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1 October 2007 Paternity and mating system in wolverines Gulo gulo
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Knowledge of the wolverine Gulo gulo mating system is limited. In this study, we use 20 microsatellite loci for paternity testing in 145 wolverine offspring with known mothers. Samples were collected during > 10 years in two Scandinavian populations, mainly in connection with radio-telemetry studies and as part of long-term population monitoring. In total, 51% of the offspring were assigned a father. Our results demonstrate that the wolverine exhibits a polygamous mating system as some males were shown to produce offspring with more than one female in a single year. Females often reproduced with the same male in subsequent breeding years, but sometimes changed their partner, potentially as a consequence of a change in the territory-holding male in the area. In the majority of litters, siblings were unambiguously assigned the same father, indicating that multiple paternity is rare. Of 23 breeding pairs, for which telemetry data were available, 20 had overlapping home ranges, suggesting that pair formation generally is consistent with the territories held by wolverine males and females.

The wolverine Gulo gulo is a medium-sized, solitary carnivore occurring at low densities in remote areas of northern tundra and taiga in Eurasia and North America. Wolverines exhibit intra-sexual territoriality and males usually have large territories that overlap those of a few females (Magoun 1985, Banci 1994). The mating system has been suggested to be polygamous based on field observations (Rausch & Pearson 1972), but our knowledge is limited and genetic techniques have not been applied for analyses of parentage or other close relationships.

Previously, wolverines were widely distributed in Scandinavia, however, at the beginning of the 20th century the population declined drastically due to human persecution (Landa et al. 2000). The species received legal protection in 1969 in Sweden and during 1973-1983 in Norway, and the population has since then started to recover slowly. According to records of active natal dens (Landa et al. 1998), the current Scandinavian population size amounts to about 330 individuals in Norway ( and approximately 480 individuals in Sweden ( The majority of the wolverines are found in the mountain range along the border of Sweden and Norway, but a small subpopulation (∼ 80 individuals) is also present in central parts of southern Norway. Genetic studies have revealed low levels of microsatellite diversity in Scandinavian wolverines (Walker et al. 2001), and that the subpopulation in southern Norway is differentiated from the mountain-range population (Walker et al. 2001, Flagstad et al. 2004). Moreover, since 2001 non-invasive genetic techniques are used to aid in population monitoring (Flagstad et al. 2004), with genetic data being directly implemented in national management programmes in Sweden and Norway.

For management of threatened populations to be effective, it must be based on thorough knowledge of the biology of the species. Understanding the mating system can be important as it influences the ability of a population to maintain genetic diversity. With information on parentage and individual mating success, the effective population size may be assessed. In conservation this is essential as the genetic diversity in small populations decreases at a rate dependent on the effective population size. Genetic parentage and relatedness analysis have proven to be useful in studies of social organisation and mating system in wild populations (e.g. Moritz et al. 1997, Girman et al. 1997, Garnier et al. 2001, Constable et al. 2001, Kovach & Powell 2003, Huck et al. 2005). However, the low level of genetic diversity observed in the Scandinavian wolverine population means that the power and resolution of such analysis may be lower than for other species. On the other hand, the fact that a large number of mother-offspring pairs are known from telemetry studies acts in the opposite direction, since the ability to find the biological father is facilitated when maternal genotypes are specified (Marshall et al. 1998). To study the mating system of Scandinavian wolverines, we combine genetic analysis of 20 microsatellite loci in more than 300 individuals, with telemetry data available from 181 of these animals.

Material and Methods

Study Areas and Samples

Samples were from two study areas, one in northern Sweden located in and around Sarek National Park (Kvikkjokk; 67°00′N, 17°40′E) and one around the Snøhetta plateau (62°00′N, 10°00′E) in central southern Norway (Fig. 1). Both areas are characterised by deep valleys, high alpine plateaus and peaks up to 2,000 m a.s.l. Based on the number of recorded natal dens (cf. Landa et al. 1998), the approximate density of wolverines has been estimated at 1.4/100 km2 in the area of Sarek National Park (Persson 2003).

Figure 1

The two study populations are indicated by circles. Hatched areas represent the current wolverine distribution in the Nordic countries.


In northern Sweden, small tissue biopsies for DNA analysis were taken from immobilised animals that were captured for radio-marking in a long-term study of wolverine ecology during 1993-2004 (e.g. Persson et al. 2003). In this study, animals were equipped with implanted radio-transmitters with mortality sensors. Movements of marked animals were monitored by means of traditional radio-tracking from the air and the ground. We sampled 111 offspring of radio-marked females at the age of 2-3 months at rendezvous sites (sites where offspring were left while the female foraged). These offspring were reared in 63 litters by 37 different females, which also were sampled for tissue. Five were litters with three offspring, 38 with two offspring and 20 with a single offspring. In addition, 29 male wolverines of unknown age and relation to other individuals were sampled for tissue. Adult individuals were either darted from helicopter, or in some cases for females, captured at rendezvous sites following snow-tracking.

From the southern Norway population, tissue from 18 offspring was sampled during radio-telemetry and 16 were obtained from offspring legally killed together with their mothers in a programme for carnivore control in conflict areas. The 34 offspring, sampled during 2001-2004, were reared in 16 litters by 15 different females. Three were litters with three offspring, 12 with two offspring and one with a single offspring. All mothers were also sampled (in one case with a faecal sample, otherwise with tissue). In addition, a vast number of additional wolverine samples (33 tissue and approximately 1,200 faecal samples) were collected in southern Norway during 2000-2004 as part of a national population monitoring programme, based on non-invasive sampling (Flagstad et al. 2004, Flagstad et al. 2005). These turned out to represent 80 males, 76 females and nine individuals of unknown sex.

Laboratory Analysis

DNA from tissue was extracted using a phenol: chloroform protocol (Sambrook et al. 1989) and was used for genotyping with 20 microsatellite markers (Table 1). PCR was performed in 10 µl reactions containing 1 × AmpliTaq Buffer, 1.5-3.0 mM MgCl2, 0.2 mM of each dNTP, 3.2 pmol of each primer, 0.3 U of AmpliTaq DNA polymerase (Applied Biosystems) and 20 ng DNA. Initial denaturation at 94°C for three minutes was followed by 32-34 cycles of amplifications with 94°C for 30 seconds, 52-58°C for 30 seconds and 72°C for one minute, and a final extension at 72°C for 10 minutes. For Lut604 a touch-down program was used; three minutes at 94°C, 20 touch-down cycles with 30 seconds at 94°C, 30 seconds at 60°C decreasing 0.5°C each cycle, and one minute at 72°C, followed by 23 cycles of 30 seconds at 94°C, 30 seconds at 50°C, and 72°C for one minute. Prior to 2003, PCR products were run on an ABI 377 instrument (Applied Biosystems, Foster City, CA, USA). From 2003 and onwards all genotyping were performed using a MegaBACE 1000 capillary instrument (Amersham Biosciences). Consistency in allele scoring on the different instruments was secured through careful calibration where several wolverine samples were analysed on both machines.

Table 1

Number of alleles (A) and observed and expected heterozygosity (Hobs and Hexp) in the studied wolverine populations.


In all microsatellite analyses from faecal DNA we applied a multiple-tube approach requiring a minimum of three unambiguous amplification results to accept a homozygous genotype. Moreover, both alleles had to be observed at least twice for a heterozygous genotype. Details on the procedure of DNA extraction, microsatellite genotyping, interpretation and molecular sexing from wolverine faecal samples are provided in Hedmark et al. (2004) and Flagstad et al. (2004).

Population Genetic Analysis

Allele frequencies were calculated separately for each population using GIMLET 1.3.1 (Valière 2002). In northern Sweden, allele frequencies were estimated from individuals sampled as adults (N  =  69) to avoid biases towards related individuals. In southern Norway, the estimate was based on all individuals except the 34 known offspring. We tested for departure from Hardy-Weinberg equilibrium (HWE) and for linkage disequilibrium using the GENEPOP 3.4 software (Raymond & Rousset 1995). Sequential Bonferroni correction (Rice 1989) was applied for multiple tests.

Paternity Analysis

Paternity assignments were based on paternity tests performed in CERVUS 2.0 (Marshall et al. 1998) and on relatedness estimates between pairs of individuals calculated in KINSHIP (Goodnight & Queller 1999). CERVUS uses the principles of Mendelian inheritance and the population allele frequencies to determine which male, from a pool of candidates, is the most likely father. The program uses simulations to define a critical value of the log-likelihood (LOD) difference between the two most likely candidates. However, since the accuracy of these critical values relies on the assumption that no relatives are present, which is likely to be the case in our populations, we applied a number of other criteria to assign paternity. Each criterion is explained in detail below.

Parameters in CERVUS were specified to allow a 1% genotyping error rate, and varying proportions of males sampled in different areas and during different time periods (depending on sampling). The number of animals captured each year in northern Sweden increased progressively during the course of the study and the proportion of sampled males was therefore higher in later years. Also, the central parts of our study area in northern Sweden were more intensively monitored. Accordingly, offspring in northern Sweden were divided into four groups: core area 1993-1998, core area 1999-2004, periphery 1993-1998 and periphery 1999-2004. For these groups we estimated that 55, 85, 25 and 60% of the male population was sampled, respectively. These estimates were obtained by assuming that all parts of the study area in northern Sweden were inhabited by wolverines and that male home ranges (100% minimum convex polygon; MCP) were non-overlapping. The study area (core and periphery, respectively) was divided by the average size of a male home range in northern Sweden (400 km2; J. Persson, unpubl. data) to obtain the number of males expected in each area. The number of sampled males present in each area a given year (as known from telemetry) was divided by the number of males expected to be present. The obtained proportions were then averaged over the years within each of the two time periods. In southern Norway, the estimated proportion of males sampled (80%) was based on population size estimates (Flagstad et al. 2005).

In paternity tests, the mother was always given, and all males sampled by either tissue or faeces in the respective population were considered as potential candidates, with the exception of males known to have died before mating and known male siblings of the analysed offspring. Moreover, as most wolverine males do not reach sexual maturity before two years of age (Rausch & Pearson 1972, Banci & Harestad 1988), males of known age were not considered as possible fathers until they were in their third year of life. Also in CERVUS, allele frequencies were specified to avoid biases towards related individuals. Thus, allele frequencies used for northern Sweden were based on individuals sampled as adults (N  =  69), and for southern Norway on all sampled individuals except the 34 known offspring.

A genetic relatedness index, r, between pairs of individuals was calculated using KINSHIP 1.3.1 (Goodnight & Queller 1999), based on the method of Queller & Goodnight (1989). The index is calculated from population allele frequencies and assesses the proportion of alleles between two individuals that are identical by decent. The r-value ranges from -1 to 1, and should be 0.5 for first order relatives (i.e. parent-offspring pairs and full siblings), 0.25 for second order relatives and zero for unrelated pairs. Given the low genetic diversity of Scandinavian wolverines and the relatively limited number of markers available, r is likely to show a wide distribution around the expected value. Based on the observed allele frequencies from each population, we generated 1,000 pairs each of unrelated individuals, half siblings and parent-offspring to obtain the expected distributions. The distribution of r for parent-offspring pairs was also obtained for known mother-offspring pairs in northern Sweden and southern Norway, respectively.

Paternity Assignment

To assign a male as the father of offspring, we applied four criteria: 1) the LOD-score obtained in CERVUS had to be 3.0 or more; 2) the r-value between the male and the offspring had to exceed the cut-off value at which 95% of 1000 simulated parent-offspring pairs fell; 3) no more than one mismatching allele was accepted among mother-offspring-father trios (allowing one mismatching allele can be justified by the fact that genotyping errors are difficult to completely avoid, especially in analysis of faecal DNA); 4) a male was not assigned paternity if his r-value to the mother exceeded a cut-off value at which 95% of 1000 simulated unrelated pairs fell. The last criterion was included to reduce the risk that a (unknown) brother or uncle, or other male relative, would be incorrectly assigned paternity. Moreover, if more than one male fulfilled all criteria the one with the highest LOD-score was assigned paternity, unless for a few exceptions where telemetry data and/or relatedness analysis suggested that the male with the second highest LOD-score was more likely. In such cases paternity was not assigned; these cases are described in detail in Appendix III.


Average heterozygosity across all loci was 0.52 and 0.45 for northern Sweden and southern Norway, respectively (see Table 1). The number of alleles per locus ranged within 2-6 in both populations with a mean of 3.45 in northern Sweden and 3.40 in southern Norway (see Table 1). This level of genetic variation is comparable to what has previously been observed among Scandinavian wolverines (Walker at al. 2001, Flagstad et al. 2004), but is lower compared to wolverines in several regions of North America (Kyle & Strobeck 2001, 2002). In northern Sweden, all loci were unlinked and in HWE. In southern Norway, one locus, Mvis075, deviated significantly from HWE and 21 of 190 pairs of loci appeared to be linked. The non-random association observed in Norway was probably caused by chance events typical of small populations and/or recent admixture.

The range of simulated r-values within each relatedness category (unrelated, half siblings and parent-offspring) overlapped with that of other categories (Fig. 2), reducing the ability to distinguish between different categories. Nevertheless, since 95% of parent-offspring pairs fell above an r-value of 0.27-0.28 in the two populations and 95% of unrelated individuals fell below 0.31, there was potential to distinguish between these categories. The distribution of observed relatedness values for known mother-offspring pairs in northern Sweden was similar to that obtained from simulations, although slightly skewed towards lower values (Fig. 3). The distribution obtained for the limited number of mother-offspring pairs in southern Norway (N  =  34) was wide and irregular (see Fig. 3).

Figure 2

Distribution of relatedness values for 1000 simulated pairs of unrelated individuals, half siblings and parent-offspring generated based on observed allele frequencies in northern Sweden. The allele frequencies observed in the southern Norway population provide a similar distribution (graph not shown).


Figure 3

Distribution of relatedness values for 1000 simulated parent-offspring pairs and for known mother-offspring pairs in northern Sweden (N  =  111) and southern Norway (N  =  34).


Paternity Assignments

With the set of 20 microsatellites and the allele frequencies observed in each population, the total exclusionary power for the second parent was 0.9981 in northern Sweden and 0.9976 in southern Norway. Paternity was resolved for 74 of the 145 offspring (51%; Table 2). For 50 of these offspring only one male fulfilled the assignment criteria. For the remaining 24, the male that showed the highest LOD-score among two or more that fulfilled the criteria was assigned. In northern Sweden paternity was resolved in 57 cases with 14 different males being assigned as fathers (Appendix I). These 57 offspring were reared in 36 litters by 23 different females. Eight of the 14 assigned males reproduced with more than one female, six males with two females and two with three. There were six occasions where one male reproduced with two different females in the same year. In southern Norway, paternity could be resolved for 17 offspring of seven different females (see Appendix I). All southern Norway females reproduced with different males. The only female for which two litters were sampled reproduced with the same male.

Table 2

Summary of paternity assignments. Data is shown separately for each temporal/spatial group in northern Sweden. Dubious cases are explained in detail in Appendix III.


Telemetry data revealed that breeding male and female home ranges overlapped in 20 out of 23 cases, with home range borders located within 2-5 km from each other in the remaining three cases. The home ranges of males breeding with different females generally overlapped with each of the females' ranges (Fig. 4).

Figure 4

Spatial distribution (100% MCP home ranges) of three reproductive females and the male who were assigned paternity to their offspring, illustrating that the male home range fully or partly overlap those of the females. In 1999 the male reproduced both with F9540 and F9995 whereas in 2001 he reproduced with both F9995 and F01142.


Females often reproduced with the same male in subsequent breeding years. Only two out of 11 females that produced more than one sampled litter in which paternity was resolved bred with two different males. However, if data from females with at least one litter with resolved paternity and at least one with unresolved paternity was also included, and assuming that the father in the latter case was different from the former, eight out of 13 females bred with different males (Appendix II). Two females (J9647 and J9651) were shown to breed with a new male although their previous breeding partner was still alive according to telemetry. Moreover, in one of these cases the first male still had a home range that partly overlapped with that of the female.

Multiple Paternity

A single male genotype could in all cases explain the paternal alleles observed among siblings within litters. However, the possibility to detect multiple paternity by counting paternal alleles was limited in our study as there were only eight litters with three offspring. Moreover, the number of alleles at each locus was limited. However, a possible case of multiple paternity was indicated from a litter with incomplete paternity assignment. In this litter, one offspring (J9646) was assigned a father, but neither this nor other candidate males matched its sibling. The r-value for those potential half-siblings was 0.40, which was within the range of both half- and full siblings.


Our study provided conclusive evidence for a polygamous mating system among wolverines (cf. Rausch & Pearson 1972). If reproduction in different years was taken into account, eight of 14 males that were assigned paternity in northern Sweden bred with more than one female. Moreover, eight of 13 females of which more than one litter was sampled (and where paternity was resolved in at least one) bred with more than one male. Partner shift was potentially a consequence of change of the resident male in the area. In general, when telemetry and genetic data was combined, breeding pairs were found to have overlapping territories.

In populations with polygamous mating, the effective population size may be reduced relative to a monogamous population with the same number of breeding pairs (Frankham et al. 2002). However, the difference between the number of breeding male and female wolverines appears to be relatively small. No male was found to breed with more than two females within a single year or with more than three females across all years. In northern Sweden during 1999-2004 (i.e. when a large proportion of all paternities were resolved) the observed male-to-female ratio of reproducing adults was 0.84. Note, however, that only offspring that survived until the age of 2-3 months were sampled. At this time, an average of 37% of females in the area had offspring, while an average of 53% was confirmed reproducing and most adult wolverine females are presumed to mate every year (Persson et al. 2006). Therefore, our analysis was likely to underestimate the number of females mated by a specific male each year.

Male wolverines defend territories that overlap those of a few females but territories are non-overlapping within sexes (Magoun 1985, Banci 1994). Given that the sex ratio in wolverine populations appears to be about 50∶50 (Flagstad et al. 2004), this suggests that there is a fraction of males without defined territories. Thus, there may be stray males that mate with females within the territories of other males. If this is the case, one should expect to find litters fathered by a different male than the one holding the territory. However, no such observations were made as judged from cases where telemetry data were available. This could be explained by low mating success among stray males. Intraspecific predation (infanticide) is known to be an important cause of juvenile mortality among wolverines (Persson et al. 2003). Thus, another potential explanation might be that offspring fathered by stray males face increased intraspecific mortality from infanticide before they are sampled.

Multiple paternity is known to occur in several mustelids (Yamaguchi et al. 2004, Carpenter et al. 2005, Holland & Gleeson 2005). Multiple paternity is usually detected by counting paternal alleles in litters of three or more offspring (e.g. Say et al. 1999, Burton 2002, Morrison et al. 2002, Solomon et al. 2004). Likelihood based paternity tests may also be used, as assignments of different fathers to siblings in the same litter are indicative of multiple paternity (Burton 2002, Haynie et al 2003, Winters & Waser 2003, Burland et al. 2004). However, data from our study indicate that multiple paternity, if it occurs, is a rare phenomenon among Scandinavian wolverines. We detected only one potential litter, among a total of 32 (3%), in which multiple paternity may have occurred. This is lower than the incidence reported for other mustelids; in badgers Meles meles multiple paternity was observed in five of 31 examined litters (Carpenter et al. 2005), in mink Mustela vison in all of six litters (Yamaguchi et al. 2004) and in stoat Mustela erminea in one of five litters (Holland & Gleeson 2005). It can be hypothesised that the low frequency of multiple paternity in wolverines should be seen in relation to their solitary lifestyle, low population densities and strong male territoriality.

Relatively few loci can provide sufficient resolution for parentage tests at the level of genetic variation seen in outbred mammal populations (e.g. Say et al. 1999, Hughes et al. 2003). However, the ability to distinguish between orders of relatives (e.g. half- and full siblings) decreases rapidly with lower heterozygosity (Blouin et al. 1996, Blouin 2003). As a result of the low genetic variation in our study populations, the r-values showed a large overlap between different classes of relatives (see Fig. 2) and could not readily be used to separate first and second order relatives. For this to become possible, extended marker sets would be needed. Paternity assignment was assisted by our ability to define a refined list of candidate males as provided by telemetry data (e.g. age, year of death and other relationships). The lack of such data from the population in southern Norway likely explains why the ability to unambiguously infer paternity was lower in this population.


financial support was obtained from the Norwegian Directorate for Nature Management, the Swedish Environmental Protection Agency and WWF Sweden. Thanks to the Conservation Genetics group at the department of Evolutionary Biology, Uppsala University, for helpful discussion.



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Appendix I

Appendix I

Offspring for which paternity was resolved, sorted after their mothers. LOD-score for the assigned father and relatedness (r) values for mother-offspring (M-O), father-offspring (F-O) and mother-father (M-F) are provided. The study area in northern Sweden was divided into central part (core) and periphery (perip).


Appendix II

Outcome of the paternity tests for each litter. When a father could not be assigned, the male is marked as unknown (unkn.). The potential case of multiple paternity is indicated in italics.


Appendix III

Supplementary Material

A few dubious cases of paternity (mainly inconsistent observations from genetics and telemetry) were encountered and data from these cases were not included in further analyses. A detailed account for all these cases is given below.

The offspring J01140 had two candidate males showing significant LOD scores as potential father (J00120, LOD  =  4.82; J9766, LOD  =  3.90). However, we did not assign the male with the highest LOD-score as father since J00120, equipped with a radio transmitter, was never observed closer than 28 km to the outermost range of the territory of J9870, the mother of J01140. In contrast, J9766 had overlapping territory with J9870. J9766 was unambiguously assigned paternity to all other offspring of J9870 (both older and younger than J01140). In addition, relatedness analysis revealed that J00120 and J9766 were closely related (r  =  0.56), J00120 could therefore potentially be a brother or an uncle to J01140, which would explain why he appeared as a likely candidate.

In a similar case, J03131 was not assigned a father because the second best candidate, J9766 (LOD  =  5.01), appeared more likely than the first candidate, J9880 (LOD  =  5.59). J9766 and J03131's mother (J01130) were known to have overlapping territories, while J9880 remained in the area where he was born, 30-40 km away from J01130's territory, until March in the year of mating. Radio-contact with J9880 was lost in March, probably as a result of dispersal. It seems unlikely that he dispersed 30-40 km and then immediately, as young (two years old) and inexperienced, was able to mate within the territory of an older well-established male. Moreover, J9880 was closely related to J9766 (r  =  0.61).

For a third offspring (J03170), the male J01123 was not assigned paternity although he fulfilled all criteria. However, from telemetry data he was known to be dispersing from his previous area and to be > 100 km from the territory of J03170's mother (J03171) when radio-contact with him was broken just before the actual breeding season. Moreover, J01123 was closely related to J9991 (r  =  0.61) who was assigned as the father to J03170's sibling in the same litter. J9991 came out as the second most likely candidate for J03170 although there was one mismatching loci and a low LOD-score (1.46). The r-value between J03170 and J9991 was also low (0.19). However, when re-running the paternity test and relatedness analysis without providing a genotype for J03170 at the mismatching loci, it appeared as if that particular mismatch had a strong effect both on LOD-score and r-value as the results obtained now were within the requirements for assignment (LOD  =  4.04 and r  =  0.31). In this case, we did not assign J9991 as the father to J03170, but neither did we consider it to be a likely case of multiple paternity.

For offspring J9655, J02164, J01145 and JJ03172, paternity could not be assigned although the male with the highest LOD-score appeared likely (as judging from father assignments of their siblings and overlapping male and female territories), due to the r-value between the respective offspring and the male being slightly below the required cut-off value. In each of these cases the male fulfilled the criteria for the particular offspring's siblings and was assigned for those.

Finally, if the pattern of paternity allocation for siblings within litters was dubious in a such way that it appeared as if the siblings were fathered by a male with a similar genotype (e.g. if the most likely male for one sibling appeared as the second or third most likely for the other siblings and vice versa), paternity was not assigned to any of the siblings even if one or more could have been assigned a father according to the criteria. This was done because such a pattern may indicate that the siblings in the litter were fathered by the same male, but that he was not sampled. In southern Norway, paternity of six offspring (R019, Ind170, R011, V009, V010 and V015) in four different litters was not assigned although at least one male fulfilled the assignment criteria because the pattern of paternity allocation within the litters indicated that the offspring could be full-siblings fathered by a non-sampled male.

Appendix Table 1. Details on all offspring included in paternity tests. The information is sorted in the order of group, mother and offspring birth year. All candidate males with LOD ≥ 3.0 are shown. If there is more than one candidate for an offspring, those are given on separate rows. In cases where a male was assigned as the father although he showed a mismatch at one locus, relatedness values for the parent-offspring trio was recalculated without providing a genotype for the putative father at the mismatching loci. Abbreviations: r  =  relatedness value; M  =  mother, O  =  offspring, CP  =  candidate parent, peri  =  periphery.

Eva Hedmark, Jens Persson, Peter Segerström, Arild Landa, and Hans Ellegren "Paternity and mating system in wolverines Gulo gulo," Wildlife Biology 13(sp2), 13-30, (1 October 2007).[13:PAMSIW]2.0.CO;2
Published: 1 October 2007

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