Responses of stoats to scent lures in tracking tunnels

Abstract

Scent lures made from the anal sac secretions of stoats (Mustela ermined) in a long‐life formulation increased the number of visits by stoats to footprint tracking tunnels set near the shoreline of Lake Waikaremoana. Lures derived from female stoats received a similar number of visits to those derived from males. Blank lures with no active ingredient did not attract stoats. Most of the lures remained intact and active for about seven weeks in summer. Rodents were unaffected by the lures, being neither repelled by the scent of stoats, nor attracted to the edible casein‐based carrier compound. Our results suggest that scent lures could be useful for indexing stoat populations. Trials are needed to compare the effectiveness of lures and bait, and to determine seasonal changes in lure attractiveness. Problems of supply of the active ingredients will need to be overcome.     

The potential for biological control of stoats (Mustela erminea)

Abstract

Accelerating the mortality of stoats (Mustela erminea) using biological agents, or reducing their fertility using chemosterilants or biological agents, are increasingly seen as more sustainable and more humane than trapping and poisoning. Obligate delayed implantation in fertilised female stoats of all ages allows 10–11 months for an applied biological agent or chemosterilant to interfere with gestation. Two chemosterilants (cabergoline and mifepristone) disrupt pregnancy in some species and may be effective on stoats, although they are not species‐specific and are probably more expensive than poisoning. For the longer term, more recent fertility control research has explored potentially more species‐specific options for other species based on inducing an immune response to an animal's own reproductive hormones, gametes, or products from embryos. Conception will be difficult to disrupt in stoats because females are sexually mature and are mated in the nest during a short period before they are weaned. A large research effort will be required to determine which of the immunosterilants being developed could be suitable candidates for stoat control. There are fewer options apparent for using biological agents to increase stoat mortality, although species‐specific strains of canine distemper virus may be effective against stoats.

The greatest impediment to controlling stoat fertility will be effective delivery of sterilants. For the foreseeable future, it will probably be necessary to rely on baits, but they are unlikely to put all target stoats at risk, and will be incapable of delivery over larger scales than at present.

Before undertaking expensive field trials and development of anti‐fertility and biological agents, the effects of putative compensatory changes in demographics that may be associated with changes in stoat density should be modelled to see if the sterilisation and mortality rates that are required to achieve a given level of population control are realistic targets. Also, population control should be defined in terms of accrued benefit for wildlife by establishing the relationships between stoat densities and the viability of prey populations.

Biological control of fertility or mortality may never be suitable as stand‐alone control options for stoats, particularly when some native fauna survive only if stoats are reduced to very low densities. Biological control may have greater potential when integrated with conventional control.     

Do mallard ducks feature in the diet of stoats in an agricultural landscape?

ABSTRACT

Research on stoat diet composition in New Zealand has primarily focussed on consumption of indigenous fauna in largely unmodified landscapes. This study used stomach content and stable isotope (δ¹³C and δ¹⁵N) analysis to assess stoat diet in a highly modified agricultural landscape in Southland, New Zealand, focussing on stoat predation of the mallard duck. Stoats were captured in Lochiel, Southland during August–November 2016 and 2017. Stomach content analysis of 26 captured stoats revealed limited stoat predation of mallards (n?=?1) and mallard eggs (n?=?1). Using liver tissue, stable isotope mixing models suggested that bird eggs on average met between 73 and 85% of stoat metabolic requirements throughout the mallard breeding period. Furthermore, mixing model outputs suggested that bird eggs made up a substantial proportion (77–84%) of stoat assimilated diet early in the mallard breeding period, when mallard eggs are readily available. In contrast, isotope mixing models suggested that mallard ducks/ducklings did not make a large overall contribution to stoat diets (< 3%). This study shows that stoats are an egg predator in the Southland agricultural landscape and mallard eggs may contribute to stoat assimilated diet early in the mallard breeding season before alternative prey items become available.     

Field trials of slow‐release synthetic lures for stoats (Mustela erminea) and ferrets (M. furo)

Abstract

Experimental field trials were used to compare the attractiveness to stoats (Mustela erminea) and ferrets (M. furo) of traps set with either a synthetic scent lure or with fresh food bait. One lure, containing 2‐n‐propylthietane, effectively attracted as many ferrets as did rabbit meat bait. Fewer stoats were caught with this lure than with egg bait. Made up in a slow‐release formulation in “plastic rope”, the lure remained attractive to ferrets for at least 2 weeks under sunny field conditions. Traps containing a second lure, 3‐n‐propyl‐l,2‐dithiolane, were less successful at catching both mustelid species than those containing fresh food baits. The scent lures were not attractive to non‐target species, but neither did they deter some species.     

Selection of alpine grasslands over beech forest by stoats (

Predation by introduced stoats is now considered a major threat to the population viability of several New Zealand endemic bird species. Historically stoat research and management has focused on beech forests and little is known about the ecology of stoats in the alpine grasslands occurring above the natural altitudinal limit of beech forest. Several stoat control operations in beech forest valley floors in southern New Zealand assume that adjacent montane areas act as a barrier to stoat immigration. Stoats were live-trapped and radio-tracked in alpine grasslands above the Borland Burn, Fiordland National Park, during the summer and autumn of 2003 and 2004. Seventeen stoats were radio-collared and home ranges were estimated for 11 of them. These home ranges were used in a compositional analysis which showed that these stoats spent significantly more time in alpine grassland than in adjacent beech forest. Range cores calculated for six of these stoats were located high up in alpine grassland and contained very little beech forest. This means that montane areas that contain alpine grasslands are unlikely to be barriers to stoat immigration; rather they may be a source of dispersing stoats that reinvade control areas. Also, endemic animal species that inhabit alpine grasslands could be at risk from stoat predation.     

A review of potential techniques for identifying individual stoats (Mustela erminea) visiting control or monitoring stations

Abstract

We review ways of individually identifying stoats (Mustela erminea) and similar small mammals from visits to bait stations or to monitoring devices in the field. Tracking devices are the cheapest and most practical method currently available of measuring the presence of a particular species, but there has been little research on the recognition of individuals. Elongation of tracking tunnels, or using sooty plates rather than ink to record prints, may improve detectability of individual markings. Recording visits to bait stations or tracking tunnels from DNA sequencing of hair or skin samples is likely to be prohibitively expensive for many monitoring programmes. Identification of stoats visiting bait stations or tracking tunnels using electronic devices has great potential, but these techniques are impracticably expensive because stoats move over such large areas that individual receivers and data loggers would be needed for each bait station. Chemical bait markers such as rhodamine B may be the most suitable method for identifying which animals have used a particular bait station.     

The use of poison eggs for the control of stoats

Abstract

Stoats (Mustela erminea) are an important predator of many forest bird species in New Zealand, and more effective methods for their control are being sought. Stoat control using Fenn traps has been shown to prevent predation on mohua (Mohoua ochrocephala), but this technique is labour‐intensive and costly to use for protection of large areas of habitat. We evaluated 1080 delivered in eggs as a poison for control of stoats. The lethal dose has been determined by captive and field trials, but attempts to implement a large‐scale control operation have given inconclusive results. To clarify the effectiveness of 1080 eggs as a control technique, we carried out further field trials with radio‐tagged stoats in the Makarora Valley. Twenty animals were monitored by radio tracking, and data loggers and video cameras recorded their visits to bait stations. The precise time an individual stoat ate a poison egg could be determined from data logger and video information, and its fate was followed. Sixteen of twenty stoats were killed by 1080 eggs, three died of other causes and one remained alive at the end of the trials.     

Using genetic techniques to quantify reinvasion,survival and in situ breeding rates during control operations

Determining the origin of individuals caught during a control/eradication programme enables conservation managers to assess the reinvasion rates of their target species and evaluate the level of success of their control methods. We examine how genetic techniques can focus management by distinguishing between hypotheses of ‘reinvasion’ and ‘survivor’, and defining kin groups for invasive stoats (Mustela erminea) on Secretary Island, New Zealand. 205 stoats caught on the island were genotyped at 16 microsatellite loci, along with 40 stoats from the opposing mainland coast, and the age and sex were determined for each individual. Using these data, we compare and combine a variety of genetic techniques including genetic clustering, population assignment and kinship‐based techniques to assess the origin of each stoat. The population history and individual movement could be described in fine detail, with results indicating that both in‐situ survival and breeding, and reinvasion are occurring. Immigration to the island was found to be generally low, apart from in 1 year where around 8 stoats emigrated from the mainland. This increased immigration was probably linked to a stoat population spike on the mainland in that year, caused by a masting event of southern beech forest (Nothofagus sp.) and the subsequent rodent irruption. Our study provides an example of some of the ways genetic analyses can feed directly into informing management practices for invasive species.     

No evidence of past bottlenecks in two Danish mustelids: results of craniometric and genetic studies in time and space

A craniometric and molecular genetic investigation was conducted in Danish stoat (Mustela erminea) and weasel (Mustela nivalis) populations. Specimens used were collected over a wide time span (stoat: 1864–2002; weasel: 1863–1990) and from several geographical regions (Jutland peninsula and the two islands of Funen and Zealand). The study was made with a temporal and a spatial perspective, allowing the estimation of differences in genetic diversity and craniometrical trait means between geographical regions and through time with the use of ancient DNA techniques. Univariate statistics of 11 trait lengths did not reveal geographical differentiation in size and shape among the different regions for the stoat, but a geographical differentiation in shape was found for the weasel. There was evidence for reductions in skull size with the year of collection in male stoats, but not in females, which suggests that some selective pressures or environmental factors have affected male stoats to a greater extent than female stoats and the weasel. Relatively high values of heterozygosity were found in both the stoat and weasel, using microsatellite markers. The level of genetic variability of the stoat collected recently was compared with the level of genetic variability in the historical samples, demonstrating that the stoat has not suffered severe loss of genetic variability through the investigated period. A comparison of recent and historical genetic variability of the weasel was not possible because the ancient DNA extracted from the weasels was too degraded. Pairwise F_ST values and assignment tests showed small but significant genetic differentiation between the different geographical regions for both the stoat and weasel. No genetic differentiation between the recent and historical samples of the stoat was found. © 2006 The Linnean Society of London, Biological Journal of the Linnean Society, 2006, 88 , 541–553.     

The biology of the stoat (Mustela erminea) in the National Parks of New Zealand VI. Infestation with Skrjabingylus nasicola

Abstract

The natural distribution of the parasite Skrjabingylus nasicola was surveyed in 1492 stoats from New Zealand’s National Parks. Infestation was rare in the young, so distribution was expressed as frequency of occurrence of skulls containing nematodes in samples of stoats more than 6 months old. Conservative estimates of incidence ranged from 0 to 37% in 27 local subsamples with at least 6 adults and subadults (mean 10%, n = 1005), sometimes varying substantially across short distances. Incidence was highest in beech forest and scrub/grassland habitats with annual rainfall less than 1600 mm. Subadult males (6–10 months old) were infested as frequently as adult males (older than 10 months), and there was no difference in incidence between the sexes. Worms recovered from 97 infested stoats occurred equally often in either side of the skull; were more often large (i.e., probably female) at all intensities of infestation; and numbered 1–73 per infested stoat (mean 12.9 in females, 14.2 in males; difference not significant). There was no evidence that infested stoats were smaller or lighter than uninfested onces.     

Using genetics and Bayesian modelling to evaluate the eradication of stoats (

The New Zealand Department of Conservation recently (May 2008) began a programme to eradicate stoats (Mustela erminea) from Resolution Island (Fiordland, New Zealand) using kill traps. In conjunction with this eradication effort we have the following 3 objectives: (1) to measure the population abundance of stoats prior to trapping using hair tubes and forensic DNA methods; (2) optimise techniques for detecting individual stoats, in order to quantify the probability of stoat persistence given no detections after several months of trapping; and (3) use genetic analyses to identify the possible origins (mainland incursions or in situ breeding) of new stoats captured in a control zone. We present Bayesian modelling techniques used to determine the probability of stoat persistence on the island after the initial population reduction, when individual stoats are no longer captured in traps. We also provide details on an effective level of monitoring and trapping effort required to maintain a comfortable level of confidence that stoats no longer persist on the island. Improving these techniques adds to variety of valuable tools for management of invasive mammal species in a range of natural environments worldwide.     

Swimming capabilities of stoats and the threat to inshore sanctuaries

Stoats (Mustela erminea) are small carnivorous mammals which were introduced into New Zealand in the late nineteenth century, and have now become widespread invasive pests. Stoats have long been known to be capable of swimming to islands 1–1.5 km offshore. Islands further out have usually been assumed to be safe from invasion, therefore routine stoat monitoring on them has been considered un-necessary. Recent incursions, including a stoat found on Rangitoto Island (3 km offshore) in 2010, and another which was deduced to have reached Kapiti (5 km offshore) in 2009, along with distribution modelling and genetic studies, strongly support the proposition that stoats can swim much further than 1.5 km. Acceptance of this hypothesis depends on estimating the probability that such small animals could indeed swim so far unaided. This paper reports the results of a project designed to assist this debate by recording the paddling action, speed and minimal endurance of nine stoats observed (once each) swimming against an endless current in a flume at the Aquatic Research Centre, University of Waikato. Four of the five males and two of the four females could hold a position for at least 5 min against the maximum current available, averaging 1.36 ± 0.336 km/h. In steady swimming against a current of c. 1 km/h, they all used a rapid quadripedal paddling action (averaging 250 strokes/min, stronger with the spread forepaws). Four of the nine swam strongly for >1 h, including one female who covered 1.8 km in nearly 2 h non-stop. Results from such artificial conditions cannot be conclusive, but support suggestions that wild stoats could indeed swim much further than 1.5 km, hence we conclude that the “risk zone” for stoat reinvasions of inshore islands has been seriously under-estimated.     

The effects of mice on stoats in southern beech forests

Introduced stoats (Mustela erminea) are important invasive predators in southern beech (Nothofagus sp.) forests in New Zealand. In these forests, one of their primary prey species – introduced house mice (Mus musculus), fluctuate dramatically between years, driven by the irregular heavy seed‐fall (masting) of the beech trees. We examined the effects of mice on stoats in this system by comparing the weights, age structure and population densities of stoats caught on two large islands in Fiordland, New Zealand – one that has mice (Resolution Island) and one that does not (Secretary Island). On Resolution Island, the stoat population showed a history of recruitment spikes and troughs linked to beech masting, whereas the Secretary Island population had more constant recruitment, indicating that rodents are probably the primary cause for the ‘boom and bust’ population cycle of stoats in beech forests. Resolutions Island stoats were 10% heavier on average than Secretary Island stoats, supporting the hypothesis that the availability of larger prey (mice verses wētā) leads to larger stoats. Beech masting years on this island were also correlated with a higher weight for stoats born in the year of the masting event. The detailed demographic information on the stoat populations of these two islands supports previously suggested interactions among mice, stoats and beech masting. These interactions may have important consequences for the endemic species that interact with fluctuating populations of mice and stoats.     

Stoat density, diet and survival compared between alpine grassland and beech forest habitats

In New Zealand, alpine grasslands occur above the treeline of beech forest. Historically stoat control paradigms in New Zealand?s montane natural areas have assumed alpine grassland is a marginal habitat that limits dispersal between beech forest stoat populations. We compared the summer-to-autumn (January?April) density, weight, diet and winter survival of stoats between these two habitatsduring years of low beech seedfall. Stoats were live-trapped, marked and released in alpine grassland and low-altitude beech forest in the Borland Valley, Fiordland National Park, during 2003 and 2004, and were caught and euthanased for necropsy in 2005. Stoat density was estimated using spatially explicit capture?recapture (SECR). The proportion of stoats marked in one year but recaptured in the next was used as a measure of ?observed survival?. Prey remains were identified from scats collected during 2003 and 2004 and stomachs from stoats killed in 2005. Stoat density was similar in both habitats over the two years, about one stoat per square kilometre. Observed survival from 2003?2004 was also similar, but survival from 2004?2005 was higher in alpine grassland than in beech forest. In 2003, male stoats were on average heavier in alpine grassland than in beech forest, although average weights were similar in the other years. Diet differed significantly between the two habitats, with stoats in alpine grasslands eating mainly ground weta (a large invertebrate) (72%) and hares (23%), while stoats in beech forest ate mainly birds (31%) and mice (19%). Collectively these results suggest that alpine grasslands are not a poor quality habitat for stoats. Traditionally it has been thought that stoats cannot survive on invertebrate prey alone. This research demonstrates that stoats relying largely on invertebrate prey can occur at similar densities and with equivalent survival to stoats relying on vertebrate prey.     

Managing an invasive predator pre-adapted to a pulsed resource: a model of stoat (Mustela erminea) irruptions in New Zealand beech forests

The stoat (Mustela erminea) is a specialist predator that evolved to exploit the unstable populations of northern voles and lemmings. It was introduced to New Zealand, where it is pre-adapted to respond with a population irruption to the resource pulses that follow a heavy seedfall of southern beech (Nothofagus spp.). Culling stoats during an irruption is necessary to reduce damaging predation on nesting endemic birds. Culling might not reduce the stoat population long term, however, if high natural mortality exceeds culling mortality in peak years. During other phases of the beech-mast cycle, culling might have a greater effect on a smaller stoat population, whether or not damage prevention is critical. We developed a 4-matrix model to predict the effects of culling on λ, the annual rate of change in the size of the stoat population, through the four annual phases of an average masting cycle, explicitly distinguishing between apparent and real culling. In the Post-seedfall phase of the cycle, large numbers of stoats are killed, but little of this extra mortality is additive; in other phases, culling removes larger proportions of smaller total numbers of stoats that would otherwise have lived. Culling throughout all phases is most effective at reducing stoat populations, but is also the most expensive option. Culling in Post-seedfall plus Seed or Crash years is somewhat less effective but better than culling in one phase only. Culling has different short-term effects on stoat age distribution depending on the phase of the cycle when culling begins.     

Habitat selection of coexisting competitors: a study of small mustelids in northern Norway

The coexistence of two very similar species, stoat and least weasel, has puzzled many researchers. From their ecology it is expected that they do not coexist, not locally at least, and still they seem to do. We reviewed the specific hypotheses proposed to explain their coexistence and related these to general theories of competitive coexistence. To test these conjectures, we studied the habitat selection of least weasels and stoats on landscape and on local scale. The study was performed during the winters, the most critical season, in years 1986–2001 in northern Norway. Stoats were usually more numerous than least weasels. Stoats showed preference for productive areas both at the landscape and at the habitat scale and appeared stereotypic in their habitat selection. Least weasels were more generalized and flexible in their habitat selection. Contrary to results reported in many studies, least weasel did not react to the presence of stoats and were not excluded from the areas with stoats. We suggest that in the conditions of northernmost Fennoscandia, the two species exhibit a variant of classical competitive coexistence. Both species have a shared preference for rodents, but the access to exclusive alternative prey in stoats allows their coexistence with least weasels, which are more efficient predators on rodents. We suggest that more attention should be paid on survival resources, exploited during times of low resource density, when studying the coexistence between close competitors.     

Ecology of the stoat in

We studied the ecology of a high-density population of stoats in Fiordland, New Zealand, in the summer and autumn of 1990-91 following a Nothofagus seeding in 1990. Results are compared with findings from the same area in 1991-92, a period of lower stoat density. In the high-density year, minimum home ranges (revealed by radio-tracking) of four females averaged 69 ha and those of three males 93 ha; range lengths averaged 1.3 km and 2.5 km respectively. Neither difference was statistically significant. For combined sexes, average range area in the high-density year was significantly less, and range length was significantly shorter, than in the following year. When we compared stoat diet in the high-density year with that in the following two years, there were no significant differences in the frequencies of occurrence of birds or invertebrates in stoat guts. Overall, bird remains were found in 56% of guts, and invertebrates in 28%. Possum remains occurred in 6% of male stoats but were never found in females. Mice were only detected in stoats in the high-density year, when they occurred in 54% of guts. Lagomorphs occurred significantly more often in the guts of stoats during lower-density years (26%) than the high- density year (7%). Seedfall in Nothofagus forest is synchronous and periodic. Following seedfall, mouse density rises dramatically, followed by a sharp rise in stoat numbers. It has been suggested that mice feed on the abundant seed and that stoats in turn increase because of the large numbers of mice available to them. We suggest that the situation is more complex and that increases in not only mouse, but also bird (and possibly invertebrate), densities may contribute to the high productivity of stoats in the year following a Nothofagus seedfall.     

Whisker plucking alters responses of rat trigeminal ganglion neurons

Whisker plucking in developing and adult rats provides a convenient method of temporarily altering tactile input for the purposes of studying experience-dependent plasticity in the somatosensory cortex. Yet, a comprehensive examination of the effect of whisker plucking on the response properties of whisker follicle-innervating trigeminal ganglion (NVg) neurons is lacking. We used extracellular single unit recordings to examine responses of NVg neurons to controlled whisker stimuli in three groups of animals: (1) rats whose whiskers were plucked from birth for 21 days; (2) rats whose whiskers were plucked once at 21 days of age; and (3) control animals. After at least 3 weeks of whisker re-growth, NVg neurons in plucked rats displayed normal, single whisker receptive fields and could be characterized as slowly (SA) or rapidly adapting (RA). The proportion of SA and RA neurons was unaffected by whisker plucking. Both SA and RA NVg neurons in plucked rats displayed normal response latencies and angular tuning but abnormally large responses to whisker movement onsets and offsets. SA neurons were affected to a greater extent than RA neurons. The effect of whisker plucking was more pronounced in animals whose whiskers were plucked repeatedly during development than in rats whose whiskers were plucked once. Individual neurons in plucked animals displayed abnormal periods of prolonged rhythmic firing following deflection onsets and aberrant bursts of activity during the plateau phase of the stimulus. These results indicate that whisker plucking exerts a long-term effect on responses of trigeminal ganglion neurons to peripheral stimulation.     

Whisker plucking alters responses of rat trigeminal ganglion neurons

Whisker plucking in developing and adult rats provides a convenient method of temporarily altering tactile input for the purposes of studying experience-dependent plasticity in the somatosensory cortex. Yet, a comprehensive examination of the effect of whisker plucking on the response properties of whisker follicle-innervating trigeminal ganglion (NVg) neurons is lacking. We used extracellular single unit recordings to examine responses of NVg neurons to controlled whisker stimuli in three groups of animals: (1) rats whose whiskers were plucked from birth for 21 days; (2) rats whose whiskers were plucked once at 21 days of age; and (3) control animals. After at least 3 weeks of whisker re-growth, NVg neurons in plucked rats displayed normal, single whisker receptive fields and could be characterized as slowly (SA) or rapidly adapting (RA). The proportion of SA and RA neurons was unaffected by whisker plucking. Both SA and RA NVg neurons in plucked rats displayed normal response latencies and angular tuning but abnormally large responses to whisker movement onsets and offsets. SA neurons were affected to a greater extent than RA neurons. The effect of whisker plucking was more pronounced in animals whose whiskers were plucked repeatedly during development than in rats whose whiskers were plucked once. Individual neurons in plucked animals displayed abnormal periods of prolonged rhythmic firing following deflection onsets and aberrant bursts of activity during the plateau phase of the stimulus. These results indicate that whisker plucking exerts a long-term effect on responses of trigeminal ganglion neurons to peripheral stimulation.     

Long-lasting systemic bait markers for Eurasian badgers

This study was carried out to assess whether Rhodamine B, ethyl-iophenoxic acid (EtIPA), and propyl-iophenoxic acid (PrIPA) can be used as long-lasting systemic bait markers for free-living badgers (Meles meles). Between June and November 2003, these chemicals were incorporated into bait distributed around badger setts. Serum, hair, and whiskers from individually marked badgers were collected in the following 4 to 24 wk. Rhodamine B was detectable as fluorescent bands up to 24 wk after ingestion of the bait. Individual badgers were found positive for EtIPA and PrIPA up to 20 wk and 18 wk after exposure, respectively. This study indicates that Rhodamine B, PrIPA, and EtIPA could be used as long-lasting markers for badgers.