone.0037403. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 16.Codron J, Codron D, Sponheimer M, Kirkman K, Duffy KJ, Raubenheimer EJ, Mélice J, Grant R, Clauss M, Lee-Thorp JA. Stable isotope series from elephant ivory reveal lifetime histories of a true dietary generalist. Proc Roy Soc B. 2012;279:2433. doi: 10.1098/rspb.2011.2472. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 17.Gillespie JH. Application of stable isotope analysis to study temporal changes in foraging ecology in a highly endangered amphibian. PloS One. 2013;8:e53041. doi: 10.1371/journal.pone.0053041. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 18.Hobson KA. Tracing origins and migration of wildlife using stable isotopes: a review. Oecologia. 1999;120:314. doi: 10.1007/s004420050865. [DOI] [PubMed] [Google Scholar]
- 19.Dalerum F, Angerbjörn A. Resolving temporal variation in vertebrate diets using naturally occurring stable isotopes. Oecologia. 2005;144:647. doi: 10.1007/s00442-005-0118-0. [DOI] [PubMed] [Google Scholar]
- 20.Reich KJ, Bjorndal KA, Martinez del Rio C. Effects of growth and tissue type on the kinetics of 13C and 15N incorporation in a rapidly growing ectotherm. Oecologia. 2008;155:651. doi: 10.1007/s00442-007-0949-y. [DOI] [PubMed] [Google Scholar]
- 21.Kurle CM. Interpreting temporal variation in omnivore foraging ecology via stable isotope modelling. Funct Ecol. 2009;23:733. [Google Scholar]
- 22.Vander Zanden HB, Tucker AD, Bolten AB, Reich KJ, Bjorndal KA. Stable isotopic comparison between loggerhead sea turtle tissues. Rapid Commun Mass Spectrom. 2014;28:2059. doi: 10.1002/rcm.6995. [DOI] [PubMed] [Google Scholar]
- 23.Thomas SM, Crowther TW. Predicting rates of isotopic turnover across the animal kingdom: a synthesis of existing data. J Anim Ecol. 2015;84:861. doi: 10.1111/1365-2656.12326. [DOI] [PubMed] [Google Scholar]
- 24.Snover M, Hohn A, Crowder L, Macko S. Combining stable isotopes and skeletal growth marks to detect habitat shifts in juvenile loggerhead sea turtles Caretta caretta. Endanger Species Res. 2010;13:25. [Google Scholar]
- 25.Elorriaga-Verplancken F, Aurioles-Gamboa D, Newsome SD, Martínez-Díaz SF. δ15N and δ13C values in dental collagen as a proxy for age- and sex-related variation in foraging strategies of California sea lions. Mar Biol. 2013;160:641. [Google Scholar]
- 26.Turner Tomaszewicz CN, Seminoff JA, Avens L, Kurle C. Methods for sampling sequential annual bone growth layers for stable isotope analysis. Methods Ecol and Evol. in review. [Google Scholar]
- 27.Koch PL. In: Stable Isotopes in Ecology and Environmental Science. 2nd. Michener R, Lajtha K, editors. Blackwell; Malden: 2007. pp. 99–154. [Google Scholar]
- 28.Betts F, Blumenthaland NC, Posner AS. Bone Mineralization. J Cryst Growth. 1980;53:63. [Google Scholar]
- 29.LeGeros RZ. Apatites in biological systems. Progress in Crystal Growth Characteristics. 1981;4:1. [Google Scholar]
- 30.Koch PL, Tuross N, Fogel ML. The effects of sample treatment and diagenesis on the isotopic integrity of carbonate in biogenic hydroxylapatite. J Archaeol Sci. 1997;24:417. [Google Scholar]
- 31.Vallet-Regi M, Gonzalez-Calbet JM. Calcium phosphates as substitution of bone tissues. Progress in Solid State Chemistry. 2004;32:1. [Google Scholar]
- 32.Lee-Thorp JA, Van Der Merwe NJ. Aspects of the chemistry of modern and fossil biological apatites. J Archaeol Sci. 1991;18:343. [Google Scholar]
- 33.Biasatti DM. Stable carbon isotopic profiles of sea turtle humeri: implications for ecology and physiology. Palaeogeogr Palaeoclimatol Palaeoecol. 2004;206:203. [Google Scholar]
- 34.Lee-Thorp JA, Scaly JC, van der Merwe NJ. Stable Carbon Isotope Ratio Differences Between Bone Collagen and Bone Apatite, and their Relationship to Diet. J Archaeol Sci. 1989;16:585. [Google Scholar]
- 35.Cerling TE, Harris JM. Carbon isotope fractionation between diet and bioapatite in ungulate mammals and implications for ecological and paleoecological studies. Oecologia. 1999;120:347. doi: 10.1007/s004420050868. [DOI] [PubMed] [Google Scholar]
- 36.Kohn MJ, Cerling TE. In: Phosphates Geochemical, Geobiological, and Materials Importance Reviews in Mineralogy and Geochemistry. Kohn MJ, Rakovan J, Hughes JM, editors. Mineralogical Society of America; Washington D.C.: 2002. pp. 455–488. [Google Scholar]
- 37.Lee-Thorp J, Sponheimer M. Three case studies used to reassess the reliability of fossil bone and enamel isotope signals for paleodietary studies. J Anthropol Archaeol. 2003;22:208. [Google Scholar]
- 38.Ambrose SH. Preparation and characterization of bone and tooth collagen for isotope analysis. J Archaeol Sci. 1990;17:431. [Google Scholar]
- 39.Krueger HW, Sullivan CH. In: Stable Isotopes in Nutrition. Turnlund J, editor. American Chemical Society Symposium Series; Washington D.C.: 1984. pp. 205–220. [Google Scholar]
- 40.Ambrose SH, Norr L. In: Prehistoric Human Bone: Archaeology at the Molecular Level. Lambert J, Grupe G, editors. Springer; Berlin: 1993. pp. 1–37. [Google Scholar]
- 41.Tieszen LL, Fagre T. Carbon isotopic variability in modern and archaeological maize. J Archaeol Sci. 1993;20:25. [Google Scholar]
- 42.Chisholm BS, Nelson DE, Hobson KA, Schwarcz HP, Knyf M. Carbon isotope measurement techniques for bone collagen: Notes for the archaeologist. J Archaeol Sci. 1983;10:355. [Google Scholar]
- 43.Jørkov MLS, Heinemeier J, Lynnerup N. Evaluating bone collagen extraction methods for stable isotope analysis in dietary studies. J Archaeol Sci. 2007;34:1824. [Google Scholar]
- 44.Medeiros L, da Silveira Monteiro D, Petitet R, Bugoni L. Effects of lipid extraction on the isotopic values of sea turtle bone collagen. Aquat Biol. 2015;23:191. [Google Scholar]
- 45.Zug GR, Wynn AH, Ruckdeschel C. Age Determination of Loggerhead Sea Turtles, Caretta caretta, by Incremental Growth Marks in the Skeleton. Smithsonian Contributions to Zoology. 1986:1. [Google Scholar]
- 46.Goshe LR, Avens L, Bybee J, Hohn AA. An evaluation of histological techniques used in skeletochronological age estimation of sea turtles. Chelonian Conserv Biol. 2009;8:217. [Google Scholar]
- 47.Goshe LR, Avens L, Scharf FS, Southwood AL. Estimation of age at maturation and growth of Atlantic green turtles (Chelonia mydas) using skeletochronology. Mar Biol. 2010;157:1725. [Google Scholar]
- 48.Avens L, Goshe LR, Harms CA, Anderson ET, Goodman Hall A, Cluse WM, Godfrey MH, Braun-Mc Neill J, Bailey R, Lamont MM. Population characteristics, age structure, and growth dynamics of neritic juvenile green turtles in the northeastern Gulf of Mexico. Mar Ecol Prog Ser. 2012;458:213. [Google Scholar]
- 49.Godley BJ, Thompson DR, Waldron S, Furness RW. The trophic status of marine turtles as determined by stable isotope analysis. Mar Ecol Prog Ser. 1998;166:277. [Google Scholar]
- 50.Newsome SD, Koch PL, Etnier MA, Aurioles-Gamboa D. Using Carbon and Nitrogen Isotope Values To Investigate Maternal Strategies in Northeast Pacific Otariids. Mar Mamm Sci. 2006;22:556. [Google Scholar]
- 51.Percot A, Viton C, Domard A. Optimization of chitin extraction from shrimp shells. Biomacromolecules. 2003;4:12. doi: 10.1021/bm025602k. [DOI] [PubMed] [Google Scholar]
- 52.Jacob U, Mintenbeck K, Brey T, Knust R, Beyer K. Stable isotope food web studies: a case for standardized sample treatment. Mar Ecol Prog Ser. 2005;287:251. [Google Scholar]
- 53.Serrano O, Serrano L, Mateo MA, Colombini I, Chelazzi L, Gagnarli E, Fallaci M. Acid washing effect on elemental and isotopic composition of whole beach arthropods: Implications for food web studies using stable isotopes. Acta Oecol. 2008;34:89. [Google Scholar]
- 54.Koch PL, Fogel ML, Tuross N. In: Stable Isotopes in Ecology and Environmental Science. 1st. Michener R, Lajtha K, editors. Blackwell; Oxford: 1994. pp. 63–92. [Google Scholar]
- 55.Post DM, Layman CA, Arrington DA, Takimoto G, Quattrochi J, Montaña CG. Getting to the fat of the matter: models, methods and assumptions for dealing with lipids in stable isotope analyses. Oecologia. 2007;152:179. doi: 10.1007/s00442-006-0630-x. [DOI] [PubMed] [Google Scholar]
- 56.R Core Team. R: A language and environment for statistical computing. Vienna: 2013. Internet. [Google Scholar]
- 57.Schoeninger MJ, Moore KM, Murray ML, Kingston JD. Detection of bone preservation in archaeological and fossil samples. Appl Geochem. 1989;4:281. [Google Scholar]
- 58.Van Klinken GJ. Bone Collagen Quality Indicators for Palaeodietary and Radiocarbon Measurements. J Archaeol Sci. 1999;26:687. [Google Scholar]
- 59.Kurle CM, Koch PL, Tershy BR, Croll DA. The effects of sex, tissue type, and dietary components on stable isotope discrimination factors (Δ13C and Δ15N) in mammalian omnivores. Isot Environ Health Stud. 2014;50:307. doi: 10.1080/10256016.2014.908872. [DOI] [PubMed] [Google Scholar]
- 60.Koch PL. Isotopic reconstruction of past continental environments. Annu Rev Earth Planet Sci. 1998;26:573. [Google Scholar]
- 61.Kolasinski J, Rogers K, Frouin P. Effects of acidification on carbon and nitrogen stable isotopes of benthic macrofauna from a tropical coral reef. Rapid Commun Mass Spectrom. 2008;22:2955. doi: 10.1002/rcm.3694. [DOI] [PubMed] [Google Scholar]
- 62.Mateo MA, Serrano O, Serrano L, Michener RH. Effects of sample preparation on stable isotope ratios of carbon and nitrogen in marine invertebrates: implications for food web studies using stable isotopes. Oecologia. 2008;157:105. doi: 10.1007/s00442-008-1052-8. [DOI] [PubMed] [Google Scholar]
- 63.Schlacher TA, Connolly RM. Effects of acid treatment on carbon and nitrogen stable isotope ratios in ecological samples: a review and synthesis. Methods Ecol Evol. 2014;5:541. [Google Scholar]
- 64.Rau GH, Sweeney RE, Kaplan IR. Plankton 13C:12C ratio changes with latitude : differences between northern and southern oceans. Deep Sea Res. 1982;29:1035. [Google Scholar]
- 65.Wallace BP, Seminoff JA, Kilham SS, Spotila JR, Dutton PH. Leatherback turtles as oceanographic indicators: stable isotope analyses reveal a trophic dichotomy between ocean basins. Mar Biol. 2006;149:953. [Google Scholar]
- 66.Vander Zanden HB, Bjorndal KA, Mustin W, Ponciano JM, Bolten AB. Inherent variation in stable isotope values and discrimination factors in two life stages of green turtles. Physiol Biochem Zool. 2012;85:431. doi: 10.1086/666902. [DOI] [PubMed] [Google Scholar]
- 67.Clementz MT, Koch PL, Beck CA. Diet induced differences in carbon isotope fractionation between sirenians and terrestrial ungulates. Mar Biol. 2007;151:1773. [Google Scholar]
- 68.Parng E, Crumpacker A, Kurle CM. Variation in the stable carbon and nitrogen isotope discrimination factors from diet to fur in four felid species held on different diets. J Mammal. 2014;95:151. [Google Scholar]
- 69.Avens L, Goshe LR, Pajuelo M, Bjorndal KA, MacDonald BD, Lemons GE, Bolten AB, Seminoff JA. Complementary skeletochronology and stable isotope analyses offer new insight into juvenile loggerhead sea turtle oceanic stage duration and growth dynamics. Mar Ecol Prog Ser. 2013;491:235. [Google Scholar]
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