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Age Structure of the Otter (Lutra lutra) Population in England and Wales, and Problems with Cementum Ageing

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Age is an important parameter in understanding population structure and age-dependent processes such as accumulation of contaminants. In the current study, canines and incisors of sub-adult and mature wild otters (Lutra lutra) from England and Wales were sectioned and incremental cementum lines were used as an indication of age. The age structure of the sample population is much younger than some European populations (of 110 otters aged, only 10 were aged four or older). Cementum ageing is useful here in giving a broad indication of age structure, but is imprecise for species which do not exhibit seasonal breeding. Age is likely to be underestimated in most cases.
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IUCN Otter Spec. Group Bull. 27(1) 2010
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A R T I C L E
AGE STRUCTURE OF THE OTTER (Lutra lutra) POPULATION
IN ENGLAND AND WALES, AND PROBLEMS WITH
CEMENTUM AGEING
SHERRARD-SMITH, E., CHADWICK, E.A.
*Cardiff School of Biosciences, Cardiff University, Museum Avenue, Cardiff, CF10 3AX, UK
e-mail: Chadwickea@cardiff.ac.uk
(received 23rd September 2009, accepted 15th
October 2009)
Abstract: Age is an important parameter in understanding population structure and age-
dependent processes such as accumulation of contaminants. In the current study, canines
and incisors of sub-adult and mature wild otters (Lutra lutra) from England and Wales
were sectioned and incremental cementum lines were used as an indication of age. The
age structure of the sample population is much younger than some European populations
(of 110 otters aged, only 10 were aged four or older). Cementum ageing is useful here in
giving a broad indication of age structure, but is imprecise for species which do not
exhibit seasonal breeding. Age is likely to be underestimated in most cases.
Keywords: Age structure; Cementum analysis; Road-traffic casualties; Otter, Lutra lutra
INTRODUCTION
Many conservation goals require an understanding of population age structure,
age-specific reproduction, growth and survival (Bodkin et al., 1997, Harris et al.,
1992, Stoneberg and Jonkel, 1966). A range of methods for ageing wild animals are
described in the literature e.g. size frequencies (Tanaka, 1956), lens weight (Teska
and Pinder, 1986), degree of tooth wear (Brothwell, 1989), and cementum banding
(Castanet et al., 1990); here, we discuss the use of cementum banding in ageing
Eurasian otters Lutra lutra.
Lieberman (1994) describes the biological basis for seasonal cementum
banding. Cementum is a bone-like connective tissue that grows in incremental layers
around the root of teeth. Banding patterns are caused by changes in mineralization and
collagen orientation; these can be caused by nutritional or biomechanical factors that
vary on a seasonal or annual basis. There have been a number of controlled studies
indicating that cementum banding can be used to accurately age mammals including
buffalo (Moffit, 1998), harbour seals (Norgaard and Larsen, 1991), stoat (King,
1991), and badger (Harris et al., 1992). In Eurasian otters taken from the wild in
Denmark and Norway, a single dark line is produced annually (Heggberget, 1984).
IUCN Otter Spec. Group Bull. 27(1) 2010
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Here, we present the results of cementum banding analysis of otters Lutra lutra
found dead in England and Wales between 1992 and 2004. We discuss the age
structure of the animals found, and potential errors implicit in using cementum
analysis to age Lutra lutra from the UK.
ANIMALS, MATERIAL AND METHODS
Sample collection
Since 1992, otters found dead in England and Wales have been sent for post
mortem examination to Cardiff University. During examination, data are collated
following a standard protocol (www.otterproject.cf.ac.uk) including sex and age-class.
Otters are classified as juvenile where body weight is <2.1kg (females) or < 3kg
(males). Where these weights are exceeded, individuals are categorised as adult if
reproductively mature (baculum length >60mm [males], signs of uterine thickening,
placental scarring, previous or current lactation, or pregnancy [females]), or as sub-
adults if reproductively immature.
Following post mortem examination, skulls are retained and cleaned. For this
study, teeth were taken from 143 individuals (87 male, 56 female), for cementum
analysis. Newly erupted teeth (those with a thin walled root and a large apical
foramen) were counted, but omitted from cementum analysis. For carnivores, it is
recommended to use lower canines for cementum analysis (Matson, 1981). Here, the
lower left canine was taken where available (n = 131) or the lower right where the left
was not available (n = 12). In order to assess reproducibility of results for left and
right canines, and for different tooth types, groups of teeth from the same individual
were taken as follows; upper left incisor, left canine, and right canine (n = 21), lower
left canine and lower right canine (n = 3).
Cementum analysis
Tooth preparation and cementum analysis was undertaken by Matson’s
Laboratory, USA, following their standard procedure (http://www.matsonslab.com).
A standardized analysis model specific to otters and the tooth type was then applied to
count annuli. Matson’s Laboratory based the age model for Eurasian otters on that of
North American river otters (Lontra canadensis) so assume dark cementum rings are
deposited in winter and assume a birth date of April. A reliability grading was given
to each tooth, ‘A’ where histology was good, ‘B’ where it was reasonable. ‘X’ was
given where ageing was not attempted due to cementum damage.
Data analysis
Preliminary analysis was carried out to test whether the subset of cementum
aged animals was representative of the post mortem dataset as a whole (n = 515
[males], n = 348 [females] to June 2008). Otters are sexually dimorphic so sexes were
analysed separately. Juveniles were eliminated from the comparison because newly
erupted teeth were excluded from the aged data set. Analysis of Covariance using a
General Linear Model was applied to test whether the aged animals differed from the
non-aged animals in terms of animal size (weight, total length, tail length, femur, tibia
and fibula length and weight) and condition (Wt/L), and showed no significant
difference.
Analysis of Covariance using a General Linear Model was applied to test
whether there were differences in the age structure of the male and female
populations. All analyses were performed using Minitab 15.
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RESULTS
Age Ageing was not possible for 45 teeth, representing 33 individuals (9 females and
29 males). This was due to poor histology, resulting from the use of detergents
containing bleach to clean the teeth, prior to the decision to perform cementum
analysis. Histological sections were good (graded A or B) for 62 male and 48 female
otters (e.g. Figure 1); data from these were used in further analysis.
Reproducibility of cementum ageing for different canines from the same
animals (n = 19 pairs) was 78.95% (fifteen aged the same, three cases with a one year
difference, and one case with a two year difference). Matched pairs of incisors and
canines (n = 14) showed a lower reproducibility of 57.1% (eight were aged the same,
four aged one year different, and two aged two years different).
The age distribution was skewed towards younger animals, with the majority of
otters aged between 0 and 2 years. Only 10 otters were 4 years or older, and the
maximum age recorded was 8 yrs (Figure 2). There was no significant difference
between the age structures of males and females (F ratio = 0.76, df = 1, P = 0.398).
DISCUSSION
Our data suggest a skewed age distribution, with most otters being less than
three years of age, and the most frequent age being just one year old. There was no
significant difference in age distribution between males and females. A similarly
young age structure was found in Shetland, where otters were most commonly
recorded in their first year (Kruuk, 2006). In Germany, the most frequent age class
was again 1 year old, but otters aged 2-10 were also frequently found, and the
maximum age was 16 years (from a sample size of 225) (Ansorge et al., 1997). Hauer
et al. (2002a) also found many otters in age classes 3, 4-9 and >9 years (maximum age
found is not given).
Interestingly, Hauer et al. (2002b) found the bulk of reproductively active
females in Germany were 6-9 years of age. In our study we had only two females
aged 6 or over. This suggests either that the age distribution presented here does not
mirror that of the actual population, females breed at an earlier age in England and
Wales than those in Germany, or that many otters are killed prior to peak reproductive
age in England and Wales.
The majority of otters in this study were killed by traffic (94%). This is likely
to be biased, because road kills are more detectable than natural deaths. However, this
represents one of the highest proportions in Europe and can be compared to 36.1% in
Norway (Heggberget, 1991); 69.9% in Germany (Hauer et al., 2002a); 64% in Upper
Lusatia, Germany (Ansorge et al., 1997) and 83% in south-west England (Simpson,
1997). It is possible that the age structure differs between our sampled population and
the true population. Hauer (2002a) found that among otters sampled from road traffic
mortalities, the most common age was 3 years, whereas among otters killed by
disease or by hunting both young (<1) and old (>9) otters were more commonly found
than intermediate ages. We have insufficient data for non road traffic mortalities to
make a similar comparison.
IUCN Otter Spec. Group Bull. 27(1) 2010
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A
B
Figure 1. Cementum banding in Eurasian otter aged 6; A root of otter tooth; B enlarged version of
cementum showing 6 (discontinuous) annuli
IUCN Otter Spec. Group Bull. 27(1) 2010
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0
5
10
15
20
25
30
012345678
Age (Years)
Number of otters
Males Females
Figure 2. Age distribution of otters
In addition to potential bias associated with sample collection, it is also
important to recognise problems associated with cementum analysis. In a study of 10
known-age captive otters, 1-11 years old, Yom-Tov et al. (2006) described the annuli
as irregular and discontinuous, and maximum counts underestimated age by a year in
half the animals examined. This may be because animals in captivity are less exposed
to seasonal variation in climate and diet, but for wild North American river otters
Lontra canadensis banding patterns are also described as indistinct, with peripheral
compression of annual bands causing difficulty in ageing (Matson, 1981). In our
study, ageing was not possible for 23% of individuals, but this failure rate was largely
due to unsuitable cleaning protocols used at a time when cementum analysis was not
planned.
Where histology is clear and counts can be made, interpretation to infer age
remains subject to further error. Interpretation relies on two assumptions; an assumed
season of band formation, and an assumed birth date. In most analyses it is assumed
that a thin dark band of cementum forms in winter, and a broader, lighter band forms
during the growth seasons of spring and summer (Matson, 1981). Grue and Jensen
(1978) found that in Danish otters (Lutra lutra) incremental lines develop in winter-
spring. In analyses of otter teeth from Norway, Heggberget (1984) found signs of
dark-staining cementum in the process of deposition in all months from February to
July, suggesting that band formation is variable. Here, we assume winter band
formation, but known-age animals have not been used to test this in the UK, and error
in this assumption could cause errors in ageing.
If we do assume winter band formation, the number of dark bands equates to the
number of winters an otter has experienced since eruption of the adult teeth. To reach
a more accurate assessment of age it is necessary to add the number of months
survived prior to first band formation, and following the last band. The latter can be
readily estimated using time elapsed between the most recent winter and the month of
death (recorded when the animal was found). The former is a summation of two
periods; (i) the period between birth and eruption of the adult teeth (in Eurasian otters,
ca. 5 - 5.5 months (Heggberget, 1996)), and (ii) the period between eruption of the
adult teeth and the first band-producing winter. Here, an assumed birth month must be
used. In species or areas where reproduction is seasonal, the number of months
IUCN Otter Spec. Group Bull. 27(1) 2010
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between eruption of the adult teeth and the first winter can be readily estimated. For
example, if an animal was found dead in April 2009, and one band was recorded, we
would assume that it was born the previous April (2008), allowing adult teeth to
develop by September-October 2008, and the first band to form in winter 2008-09.
However, if birth date is unknown, the estimated age varies: it could have been born
as late as June 2008 (adult teeth formed early winter 2008-09, band formation that
same winter, at 6 months old, and died four months later), or as early as July 2007
(adult teeth not developed until mid-winter 2007-08 therefore not banded until its
second winter, at 17 months old, and died four months later). Here, age would be
recorded as one year, but the actual age might be anything from 10 to 21 months, i.e.
the given age could be a 2 month overestimate or 9 month underestimate.
Seasonality of reproduction in Eurasian otters has been reported in some areas,
for example Kruuk et al. (1987) observed a breeding season for Shetland otters in
June, whilst Heggberget and Christensen (1994) described a late summer-autumn
breeding season for otters in Norway. However in England and Wales it is generally
stated that reproduction can occur in any month of the year, with no distinct
seasonality (Mason and MacDonald, 1986). Stephens (1957) reports estimated dates
of birth for 134 reliable instances on which cubs were sighted spread evenly
throughout the year. Data collected by CUOP also shows no evidence of seasonality
in reproduction, with pregnant females found throughout the year (Chadwick and
Sherrard-Smith, 2010). Given the lack of reproductive seasonality among our sample
population, the potential errors associated with using an assumed birth month may be
considerable.
When calculating the potential errors associated with using an assumed April
birth month, birth in January-March or July-December lead to an underestimate of
age, while birth dates in May or June lead to an overestimate of age. Otter age is
therefore more likely to be under- than over-estimated. Where, as in this study, the
majority of animals are aged at <2 years old, a potential 9 month error in age may be
problematic; using morphometry, reproductive status and observations such as tooth
wear may give a more biologically relevant estimate of age than cementum ageing.
Acknowledgements - Thank you to the Environment Agency for funding the Cardiff University Otter
Project. Thank you also to Eleanor Kean of her contributions and support. Thank you for the translation
of the French and Spanish abstracts by Muriel Alix and Sonia Valladares respectively.
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RÉSUMÉ
TITLE
L’âge est un paramètre important pour comprendre la structure d’une population ainsi
que les procédés dépendant de l’âge comme l’accumulation de contaminants.
Dans cette étude, les canines et incisives, prélevées chez des subadultes et adultes de
loutres sauvage (Lutra lutra) de populations anglaises et galloises, ainsi que les
céments dentaires, ont permis de déterminer l’âge des individus. La structure de l’âge
de cet échantillon de population est beaucoup plus jeune que pour certaines
populations européennes (sur 110 individus, seulement 10 étaient âgés de 4 ans ou
plus).
Le cément dentaire donne une approximation de la strucutre de l’âge mais n’est pas
assez précis pour des populations qui ne montrent pas de période de reproduction
saisonnière.
IUCN Otter Spec. Group Bull. 27(1) 2010
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RESUMEN
TITLE
La edad es un parámetro importante para entender la estructura de una población y los
procesos dependientes de la edad como son la acumulación de contaminantes. Los
caninos e incisivos de individuos subadultos y adultos de nutrias salvajes (Lutra lutra)
de Inglaterra y Gales fueron examinados por las líneas de incremento del cemento, las
cuales son utilizadas como un indicador de la edad en muchas especies de mamíferos.
La estructura de edad de la población de muestra es mucho más joven que algunas
poblaciones europeas (de 110 nutrias estudiadas, sólo 10 de ellas tenían 4 años o
más). El envejecimiento del cemento dental aquí es útil para obtener una amplia
visión de la estructura de edad, pero es imprecisa para especies que no exhiben una
reproducción estacional. La edad es probable que sea subestimada en muchos casos.
... Comprehensive studies on the microstructure, elemental composition, and mechanical properties of dental tissues in the Lutrinae are scarce. Previous studies on teeth have focused on aspects such as tooth morphology and age determination using annual growth layers in cementum [21,23], tooth wear patterns [24], tooth morphotypes in cheek teeth [11], and congenital dental abnormalities [25]. Patterns of enamel organization were investigated in carnivorans by the authors in [26,27], including some Mustelidae. ...
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Dead specimens provide valuable data for the conservation of threatened species, allowing investigations of mortality, health conditions, and demographic parameters. The Eurasian otter (Lutra lutra) is a semiaquatic carnivore listed as endangered in Italy. In 2009, we started the first post mortem (PM) study of otters in Italy, through collaborative research between mammal ecologists and veterinary pathologists, using standardized protocols. Twenty-eight otters, mostly collected between 2009 and 2017, were examined. Most otters were males (67%), between 1 and 3 years old (64%), and predominantly in good nutritional condition. Adult males were significantly larger than adult females (p < 0.02), as expected for the species, although both sexes appeared to be smaller than otters examined in Central–northern Europe. The youngest sexually mature female was 3 years old. Road traffic collisions were the major cause of death, especially in young individuals, and mainly occurred in autumn–winter, particularly for females. Investigations of the scene of death contributed to revealing factors forcing otters to travel out of the water and move over the road, suggesting appropriate measures to reduce vehicle collision risk. Other causes of death included blunt chest trauma of uncertain origin, dog and conspecific attacks, or diseases of infectious or non-infectious origin, such as ulcerative gastritis, pleuropneumonia and peritonitis. Other diagnosed diseases included lymphoma. Ecto- and endoparasites were rarely detected, although we report the first documentation of heartworm and Ixodes hexagonus infestation in Italian otters. It is important to continue comprehensive, standardized PM investigations of otters in Italy to define baseline health, biometric and demographic parameters, collect biological samples for comparative analyses, and to reduce road-kill mortality. The present study suggests that the timely collection of carcasses and collaborative and coordinated research efforts are essential for obtaining useful data for the conservation of otters.
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