Printer Friendly

Prevalence and abundance of cyamid "whale lice" (Cyamus ceti) on subsistence harvested bowhead whales (Balaena mysticetus).

ABSTRACT. We present findings on the prevalence and abundance of cyamid ectoparasites (Cyamus ceti) or "whale lice" on bowhead whales (Balaena mysticetus) harvested for subsistence in the Bering, Chukchi, and Beaufort Seas from 1973 to 2015. Cyamids were present on 20% of the 673 whales that were examined for cyamid ectoparasites. Logistic regression was used to determine factors associated with cyamid prevalence. The probability of cyamid presence increased with age, length, and improving body condition, but decreased over the past 35 years. Cyamid presence was also more probable on whales harvested in the spring than on those harvested in the fall. When present, cyamid abundance was typically low (< 10 per whale). Case histories provide ancillary information about the relationships between abundance of cyamids and their bowhead hosts. Environmental change and increasing anthropogenic disturbances are expected to occur in the Arctic regions inhabited by bowheads. We recommend continued monitoring of subsistence harvested whales for cyamids, as well as further investigations into the roles of environmental and anthropogenic variables in cyamid prevalence and abundance, as part of a comprehensive program of Arctic ecosystem assessment.

Key words: cyamid; whale lice; Cyamus ceti; ectoparasite; bowhead whale; Balaena mysticetus; Arctic; Bering Sea; Chukchi Sea; Beaufort Sea

RESUME. Nous presentons nos constatations en matiere de prevalence et d'abondance de l'ectoparasite cyamidae (Cyamus ceti) ou << pou des baleines >> se trouvant sur la baleine boreale (Balaena mysticetus) capturee a des fins de subsistance dans la mer de Bering, la mer des Tchouktches et la mer de Beaufort entre 1973 et 2015. Les cyamidae etaient presents sur 20 % des 673 baleines qui ont ete examinees dans le but d'y trouver des ectoparasites cyamidae. La regression logistique a servi a determiner les facteurs lies a la prevalence de cyamidae. La probabilite de la presence de cyamidae augmentait en fonction de l'age, de la longueur et de l'amelioration de l'etat corporel, mais elle a diminue au cours des 35 dernieres annees. De plus, la presence de cyamidae etait egalement plus probable chez les baleines capturees au printemps que chez les baleines capturees a l'automne. Lorsque presents, les cyamidae etaient generalement de faible abondance (<10 par baleine). Les cas types fournissent des renseignements supplementaires sur les relations entre l'abondance de cyamidae et les baleines hotes. Des changements environnementaux et de plus grandes perturbations anthropiques sont attendus dans les regions arctiques ou evolue la baleine boreale. Nous recommandons la surveillance continue des baleines attrapees a des fins de subsistance pour en detecter les cyamidae. Nous recommandons egalement des etudes plus approfondies afin de determiner le role des variables environnementales et anthropiques en matiere de prevalence et d'abondance des cyamidae, dans le cadre d'un programme exhaustif d'evaluation de l'ecosysteme arctique.

Mots cles : cyamidae; pou de la baleine; Cyamus ceti; ectoparasite; baleine boreale; Balaena mysticetus; Arctique; mer de Bering; mer des Tchouktches; mer de Beaufort

Traduit pour la revue Arctic par Nicole Giguere.


Cyamids (Crustacea, Amphipoda), also known as "whale lice," are ectoparasites that feed on the epidermis of whales (Rowntree, 1983, 1996; Schell et al., 2000). They are able to stay attached to the surface of their cetacean hosts through several adaptions, including sharp grasping claws and a flattened shape (Fig. 1). Although they are common to many cetacean species, some cyamid species are host-specific. For instance, Cyamus ovalis, C. gracilis, and C. erraticus can be found only on right whales (Eubalaena spp.) (Kaliszewska et al., 2005). Similarly, the bowhead whale (Balaena mysticetus), another member of the family Balaenidae closely related to the right whale, has a closely associated cyamid ectoparasite (Cyamus ceti, Fig. 1).

Long-term visual health assessments of North Atlantic right whales (Eubalaena glacialis) suggest a relationship between the spatial distribution and relative abundance of cyamids and the health status of their host (Pettis et al., 2004). For example, orange cyamids (C. erraticus) occur in relatively low numbers on all healthy adult right whales (R. Rolland, pers. comm. 2015; J. Seger, pers. comm. 2016), where their spatial distribution is largely confined to genital and mammary folds. But the occurrence of these cyamids in large numbers on the host's dorsal surface, particularly around the blowholes, has been associated with poor health (Schick et al., 2013; J. Seger, pers. comm. 2016). Such infestations have been observed in "last-sighting" photos, after which the whales were presumed dead (Pettis et al., 2004). In another example, a North Atlantic right whale, entangled by a line around its rostrum that prevented feeding, became almost entirely covered with cyamids before the animal's eventual death from starvation (Moore et al., 2006; M. Moore, pers. comm. 2015; R. Rolland, pers. comm. 2015). Presumably, the reduced swimming speed of physically compromised whales allows cyamids to proliferate by occupying more "environments" that are hydrodynamically favorable (Rowntree, 1996).

Although the Bering-Chukchi-Beaufort Seas (BCB) population of bowheads is currently large and increasing (Givens et al., 2016), its remote Arctic home range means that these whales are a difficult species to monitor, and little is known about their cyamid ectoparasites. Bowheads are legally hunted by Native Alaskans, and postmortem examinations of subsistence harvested bowhead whales have been conducted for more than 40 years in cooperation with the Alaska Eskimo Whaling Commission and village whaling captains' associations. This investigation reviews the harvest records collected by the National Marine Fisheries Service in the 1970s and the North Slope Borough Department of Wildlife Management from the early 1980s to the present. Our fundamental goal was to better understand the factors associated with cyamid prevalence and abundance on BCB bowhead whales, and this work presents, to our knowledge, the first such long-term investigation.

Our specific objectives were to characterize cyamid prevalence and abundance with respect to demographic, morphological, seasonal, and body condition variables of bowhead whales. A further objective was to improve the basic understanding of cyamid ecology. To do so, we compiled and analyzed data from all harvest records of bowheads that were visually inspected for cyamids.


In cooperation with the Alaska Eskimo Whaling Commission and village Whaling Captains' Associations, postmortem examinations of subsistence harvested bowhead whales were conducted by the National Marine Fisheries Service in the 1970s and by the North Slope Borough Department of Wildlife Management from the early 1980s to the present. Upon landing, the exposed skin of the whale (including the gape of the mouth, eyelids, blowholes, genital slit, and peduncle, as well as any skin depressions, scars, cracks, or wounds) was examined for cyamid ectoparasites. The presence, location, and relative abundance of cyamids were noted, as were other biometric and demographic data. Detailed descriptions of the methods used to collect whale biometric and demographic data can be found in George (2009).

Because harvested bowheads typically had fewer than 10 cyamids present, and the count distribution was highly skewed (e.g., the median count was 2, but the highest three cyamid totals were recorded as 201. 200, and 100; see Fig. 2), absolute cyamid abundance was not formally analyzed. Instead, our analyses focused on cyamid presence.

We fit logistic regression models to predict the probability of cyamid presence. The response variable for all models was an indicator variable for cyamid presence (present = 1, absent = 0). Sex of the whale (SEX, female = 1 and male = 0) was determined by external visual examination. The presence of scars (SCAR, present = 1, absent = 0) was ascertained from the observer comments recorded in the harvest records for each whale. Whales were scored as having scars if any wounds, gouges, cracks, killer whale (Orcinus orea) bites, line entanglements, or ship strikes were present. Total body length (LEN) was measured as the straight-line distance from the distal end of the rostrum to the inside of the fluke notch. Whale age (AGE) was estimated via several methods, including aspartic acid racemization of eye lens tissue (George et al., 1999), stable isotope analysis of the baleen (Lubetkin et al., 2008), and corpora counts in the ovaries (George et al., 2011). We also considered the whale's body condition (CON D) as an explanatory variable. We defined COND as the residuals from a "body condition model" that predicts the whale's girth as a function of its length. Because we ran two families of logistic regression models based on two different data sets (see Tables 1 and 2), we generated residuals from two separate body condition models:

1. body condition model 1 (used in Table 1 models)

[] = 124.5 + 0.56 x [] ([R.sup.2] = 0.88, [F.sub.1,124] = 935.8, p = 2.2 x [10.sup.-16])

2. body condition model 2 (used in Table 2 models)

[] = 166.0 + 0.52 x [] ([R.sup.2] = 0.79, [F.sub.1,495] = 1890, p = 2.2 x [10.sup.-16])

where [] = axillary girth of the whale, which is measured as one-half of the whale's circumference (cm) taken from the dorsal centerline to the ventral centerline and adjacent to the posterior insertion of the pectoral flippers; [] = total length of the whale, measured as the straight-line distance (cm) from the distal end of the whale's rostrum to the inside of the fluke notch.

The sign and magnitude of the residuals from these models indicate whether a whale is fatter or thinner than predicted for its length and thereby act as an index that characterizes body condition (COND). To assess temporal relationships, we included a variable for the season (SEAS, where spring = 0 and fall = 1) and the year (YEAR) in which each whale was harvested.

Our first set of models (Table 1, models 1-5) considered the following six explanatory variables: AGE, SEX, SCAR, COND, SEAS, and YEAR. We did not include AGE and LEN in the same models because of collinearity (Pearson's product-moment correlation, r = 0.77, p < 2.2 x [10.sup.-16]). Rather, using the same data set, we replaced AGE with LEN and re-ran our models using the same procedures (Table 1, models 6-10). The sample size for all models in the first analysis (n = 126) was substantially less than the number of examined whales because relatively few whales in our harvest records had an age estimate to associate with their length and girth measurements. However, by considering whales with length and girth measurements, regardless of the presence of an age estimate, it was possible to model cyamid presence with a sample size that was almost four times as large (n = 497). This set of models (Table 2) considered the variables LEN, COND, SEX, SCAR, SEAS, and YEAR. We generated these models with the same procedures used for those in Table 1.

All analyses were conducted using R Statistical Software (R Core Team, 2014). Our modeling procedure began by constructing all possible univariate models. We next constructed a "full" model. For the first analysis (Table 1), because LEN and AGE are highly correlated, it was necessary to construct two variants of the "full" model, each including five explanatory variables in common (SEX, SCAR, COND, SEAS, YEAR) and differing only in the inclusion of LEN or AGE. For the second analysis (Table 2) the "full" model included LEN, COND, SEX, SCAR, SEAS, and YEAR. Starting with each variant of the "full" model, we used backward elimination to sequentially drop variables based on the highest non-significant p-value until all remaining variables were significant at [alpha] = 0.05. Finally, for the highest-performing additive effect models, we considered the influence of interaction terms. Model performance was then compared and ranked by corrected Akaike's Information Criterion ([AIC.sub.c]). We considered the best models to be those with [DELTA][AIC.sub.c] scores below 2 when compared to the highest-ranking model (Burnham and Anderson, 2002). Among these, it is reasonable to prefer the most parsimonious model that retains all statistically significant effects.

We also ran chi-squared tests to assess whether cyamid presence was associated with sex, the village where each whale was harvested, and the harvest season (i.e., spring or fall). To consider the relationship between body condition and age, we compared the mean age of whales with body condition scores above the 80th percentile to that of whales with body condition scores below the 20th percentile. The mean length and age of whales harvested in the spring vs. fall were compared using t-tests. Annual patterns in the percentage of harvested whales with cyamids, as well as the mean annual length of harvested whales, were assessed for temporal autocorrelation using the "acf" function in R.

To evaluate the conditions that may be related to cyamid abundance on harvested bowheads, we also qualitatively assessed the written observations from the harvest records in our database. A selection of case studies is provided in Table 3.


We compiled records from 673 harvested bowheads that had been visually examined for ectoparasites from 1973 to 2015. This sample included 341 males (51%) and 332 females (49%). Cyamids were present on a total of 137 (20%) of the whales examined. Of the whales with cyamids, 67% had 1-5 cyamids present (Fig. 2, Class 1), whereas the remaining 33% had 6 or more cyamids (Fig. 2, Classes 2 and 3). There was no significant difference between male and female bowheads in the proportion with cyamids present (Fig. 2; [chi square] = 0.43, df = 1, p = 0.51; n = 666). Although some villages (e.g., Barrow) harvest far more bowheads than others (Fig. 3), there was no significant difference by village in the proportion of examined whales with cyamids present ([chi square] = 6.5, df = 5, p = 0.26, n = 673). Season was significantly related to the proportion of harvested bowheads with cyamids ([chi square] = 4.75, df = 2, p = 0.03, n = 730), with more spring whales having cyamids present. The mean age of whales with a body condition index (i.e., residuals from the "body condition model" described above in the methods) above the 80th percentile was 32 years, and the mean age of whales whose body condition index was below the 20th percentile was 22.8 years. However, a t-test showed no significant difference (t = 0.93, df = 44, p-value = 0.18). A comparison of the mean length and age of harvested bowheads by season shows that spring whales are significantly longer (t = -2.28, df = 660, p = 0.02) and older (t = -2.78, df = 149.9, p = 0.006) than fall whales. We also observed a pattern that might suggest periodicity in the percentage of whales with cyamids over time and in the mean annual length of harvested bowheads (Fig. 4). These patterns were significantly related ([R.sup.2] = 0.27, [F.sub.1,34] = 12.1, p = 0.001). Analysis of the annual mean lengths of harvested bowheads showed a significant positive temporal autocorrelation at a three-year time lag. There was no significant autocorrelation in the proportion of whales with cyamids (See Fig. 4).

The models in Table 1 were based on a subset of data in which an age estimate was associated with each examined whale (n = 126). Two sets of models are shown in Table 1: models 1-5 included AGE and excluded LEN, whereas models 6-10 did the opposite. Model 1 was the highest ranked model in the entire set of models in Table 1, and suggests that older whales have a higher probability of cyamid presence than younger whales. Model 1 also included a significant interaction between AGE and YEAR. Models 2-5 all had [DELTA][AIC.sub.c] scores below 2, and are therefore comparable in performance to model 1. These top five models all included the variables AGE, YEAR, and/or their interaction. Model 4 was an exception in that it also included the variable SCAR. Models 6-10 in Table 1 utilized LEN as a surrogate for age. While LEN is statistically significant in models where it replaced AGE, altogether, these models have a poorer fit. The effect of SCAR and COND were not found to be important in the highest ranked models, and when present, were not significant. Although the performance of models 6-10 was substantially lower (e.g., model 6 had the lowest [DELTA][AIC.sub.C] = 7.20), their structure was similar to the higher-ranking models in their inclusion of an age proxy (LEN), YEAR, and/or their interaction.

The models in Table 2 were based on data from examined whales regardless of whether they had an associated age estimate (n = 497). The top ranked model (model 1) was also the only model with a [DELTA][AIC.sub.C] score below 2. This model suggests that a whale's length (LEN) is significantly related to the probability of cyamid presence, but the effect of this variable is complicated by an interaction with the season of harvest (SEAS). An analysis of deviance confirms that the model terms for LEN and LEN:SEAS together significantly affect the probability of cyamid presence (P = 0.005). Body condition (COND) was also significant and was positively associated with the probability that cyamids were present. Despite their lower performance, models 2-6 (Table 2) were very consistent with model 1 in the use of LEN, COND, and SEAS.

A review of selected case histories provides ancillary information concerning the abundance of cyamids and their complex relationships with bowhead whales. A very old and large bowhead had high cyamid abundance (Table 3, whale 95B09, aged 172). So too did smaller or younger whales (Table 3, whales 14B04, 04B03) and four other sexually immature whales (i.e., < 13.9 m long; see Nerini et al., 1984). Severely physically compromised whales also had high cyamid abundance. Examples include whale 15K K01 (Table 3) which had "about 100" cyamids present; and whale 08G01, which had an apparent chronic injury to its lower spine. This whale was described as having "numerous" cyamids present, "large patches of cyamids on skin of lower body and genital slit," and with a drawing indicating "lots of bugs" posterior to the genital slit. Its skin was reported as "thin," and the skin-blubber boundary was described as "tough." In contrast, whale 99B14, despite a severe line entanglement and poor physical condition, did not have cyamids present. Finally, scarring and skin damage (e.g., 15B20, 15KK01, 92B11, 82WW01, and 76B20) were associated with cyamid presence in 21% (n = 29) of examined whales with cyamids.


Although cyamids were detected on 20% of harvested bowhead whales, cyamid abundance tended to be very low. For example, 95% of the bowheads examined for cyamids had fewer than 10 individuals present (Fig. 2). Because cyamids have no free-swimming aquatic life-stage (Rowntree, 1983, 1996), parasite transmission among bowheads likely occurs via direct contact. In addition to direct contact between whales, cyamid proliferation also requires successful attachment to the host. Unlike right whales, bowheads have no callosities upon which cyamids can grip. Thus, the presence of damaged skin, which is more likely to occur in older whales, increases the chances that whale-to-whale parasite transmission will be successful. Given the low cyamid prevalence, very low absolute numbers of cyamids, and the absence of callosities, the transmission of cyamids from host to host may be dependent upon the frequency of whale-to-whale interactions and the accumulation of skin damage. Whereas the rate of parasite transmission may be low, the very long lifespan of bowheads (George et al., 1999) makes it plausible that older whales have had more opportunities for the direct transfer of cyamids from another host through increased intra-specific interactions. Moreover, the accumulation of skin damage over time may increase the likelihood of successful parasite transmission by providing the structure to which cyamids can grip. This hypothesis is supported by the preferred models of cyamid presence (Table 1, model 1 and Table 2, model 1), each of which included AGE or LEN (a surrogate for age) as a variable that was positively related to the probability of cyamid presence. The same patterns can be seen in lower performing models, in which AGE and LEN are often significant predictors. These findings are consistent with written comments from our database (Table 3) that relate the spatial use of cyamids to whale epidermal cracks, dents, scars, and injuries, all of which tend to accrue with age.

The positive association of body condition to cyamid presence (Table 2; model 1) was a surprising trend. Presumably, whales in poor body condition swim more slowly, thereby increasing the chances that cyamids can stay attached and proliferate, whereas whales in good condition swim faster, making it more difficult for cyamids to stay attached. The relationship between body condition and age may explain this relationship. The positive association between bowhead age and body condition may be the result of lower foraging efficiency in young post-wean individuals with underdeveloped baleen racks. Later in life, when mature whales have a fully formed baleen rack, their body condition scores tend to increase (George, 2009; George et al., 2015). Additionally, if bowhead longevity is a function of body condition, then older whales (i.e., those demonstrated to be more likely to have cyamids) should have higher body condition scores. Our data suggest a weak relationship between age and body condition (p = 0.18), with whales in the best condition (body condition index [greater than or equal to] 80th percentile) about a decade older on average than those in poor condition (body condition index [less than or equal to] 20th percentile). Given the growth dynamics of bowheads throughout their maturation process, it seems likely that the association between body condition and cyamid presence may be at least partially associated with the metric that we used to score body condition.

In addition to AGE, the most parsimonious model in Table 1 also included an interaction between AGE and YEAR, which was negatively associated with cyamid presence (Table 1, model 1). The negative slope of YEAR indicates that, with the passage of time, the probability of cyamid presence on harvested bowheads decreases. Given evidence that older bowheads tend to have cyamids present, we speculated that inter-annual variation in the demographic composition of harvested bowheads may be influential. Indeed, since 1981, there has been a pronounced downward trend in the size of bowheads harvested in the fall ([R.sup.2] = 0.56, p = 5.6 x [10.sup.-7], n = 33), but not in the spring ([R.sup.2] = 0.02, p = 0.39, n = 35). A mechanistic explanation for these trends likely involves many factors. One consideration is that the current growth rate of the BCB bowhead population (Givens et al., 2016) makes it plausible that their age distribution is shifting over time toward greater numbers of younger whales. Another possibility concerns the implications of a Barrow Whaling Captains' Association decision to open the fall whaling season later in the year, when air temperatures are cooler and smaller migrating bowheads are more abundant, thereby decreasing the chance of harvesting large bowheads. Inter-seasonal variation (SEAS) was significant and included as part of the most parsimonious model in Table 2. The negative relationship between SEAS and cyamid presence indicates that, as the indicator variable increases from 0 (spring) to 1 (fall), the probability of cyamid presence decreases. Because whales caught during the spring hunts are, on average, longer and older, we surmised that the demography of harvested bowheads was also important at the inter-seasonal time scale. This inter-seasonal variability is also likely to be related to many factors, but Inupiat hunting practices, which differ between the spring and fall, may play a major role. Although some villages tend to harvest larger whales, Barrow, which accounts for a major proportion of our data, tends to harvest smaller bowheads. Given the complexities within this system, including ice dynamics, hunter selectivity, population dynamics, and many other factors, the temporal trends in cyamid presence and whale size should be interpreted with caution until a more detailed analysis can be undertaken.

Ancillary data from our harvest records suggested no apparent trends relating to the abundance of cyamids. Our records did document high cyamid abundance in a bowhead with a spinal abnormality; similarly, it has been reported that humpback whales (Megaptera novaeangliae) with severe spinal abnormalities and very poor body condition became heavily infested (Osmond and Kaufman, 1998; Felix et al., 2007). However, few other harvest records indicated elevated abundance of cyamids on bowheads in poor body condition. Moreover, contradicting reports of young, healthy, or small whales with higher cyamid abundance also existed in our records. Other than associations with skin depressions and deep wounds, meaningful patterns associated with cyamid abundance were not apparent from our harvest reports. Typically, most harvested bowheads had few or no cyamids present and were generally in very good condition (Philo et al., 1993; Willetto et al., 2002; Stimmelmayr, 2015). Another consideration is that, given the overall good health of this population, low cyamid abundance per whale, and low cyamid prevalence, successful parasite transmission from host to host may simply be a rare event. Finally, other cyamid species have been shown to have varying levels of cold tolerance (Best, 1979). Perhaps because bowheads are the only mysticete that consistently winters in Arctic waters, this species (C. ceti) may be close to its physiological limit and at the edge of its ecological niche.

Because cyamids are difficult to observe and document on free-ranging whales (Rowntree, 1983), few systematic studies of these parasites exist. This investigation suggests that most BCB bowheads do not carry cyamid parasites, and those that do tend to have low cyamid abundance. Our models also indicate that demographic variables (e.g., age and size), body condition, and temporal variables (e.g., year and season of harvest) are significant predictors of cyamid presence. Further investigations are needed in order to disentangle the complexities of ice dynamics, population ecology, and hunting selectivity from the basic ecology of bowheads and their cyamid parasites. For example, subadult (post-weaning) bowhead body condition has been shown to improve as sea ice cover declines (George et al., 2015). Bowhead productivity may increase in response, thereby increasing the chances of cyamid transmission from host to host through density-dependent effects. Further complicating matters are the effects of environmental change within Arctic marine ecosystems, which are anticipated to continue into the future (Moore and Laidre, 2006; Moore et al., 2014). Maritime traffic and industrial development are anticipated to increase in response to declining sea ice cover (Reeves et al., 2012) and will likely lead to higher anthropogenic disturbance levels.

Whether, how, and to what extent bowheads will respond to these and other changing environmental stressors remains to be seen. There is reason to believe that, given the bowhead's longevity and evolutionary strategy of "weathering" environmental variability (Burns, 1993; George et al., 1999), its response(s) to environmental perturbations may not be readily detectable. Cyamid prevalence and abundance appear to be associated with demographic, physiological, or anthropogenic factors, which are also subject to change with the environment. Visual examinations for cyamids are relatively easy to perform on harvested bowheads. We therefore recommend that similar assessments of cyamid prevalence and abundance be conducted on harvested bowheads and other large whale species in Arctic regions to further develop a basic ecological understanding of these species as part of comprehensive Arctic ecosystem assessment programs (Moore et al., 2014).

(Received 2 March 2016; accepted in revised form 8 June 2016)


We are grateful for support provided by the North Slope Borough, Alaska, for this study. The authors thank the Alaska Eskimo Whaling Commission and the captains of the participating Whaling Captains' Associations from Saint Lawrence Island to Kaktovik for allowing us to examine their whales. We could not have done this research without their cooperation. We are indebted to North Slope Borough staff and the many technicians who have assisted with field examinations over several decades. We would also like to thank Jon Seger and one anonymous reviewer for their constructive comments. All work on bowhead whales presented here was conducted under NOAA/NMFS Permits 814-1899, Permit 17350, and NOAA Marine Mammal Stranding Network Permit #932-1489-00.


Best, P.B. 1979. Social organization in sperm whales, Physeter microcephalus. In: Winn, H.E., and Olla, B.L., eds. Behavior of marine animals: Current perspectives in research. Vol. 3, Cetaceans. New York: Plenum Press. 227-289.

Burnham, K.P., and Anderson, D.R. 2002. Model selection and multimodel inference: A practical information-theoretic approach, 2nd ed. New York: Springer-Verlag.

Burns, J.J. 1993. Epilogue. In: Burns, J.J., Montague, J.J., and Cowles, C.J., eds. The bowhead whale. Special Publication Number 2. Moss Landing, California: The Society for Marine Mammalogy. 745-761.

Felix, F., Haase, B., and Aguirre, W.E. 2007. Spondylitis in a humpback whale (Megaptera novaeangliae) from the southeast Pacific. Diseases of Aquatic Organisms 75(3):259-264.

George, J.C. 2009. Growth, morphology and energetics of bowhead whales (Balaena mysticetus). PhD thesis, Department of Biology and Wildlife, University of Alaska Fairbanks. George, J.C., Bada, J., Zeh, J., Scott, L., Brown, S.E., O'Hara, T., and Suydam, R. 1999. Age and growth estimates of bowhead whales (Balaena mysticetus) via aspartic acid racemization. Canadian Journal of Zoology 77(4):571-580.

George, J.C., Follmann, E., Zeh, J., Sousa, M., Tarpley, R., Suydam, R., and Horstmann-Dehn, L. 2011. A new way to estimate the age of bowhead whales (Balaena mysticetus) using ovarian corpora counts. Canadian Journal of Zoology 89(9):840-852.

George, J.C., Druckenmiller, M.L., Laidre, K.L., Suydam, R., and Person, B. 2015. Bowhead whale body condition and links to summer sea ice and upwelling in the Beaufort Sea. Progress in Oceanography 136:250-262.

Givens, G.H., Edmondson, S.L., George, J.C., Suydam, R., Charif, R.A., Rahaman, A., Hawthorne, D., Tudor, B., DeLong, R.A., and Clark, C.W. 2016. Horvitz-Thompson whale abundance estimation adjusting for uncertain recapture, temporal availability variation and intermittent effort. Environmetrics 27(3):134-146.

Kaliszewska, Z.A., Seger, J., Rowntree, V.J., Barco, S.G., Benegas, R., Best, P.B., Brown, M.W., et al. 2005. Population histories of right whales (Cetacea: Eubalaena) inferred from mitochondrial sequence diversities and divergences of their whale lice (Amphipoda: Cyamus). Molecular Ecology 14(11):3439-3456.

Lubetkin, S.C., Zeh, J.E., Rosa, C., and George, J.C. 2008. Age estimation for young bowhead whales (Balaena mysticetus) using annual baleen growth increments. Canadian Journal of Zoology 86(6):525-538.

Moore, M.J., Bogomolni, A., Bowman, R., Hamilton, P.K., Harry, C.T., Knowlton, A.R., Landry, S., Rotstein, D.S., and Touhey, K. 2006. Fatally entangled right whales can die extremely slowly. Proceedings Oceans'06 MTS/IEEE, 18-21 September 2006, Boston, Massachusetts. 3 p.

Moore, S.E., and Laidre, K.L. 2006. Trends in sea ice cover within habitats used by bowhead whales in the western Arctic. Ecological Applications 16(3):932-944.[0932:TIS1CW]2.0.CO;2

Moore, S.E., Logerwell, E., Eisner, L., Farley, E.V., Jr., Harwood, L. A., Kuletz, K., Lovvorn, J., Murphy, J.R., and Quakenbush, L.T. 2014. Chapter 11: Marine fishes, birds and mammals as sentinels of ecosystem variability and reorganization in the Pacific Arctic Region. In: Grebmeier, J.M., and Maslowski, W., eds. The Pacific Arctic region: Ecosystem status and trends in a rapidly changing environment. 337-392.

Nerini, M.K., Braham, H.W., Marquette, W.M., and Rugh, D.J. 1984. Life history of the bowhead whale, Balaena mysticetus (Mammalia: Cetacea). Journal of Zoology 204(4):443-468.

Osmond, M.G., and Kaufman, G.D. 1998. A heavily parasitized humpback whale (Megaptera novaeangliae). Marine Mammal Science 14(1):146-149.

Pettis, H.M., Rolland, R.M., Hamilton, P.K., Brault, S., Knowlton, A.R., and Kraus, S.D. 2004. Visual health assessment of North Atlantic right whales (Eubalaena glacialis) using photographs. Canadian Journal of Zoology 82(1):8-19.

Philo, M.L., Shotts, E.B., Jr., and George, J.C. 1993. Chapter 8: Morbidity and mortality. In: Burns, J.J., Montague, J.J., and Cowles, C.J., eds. The bowhead whale. Special Publication Number 2. Moss Landing, California: The Society for Marine Mammalogy. 275-312.

R Core Team. 2014. R: A language and environment for statistical computing. Vienna, Austria: R Foundation for Statistical Computing.

Reeves, R., Rosa, C., George, J.C., Sheffield, G., and Moore, M. 2012. Implications of Arctic industrial growth and strategies to mitigate future vessel and fishing gear impacts on bowhead whales. Marine Policy 36(2):454-462.

Rowntree, V.J. 1983. Cyamids: The louse that moored. Whalewatcher: Journal of the American Cetacean Society 17:14-17.

--. 1996. Feeding, distribution, and reproductive behavior of cyamids (Crustacea: Amphipoda) living on humpback and right whales. Canadian Journal of Zoology 74(1):103-109.

Schell, D.M., Rowntree, V.J., and Pfeiffer, C.J. 2000. Stableisotope and electron-microscopic evidence that cyamids (Crustacea: Amphipoda) feed on whale skin. Canadian Journal of Zoology 78(5):721-727.

Schick, R.S., Kraus, S.D., Rolland, R.M., Knowlton, A.R., Hamilton, P.K., Pettis, H.M., Kenney, R.D., and Clark, J.S. 2013. Using hierarchical Bayes to understand movement, health, and survival in the endangered North Atlantic right whale. PLoS ONE 8(6): e64166.

Stimmelmayr, R. 2015. Health assessment of subsistence harvested Bering-Chukchi-Beaufort Seas bowhead whales (Balaena mysticetus): An overview. International Whaling Commission Technical Report SC/66a/E/8.

Willetto, C.E., O'Hara, T.M., and Rowles, T., eds. 2002. Bowhead Whale Health and Physiology Workshop: A report of the workshop held October 1-4, 2001 in Barrow, Alaska. 129 p. OHara_Rowles_2002_Bowhead_whale_health_and physiology_workshop_Oct_2001.pdf

Andrew L. Von Duyke, (1,2) Raphaela Stimmelmayr, (1) Gay Sheffield, (3) Todd Sformo, (1) Robert Suydam, (1) Geof H. Givens (4) and John C. George (1)

(1) North Slope Borough Department of Wildlife Management, PO Box 69, Barrow, Alaska 99723, USA

(2) Corresponding author: Michigan Technological University--SFRES, 1400 Townsend Drive, Houghton, Michigan 49931, USA;

(3) Alaska Sea Grant, University of Alaska Fairbanks--Northwest Campus, Pouch 400, Nome, Alaska 99762, USA

(4) Givens Statistical Solutions, LLC, 4913 Hinsdale Drive, Fort Collins, Colorado 80526, USA

TABLE 1. Ranked logistic regression models estimating the
probability of cyamid presence (n = 126). No models include
variables for both AGE and LEN because of collinearity. Models 1 5
are the five highest ranked models to include the variable AGE.
Models 6-10 are the five highest ranked models to include the
variable LEN. Explanatory variables are shown in the column headers.
Colons indicate interactions. Model 1 (bold) is the highest
performing model.

                                        Estimated coefficient

ID   [AIC.sub.c]   [DELTA][AIC.sub.c]   AGE (1)     LEN (2)    COND

1    111.93#       0.00#                4.157# *    --         --
2    112.73        0.81                 0.024# **   --         --
3    112.75        0.83                 --          --         --
4    113.42        1.49                 0.030 **    --         --
5    113.69        1.77                 2.912       --         --
6    119.13        7.20                 --          13.057 *   --
7    119.46        7.53                 --          0.181 *    --
8    119.47        7.54                 --          --         --
9    121.19        9.26                 --          0.177 *    0.002
10   121.26        9.33                 --          14.668     --

     Estimated coefficient


1    --    --       --                 -0.002# *
2    --    --       --     -0.082 *    --
3    --    --       --     -0.083 **   1.2 x [10.sup.-5] **
4    --    -1.013   --     -0.065      --
5    --    --       --     -0.036      -0.001
6    --    --       --     -           --
7    --    --       --     0.080 *     --
8    --    --       --     -0.081 *    --
9    --    --       --     -0.078 *    --
10   --    --       --     0.011       --

     Estimated coefficient


1    --
2    --
3    --
4    --
5    --
6    0.037 *
7    --
8    9.1 x [10.sup.-5] **
9    --
10   -0.007

(1) Age estimates from stable isotope analyses, corpora counts,
or aspartic acid racemization.

(2) Body length is used as a proxy for age.

** Values significant at [less than or equal to] 0.01;
* significant at [less than or equal to] 0.05.

Note: Model 1 (bold) is the highest performing model are indicated #.

TABLE 2. Ranked logistic regression models estimating the
probability of cyamid presence (n = 497). These models consider LEN
only as an analog for age. Explanatory variables are shown in the
column headers. Colons indicate interactions. Model 1 (bold) is the
highest performing model.

                                        Estimated coefficient

ID   [AIC.sub.c]    [DELTA][AIC.sub.c   LEN (1)   COND       SEX

1#   456.58#        0.00#               0.002#    0.003# *   --
2    459.93         3.35                0.104 *   0.004 *    --
3    460.98         4.40                0.095 *   0.004 *    --
4    461.97         5.39                0.010 *   0.004      --
5    462.78         6.20                0.104 *   0.004 *    --
6    464.84         8.26                0.104 *   0.004 *    -0.011
7    466.36         9.78                --        --         --
8    472.25         15.67               0.102 *   --         --
9    473.13         16.55               --        0.004 *    --
10   473.72         17.14               --        --         --
11   476.83         20.25               --        --         --
12   477.06         20.48               --        --         0.096

     Estimated coefficient


1#   --       -3.143 **#   --       0.212# *   --
2    --       -0.840 ***   --       --         --
3    --       -0.808 ***   -0.014   --         --
4    --       -0.084 ***   --       --         8.5 x [10.sup.-5]
5    -0.192   -0.831 ***   -0.013   --         --
6    0.193    -0.831 ***   -0.013   --         --
7    --       -0.774 ***   --       --         --
8    --       --           --       --         --
9    --       --           --       --         --
10   --       --           -0.026   --         --
11   0.223    --           --       --         --
12   --       --           --       --         --

(1) Length (LEN) used as an index of age.

*** values significant at [less than or equal to] 0.001;
** significant at [less than or equal to] 0.01;
* significant at [less than or equal to] 0.05.

Note: Model 1 (bold) is the highest performing model
are indicated with #.

TABLE 3. Selected case studies of bowhead whales that were harvested
for subsistence in Alaskan waters. Whales are listed in
chronological order beginning with the most recent.

ID       Year     Sex      Length (m)   Age (years)       (1)

15B20    2015    [male]       11.9        no age          ~30

15KK01   2015   [female]      12.8        no age          ~100

14B04    2014   [female]      9.0         no age        > normal

08G01    2008   [female]      14.3        no age        heavily
                                         estimate       infested

04B03    2004    [male]       9.1          ~1.0           ~100

99B14    1999   [female]      14.2         64.0           none

95B09    1995   [female]      17.5         172.0      lots of lice

92B11    1992   [female]      15.0        no age         20-30

82WW01   1982    [male]       17.7         64.9          45-50

76B20    1976    [male]       14.3         39.5         hundreds

ID       Comments

15B20    Barrow. In a scar and immediately behind the blowhole. Few on

15KK01   Kaktovik: Old bomb recovered from lower back contained in a
         large abscess capsule. Dozens of cyamids present in
         "indented" surface area located over abscess capsule.
         Harpooner said that the whale "dove differently"--likely
         compromised by chronic injury. Several chronic internal
         lesions not directly associated with old wound indicated
         general poor health.

14B04    Barrow. Recovered dead in the spring lead at Barrow, this
         whale was struck and lost near Wainwright (190 km southwest
         of Barrow) and drifted north over a period of about four
         days. Many cyamids (0.5 cm to 2.0 cm) were seen scattered
         over the head, body, peduncle, and flukes. Four days is
         likely insufficient time for the cyamids to have
         proliferated. However, they may have dispersed across a
         larger area of the whale's body because of the reduced flow
         rate of water.

08G01    Gambell. The attending commissioner from the Alaska Eskimo
         Whaling Commission related the following observations to G.
         Sheffield: Numerous large patches of cyamids on skin of lower
         body and genital slit. Black skin [epidermis] was reported as
         thin and the mangtak2 tough. Large patches of cyamids on the
         middle lower portion of the body and genital slit. The
         hunters noted that the whale had two 5 cm diameter circular
         "swollen" scars on dorsal region 25-30 cm and 3-4 m anterior
         to peduncle. When first spotted, the whale was "oblivious to
         the approach" of the whaling crew, did not swim, and
         repeatedly dove and surfaced in one place. The whale dove
         normally when it was struck, taking down two floats. But it
         "swam at a slow pace." The description suggests that this
         bowhead was physically compromised and behaved abnormally.

04B03    Barrow: Whale lice, near the eye and along the mouth -100 in
         two groups (at least).

99B14    Barrow: Severely entangled in crab lines through the mouth
         and around the peduncle. Considered to be in poor condition,
         with severe lacerations and gray skin. The examiners did not
         report cyamids on this animal. We reexamined all photographs
         of 99B14 and did not see cyamids.

95B09    Barrow: Whale 95B09 was the largest male measured at Barrow
         in our database and also among the oldest whales recorded. It
         was described as having "lots office," as well as areas of
         the vertebral column with spondylosis, a condition that has
         not been described in other BCB bowheads (Paul Nader, pers.
         comm. 1995).

92B11    Barrow. Many (20-30) cyamids in old, healed, depressed

82WW01   Wainwright: 15-20 cyamids on eroded area on chin. About 30
         larger cyamids in scar.

76B20    Barrow: Hundreds of cyamids covering soft-scarred area on
around   back and genital area.

(1) Qualitative assessments of cyamid abundance are based
on observations recorded by examiners.

(2) Mangtak = Alaskan Yupik term for the epidermis and outer blubber
layers of the whale, which are consumed for food.

FIG. 3. Map of coastal villages in northern and western Alaska where
bowhead whales were examined for the presence of cyamids. Inset
table indicates the approximate number of whales landed in each
village (1973 to 2015).


Kaktovik             114
Nuiqsut               76
Barrow               718
Wainwright           120
Point Lay             2
Point Hope            10
Kivalina              8
Little Diomede        2
Wales                 11
Shaktoolik            1
Savoonga              99
Gambell               85


Please note: Some tables or figures were omitted from this article.
COPYRIGHT 2016 Arctic Institute of North America of the University of Calgary
No portion of this article can be reproduced without the express written permission from the copyright holder.
Copyright 2016 Gale, Cengage Learning. All rights reserved.

Article Details
Printer friendly Cite/link Email Feedback
Author:Von Duyke, Andrew L.; Stimmelmayr, Raphaela; Sheffield, Gay; Sformo, Todd; Suydam, Robert; Givens, G
Article Type:Report
Geographic Code:0ARCT
Date:Dec 1, 2016
Previous Article:ASTIS subset databases expand.
Next Article:Observations of heterospecific courtship behaviour in an isolated population of Ross's Gulls (Rhodostethia rosea).

Terms of use | Privacy policy | Copyright © 2021 Farlex, Inc. | Feedback | For webmasters |