10.1098/rsbl.2012.0919 Accelerometry predicts daily energy expenditure in a bird with high activity levels Kyle Elliott, Maryline Le Vaillant, Akiko Kato, John Speakman, Yan Ropert-Coudert SUPPLEMENTARY MATERIALS: METHOD DETAILS From July 9 to August 1, 2009 we captured 20 breeding (4 incubating, 16 chick-rearing) thick-billed murres at the Coats Island colony in Nunavut, Canada, and injected them in the brood patch with 0.5 mL of doubly-labelled water (50% H2O18 and 25% D2O). We then attached an accelerometer (M190-D2GT, 12 bit resolution, 52·15 mm, 16 g, 0.1 m depth accuracy, Little Leonardo, Tokyo, Japan; average murre body mass = 1014 g, SD = 66 g) to the lower back of each bird using Tesa tape. We also attached a timedepth-temperature recorder (LAT1500, 3.2 g, resolution = 0.25β°C, time constant = 0.055 s -1, Lotek Wireless, St. John’s, Canada) to the leg band. The accelerometer recorded depth and temperature at 1 Hz and acceleration along the head-tail (surging) and dorso-ventral (heaving) axes at 16 Hz. Past experiments at our colony showed that the optimal method for measuring equilibrium isotopic values (total body water) was the plateau method at 90 minutes using the oxygen-18 equilibrium value (Jacobs et al. 2012). Therefore, we obtained 100 µL equilibrium blood samples 90 min after injection from the tarsal vein. We released the birds between the initial and equilibrium blood samples and were unable to recapture three birds for the equilibrium blood sample. In those cases, we estimated the isotopic concentrations from the equation between isotopic concentration and body mass (R2> 0.98; see Jacobs et al. 2012). We recaptured the birds, retrieved accelerometers and obtained a second 100 µL blood sample from the brachial vein 24 hours later. Based on known diet of murres at our study colony, we used a respiratory quotient of 0.85. Capillaries that contained the blood samples were then distilled [1], and water from the resulting distillate was used to produce CO2 and H2 (methods in [2] for CO2 and [3] for H2). The isotope ratios 18O: 16O and 2H: 1 H were analysed using gas source isotope ratio mass spectrometry (Optima, Micromass IRMS and Isochrom μG, Manchester, UK). Samples were run alongside three lab standards for each isotope (calibrated to international standards) to correct delta values to ppm. Isotope enrichments were converted to values of daily energy expenditure using a single pool model as recommended for this size of animal by Speakman [4]. There are several alternative approaches for the treatment of evaporative water loss in the calculation [5]. We chose the assumption of a fixed evaporation of 25% of the water flux (equation 7.17: [6]), which has been established to minimise error in a range of conditions [5,7]. All of the isotopic concentrations and daily energy expenditure calculations are attached in the Supporting Information. Validations of doubly-labelled water against respirometry usually indicate an absolute error of ±3% for average values across groups and ±10% for individuals [6]. A recent paper on closely related rhinoceros auklets [8] suggests a similar error for auks. Absolute values of doubly-labelled water measurements are strongly dependent on the equation used to estimate energy expenditure, on the respiratory quotient and on the estimate for total body water. We directly measured respiratory quotient (see above) and total body water [9], and so our error is predicted to be smaller than many other studies that do not directly measure those values [6]. Furthermore, values for daily energy expenditure estimated from different equations vary in absolute estimates but are strongly correlated (R2> 0.97 for our study for the equations listed in [6]). Thus, even if a different equation were used, the relative magnitudes of energy expenditure as estimated from doubly-labelled water would be largely unaffected and therefore the R2 and AIC values would not change. In short, our central question—whether PDBA is correlated with field metabolic rate as measured via doubly-labelled water—is unaffected by typical alterations in how energy expenditure is calculated from the doubly-labelled water measurements. Estimates of uncertainty follow Speakman [7]. Overall Dynamic Body Acceleration (ODBA) is calculated from triaxial acceleration (surge, sway and heave) [10] and Partial Dynamic Body Acceleration (PDBA) is calculated from one or two-axis acceleration data [11]. In our study, acceleration was recorded in 2 axes, corresponding surge and heave, at 16 Hz. Wing stroke and thrust can be recorded on heave and surge accelerations of the body [12]. As the flapping frequency of guillemots during flight and diving was ~6-7 Hz and 1-2 Hz, respectively, 16 Hz is below the Nyquist sampling frequency for both locomotory modes. Thus, although PDBA could be underestimated comparing to higher-frequency sampling data, the underestimation would be similar across all individuals and both wing beat frequency and amplitude can be obtained reliably. To calculate the PDBA, at first the static acceleration was approximated by applying a smoothing function to the total acceleration recorded for each axis [13]. We used the box smooth function with 31 points of IGOR Pro, which is similar to running mean of 2 sec [14], to generate the static component (π΄Μ ).The dynamic acceleration is then determined by subtracting the static component from the total acceleration, A ([13], see also Fig. 3 in [13]). PDBAsum is the sum of the absolute values of the dynamic accelerations from two axes [13], although acceleration is a vectorial quantity. PDBAvectorial could be more appropriate in cases where accelerometers cannot be accurately placed on the animal, or movements occur in a variable manner and along various planes [14]. ππ·π΅π΄π π’π = |π΄π₯ − Μ π΄Μ Μ Μ π₯ | + |π΄π¦ − Μ Μ Μ Μ π΄π¦ | 2 ππ·π΅π΄π£πππ‘πππππ = √(π΄π₯ − Μ π΄Μ Μ Μ π₯ )2 + (π΄π¦ − Μ Μ Μ Μ π΄π¦ ) Those two measures of PDBA were closely correlated with one another (R2 = 0.9986) and we therefore used PDBAvectorial as a better indicator of dynamic body acceleration because it is less sensitive to position of the logger on the body. We used the acceleration profiles coupled with the temperature and pressure logs to determine when the bird was in one of four different locomotory modes: flying, diving, at the water surface and on land [15]. After accounting for the temperature drift on depth data (never more than 1 m), we used the pressure log to determine when the bird was diving. We then used a computer script based on [16] to determine when the bird is flying (high amplitude, high frequency constant between 6-8 Hz), swimming on the water (intermediate amplitude and variable frequency) or resting on the land (low amplitude and variable frequency) via filters designed to outline the distinctive frequencies and amplitudes associated with each of those behaviours. Next, we used the temperature log as a “check” on the ethograms determined via acceleration, as temperature is high when the bird is at the colony, relatively low and variable when the bird is flying and very low and stable when the bird is on the ocean surface (see detailed description of the technique in [17] and [18]). We specifically used general linear models with the intercept set to zero for the time budget model (no energy expended if no time had occurred) to test the following two models for predicting daily energy expenditure (DEE): π·πΈπΈ = ππΏ ππΏ + ππ ππ + ππΉ ππΉ + ππ· ππ· (1) 2 (2), Where Mx is the average metabolic rate during mode x, Tx is the time spent in mode x, β is the intercept, ηx is the efficiency coefficient converting accelerometry (a proxy of mechanical work) into daily energy expenditure (metabolic work) and Ax is the integrated PDBA across all time spent in a particular locomotory mode (the sum of all PDBA values for that activity). We partitioned time budgets into the following locomotory modes: resting on land (L), swimming on surface (S), flying (F) and diving (D) and, for each individual, calculated the time spent in each mode and total PDBA (time spent in the mode * average PDBA for a particular individual for a particular locomotory mode) for each mode. The coefficients were then determined by entering the data into a general linear model, with the intercept set at zero for the time budget model, and selecting the value that reduced the log-likelihood (essentially, the model that reduced the sum of square deviances). Equation (1), which involved just time budgets and no accelerometry, was considered the null model. If accelerometry did not improve predictability of energy expenditure over time budgets alone, then the ability of equation (2) to predict DEE would be no better than equation (1). We used Akaike’s information criterion (AIC) to compare among models, as AIC penalizes models that are needlessly complex. Specifically, we compared among different models to see whether different models could be simplified. For example, if metabolic rate during swimming at the surface and diving were not significantly different, then Model (1) could be simplified by stating that MS = MD. Likewise, if the same linear regression could convert PDBA during both swimming and diving into DEE, then Model (2) could be simplified by stating that ηS = ηD. In either case, the AIC would select the more parsimonious, simplified model for describing daily energy expenditure as a function of time budgets or accelerometry. Statistical tests occurred in R 2.10.1. REFERENCES 1 Nagy, K. A. 1983 The Doubly Labeled Water (3HH18O) Method: a guide to its use. UCLA Publication no 12-1417, UCLA, Los Angeles, CA. 2 Speakman, J.R., Nagy, K.A., Masman, D., Mook, W.G., Poppitt, S.D., Strathearn, G.E. & Racey, P.A. 1990 Inter laboratory comparison of different analytical techniques for the determination of O-18 abundance. Anal. Chem.62, 703–708. 3 Speakman, J.R. & Krol, E. 2005 Validation of the doubly-labelled water method in a small mammal Physiol. Biochem. Zool.78, 650-667 4 Speakman, J. R. 1993 How should we calculate CO2 production in doubly labeled water studies of animals? Funct. 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