Showing posts with label Mammal Talks. Show all posts
Showing posts with label Mammal Talks. Show all posts

Sunday, 29 April 2018

Towards solving some prickly problems with hedgehog conservation

Hedgehog - Photo: Jorg Hempel (Wikicommons)

A talk to the Berkshire Mammal Group April 2018

Dr Phil Baker, School of Biological Sciences, University of Reading

Dr Baker explained that the threat to hedgehogs and the need for their conservation had gone ‘under the radar’ until fairly recently, and now students of this creature were ‘playing catch-up’. He argued that, as conservationists, we don’t have the data we now need to establish scientifically how things have changed. He undertook to set out what we need to know; to establish if there is a decline in numbers and to quantify how much that decline might be; to identify what has caused it and what we need to do to conserve this culturally important species. Phil hinted at controversy, referring in passing to the problems of the human introduction of hedgehogs to island ecosystems, and warned he would be playing Devil’s advocate. Indeed, as a clue, a couple of his many splendid photographs had humorously been annotated with red horns!

Introduction

First he defined the hedgehog as an insectivore, belonging to one of four groups that comprise the shrews, moles, solenodons and hedgehogs. Of the latter there are 16 species and the talk would be concerned with the West European Hedgehog (though Phil conceded the best hedgehog photographs were those of the African Pygmy Hedgehog.)

Anatomically modern hedgehogs have been found dating from the Miocene – five million years ago – so, when there were no hedgerows! We assume they were edge roaming, perhaps even woodland dwelling. (“Perhaps I should drop my aitches and call them ‘edge’ogs’”, Phil joked.) It is we who have changed the landscape and affected hedgehog behaviour and abundance.

The problem

Hedgehogs of the early modern period, c1600-1800, have been studied extensively by Roger Lovegrove (2007). He examined church records for evidence of animals killed by way of pest control. It was thought by some at the time that hedgehogs would drink milk direct from cows’ udders and steal the yield. However, Lovegrove concentrated on records from ten just counties in southwestern England, concluding that half a million were killed over this period.

In the nineteenth century the human population doubled twice: 9m in 1801 to 38m in 1901. Moreover, during this period game shooting became large-scale and more organised. Gamekeepers were employed in considerable numbers, falling back only after the outbreak of war in1914. Gamekeepers would kill anything that represented a threat to game bird production: foxes, wild cats, pine marten, stoats – even moles! Certainly hedgehogs were included for their likely predation of eggs, or even chicks. The oldest data sets we have date from the 1960s, and these reveal declining numbers of hedgehogs killed on game estates. But there is much less intensive pest control surrounding these estates, so killing predators locally creates a sink effect, with new animals moving in to vacant territories. Changing trap standards represents a threat too. Stoat traps will also kill rabbits and hedgehogs. A study in 2000 indicated they accelerated bi-catch, so the apertures of these traps were narrowed, causing a 75% reduction in kills. But such killing is no longer reported, and how can conservation work if one key group is silent? New self-setting traps from New Zealand have now been introduced and are deemed legal. These will become a threat as they catch animals repeatedly and without human involvement. There is bound to be an effect as stoats’ and hedgehogs’ heads are the same size!

Food shortages and rationing in the Second World War led to another cycle of threat. Farmers were encouraged to maximise food production; hedgerows were grubbed out to aid the efficiency of mechanisation; machines caused soil compaction and a reduction of earthworks abundance; chemicals reduced the number of invertebrates; even rodents were affected. These conditions have caused a reduction in biodiversity across all taxa – similar declines have been reported for flying insects and birds.

The road network has increased by a third since 1950 (especially with ‘A’ roads and motorways), and this has been accompanied by an increase in overall traffic volume.

Interestingly, the badger population, despite persecution and TB culls, has doubled over this time; the number of setts has increased 95% since 1985 and individual groups may also be bigger. But a study by Dave McDonald at Wytham Wood, having looked at pre- and over-winter conditions, indicates the adverse effects of climate change on food. It is much the same for hedgehogs. They have endured a 60-year onslaught!

How bad is it?

There have been several (though surprisingly not many) studies of hedgehog abundance and distribution, of which perhaps the best known was by Pat Morris in London in the 1980s. The classic work, however, was by Maurice Burton, a newspaper journalist in the 1950. Burton estimated from personal observation that in Oxfordshire there was one hedgehog per acre, so perhaps 30m hedgehogs in the UK. This is the questionable backdrop against which more recent surveys have been set.

Distribution was studied by Arnold (1993), but, like later studies, was dependant on the voluntary submission of data.

Steve Harris (1995) at Bristol mined the literature for published mammal surveys and estimated population numbers to 1km squares per land class. He allocated a score to each: 1, ‘excellent’ to 5, ‘very poor’. There were only four studies of hedgehogs to draw upon, and the results spread over 20 land classes. Harris estimated one and a half million individuals, and rated hedgehogs 4: ‘poor’. This work revealed just how much we did not know. And Defra’s recent updates suggest there has been no progress. There are massive gaps in in our knowledge of population and habitat.

The oft-quoted figure of a 90% crash between the 1950s and 1990s suggests – contentiously – that hedgehogs are worse off than tigers! But not everything is as it seems. Burton himself used the caveat, “highly unlikely” when arriving at his headline figure, and in Germany the estimate is a considerable more conservative one hedgehog per 25 acres. It is generally believed there has been a decline, but almost certainly not by as much as the quotations suggest.

We need monitoring programmes, Phil argued, such as those conducted in Hyde Park with thermal imaging equipment, but the cost usually forces us to use alternative means. There have been several ongoing crowd-sourced surveys in recent years, such as those by the People’s Trust for Endangered Species in London and the British Trust for Ornithology in East Anglia:

Mammals on Roads     One a year, reporters drive their usual routes. 3% decline since 2002
Living with Mammals     Garden survey by PTES.               2% decline since 2004
Garden Birdwatch     Mammals are an optional inclusion.       2% rise since 2007

Likewise the Breeding Bird Survey from 1996, for which volunteers walk a transect twice a year. However, these are very partial, reliant on the self-selecting involvement of volunteers and partial submission of records, with no randomisation of samples and no standardisation of effort.

Take the counting of squashed hedgehogs on roads. How does the number reflect population and vulnerability to traffic? Is it true that the more casualties, the bigger the total population must be in proportion; or conversely, that the population must have suffered a decline due to increasing attrition? This becomes more complicated when one realises that, according to a Dutch study, hedgehogs actively avoid roads. Such evidence is borne out by further work at Southampton by Rondini and Doncaster (2002). Also, the access to the evidence is transient as carcasses disappear quickly and so is difficult to verify or even quantify.

Finding an effective technique

To make matters worse, however imperfect the evidence, the conclusions of these various surveys are inconsistent and even contradictory. They simply don’t tell us the same things or even present a coherent trend. While most indicate decline, one (urban) survey suggests increasing numbers. What we need, Phil argued, is a robust technique allied to randomness of application so as to avoid the effects of recorder bias. Equipment should be accurate, cheap and verifiable if it is to keep the public engaged and allow widespread effort.

As gauging absolute numbers appears to be impossible for the present, let’s settle for presence/absence. For this the hedgehog tunnel has been developed, allowing the capture of footprints in ink. However, we must also be aware of false absence; if we have no evidence of presence, how do we know if hedgehogs are not there? We may simply have missed them. How much is apparent absence down to animal distribution and have much to inaccurate technique?

One technique (Williams et al) is to work on a site that is under the management of one person alone. Ten tunnels are set out and checked repeatedly over five days. Tunnel locations are sited appropriately, though it is accepted that the reliance on edges is an assumption. In the reference survey 261 volunteers took part in monitoring rural sites – one of the biggest citizen science projects – while 219 volunteered for urban sites (in Reading). In the latter there was a 32% success rate in 2013 and 40% in 2014.

The urban study in 2013 indicated a 60% chance each day that hedgehogs would be present over the week; and in 2014, 68%. It revealed a tendency for hedgehogs to return each day and suggested that, if a tunnel was in a garden, they’d find it. Indeed, there was a 78% consistency of use. Conversely, if you don’t get inky paw prints, it is because the hedgehog isn’t in the garden. When homeowners where asked if they thought they had hedgehogs, or to predict their presence, 35% got it wrong. Indeed lots of residents thought there were very few in the Reading area, whereas Lower Earley actually has a good population.

Phil expressed himself satisfied with the technique for garden monitoring; it is certainly better than householder perception.

Impact of badgers
 
Badger sett density has a negative impact on hedgehogs – whereas houses appear to have a positive effect! After you’ve accounted for badgers, there are few impacts of significance. Badgers affect hedgehogs like nothing else does. Just how bad are they?
Actually, this is a more widely studied field, with three studies as a result of the government-sponsored badger cull alone! Hedgehogs don’t tolerate badgers, so after the cull their numbers increased. The lesson is clear: “fewer badgers; more hedgehogs”. Hedgehogs are more present in urban areas than rural, a pattern that reflects badger distribution. Hubert et al (2011) studied the indirect evidence of food supply and concluded that hedgehogs avoid badgers by moving into town, where, coincidentally, people will also feed them!

Why are badgers a problem? Eagles apart, badgers are the most likely source of predation, though no studies have been carried out on the direct effect of predation on the overall hedgehog population. More importantly, they compete for the same foodstuffs. One badger can eat as much as can seven hedgehogs. However, it is not the case that total food supplies have dwindled, as there has been sufficient to support an increase in badger numbers.

Humans have altered the rural landscape and unintentionally made the problem of predation and competition worse. Historically they co-existed after all. Gardens, however, represent a refuge from both. The challenge is to find sites that allow co-existence, but trading badgers for hedgehogs would be a ‘hot potato’, as the reaction to Phil’s earlier comments by some members of the audience made only too clear.

Planting more hedgerows would be one answer, but that would cost large sums and recording multiple sites to get the supporting information. Then farmers would have to be funded in order to make change viable. It would be expensive!

Hibernation

Over-wintering behaviour has been studied in Sweden, where 25% to 40% of hedgehogs die each year. In the UK, survival rates are better: 18%-21%. The University of Reading has studied hibernation at locations near student accommodation in Gloucestershire and Nottingham, using radio tagging. The research has revealed multiple nests, nest movement, moving around a lot before hibernation, but also two or three moves during the period of deep sleep. In one of the studies, 22 animals used an average of 6.5 nests. Good nest sites are required for security, cover, warmth and the abundance of nesting materials. Hedgehogs like to have options, to be able to move if needed. Good quality hedgerows, woodland and brambles offer the best bets. If they get too cold (-5oC to –10oC) they will have to wake up, so climate change is a potential problem as well. Perhaps the urban heat island effect is another reason for the perceived increase in preference for urban locations?

Fragmentation by roads

Hedghogs need help with roads as the width of pavement and the speed and volume of traffic represent considerable challenges. Williams studied the effect of motorways for his PhD and tentatively came to the conclusion that they separated distinct populations that had little or no contact with each other. Populations are already patchy, with more places where hedgehogs are absent now than in the 1990s. And things are getting worse, as the Highways Agency installs solid concrete barriers rather than the old metal ones. The only viable crossings are bridges and underpasses – or purpose-built badger tunnels which come with an inherent danger! But even urban roads are a challenge.

Prospects, especially in town

Suffering poor, fragmented habitat and threatened by badgers, no wonder hedgehogs are heading for the towns! The only ‘good news’ for hedgehogs is the badger cull. (Interestingly the hedgehog hotspots are East Anglia, with a tradition of gamekeeper control of badgers and Yorkshire, with a tradition of badger-baiting.) More hedgerows are vital, but expensive. In the short term we can at least help the urban hedgehog.

It has been suggested that foxes pose a problem and indeed when the foxes of Bristol were suffering from mange a few years ago, hedgehogs appeared more numerous. However, although there have been a hundred studies of foxes’ diet, hedgehogs feature very infrequently. And dogs tend to be indoors at the times hedgehogs are out and about.

We can provide sources of food (but should not offer cow’s milk or mealworms), shelter and access. All sorts of threats can be moderated: litter, fences, rat boxes, bonfires, rubber bands. Decking is not good for food supply, though it is a good source of shelter. Phil noted that gardening and maintenance practice does make a difference. Ten years ago, you’d find plenty in the Harris Garden between 9-12pm, but not since the refuges have been systematically mown. As for holes in fences, 48,000 people have signed up to Hedgehog Street. According to the Earley gardens project (Piper 2016), we locally could do better!

If we double the access, we double the number of hedgehogs. There is no obvious difference in the gardens used. On any one night, a hedgehog might use eight gardens; a female might cover an area of 100m x 100x, or more if mating. So why not use all the gardens available? Fear? We need to radio-track to see whether they use different gardens on different nights. Hog boxes – of which there are dozen of designs – are more likely to make a garden attractive, especially if placed nearer the house! It might take time, for although hedgehogs make repeat visits, their pattern of travel will change from year to year.

Takeaways

•    We are at a moment of crux; hedgehogs are declining throughout Europe and soon to be reclassified as ‘near threatened’
•    We are now getting the data we need and urban areas are increasingly recognised as important
•    Difficult decisions have to be made; it’s in our hands, but we need buy-in from farmers and householders. Funding will be vital to make any wider scale difference.

DISCUSSION

Phil had promised to be provocative and play the devil’s advocate, and certainly prompted reactions from the floor on a number of occasions during his talk. Where possible, the subject matter of interjected questions has been incorporated into the foregoing account, but there were several others on additional topics, as answered below.

Over the past 10-15 years there has been an upswing in the study of hedgehogs. However, there have been only two studies of diet since the 1970s. There have been no studies of the impact of deer on the density of woodland vegetation, though the question prompted an interested response.

The rehabilitation of injured hedgehogs provides a valuable function, except where the release occurs in an area remote from the hedgehogs home territory.

Tip-ex surveys are a useful way of monitoring the number of individuals in a local population, thought this has raised concerns about the possible need for training and licensing in wildlife handling.

Do hedgehog have fleas? No, not to any significant degree, though some individuals might.

Thursday, 19 January 2017

Mink – Evil or Interesting?

A Talk by Dr Joanna Bagniewska to the Berkshire Mammal Group

6th October 2016


write-up courtesy of Edwin AR Trout, Berkshire Mammal Group

Dr Joanna Bagniewska, University of Reading

Opening the meeting Amanda Lloyd introduced Joanna as a zoologist specialising in behavioural ecology and invasive species research, gaining her MSc and PhD from Oxford University. Over the years she has undertaken research in five countries, having studied foxes and jackals in South Africa, wombats and wallabies in Australia, mole-rats in the USA, and both bees and mink in Britain. (Joanna observed that in view of mink’s past fortunes, she was one of few researchers able to wear her study species!) Currently Joanna works as a teaching fellow for the School of Biological Sciences at the University of Reading and has won awards as a science communicator.

She started by suggesting she was one of a minority in this country to admire the otherwise widely denigrated American mink, perhaps because she approached the subject from the point of ecology rather than conservation and control (where mink are considered pests). She defined them as mustelids and took a few moments to outline their ecology.

Mink Ecology

The American mink is native to North America, at least north of the south-western arid zone up to and including Alaska, but south of the high Arctic. Mink are to be found in areas of high water quality. They are small bodied – at 15-18” the males are twice the length of the females – and sexually dimorphic. In some areas males have shown a preference for eating rabbits (for which they have proportionately bigger jaws and teeth) and females – water voles. They are opportunistic feeders and both sexes will eat insects, fish and birds.

While native to North America, they have been introduced into Europe, Asia (especially Siberia) and South America (Patagonia in particular),

largely as a result of the former demand for their fur. In the 1920s and ‘30s they were farmed, but later, in the 1950s, many escaped or were released. They are now regarded an invasive species.

They have, in many ways, become too successful for their own good. Why? They are generalist foragers, with a broad diet: birds, amphibians, reptiles, rodents, insects, and crustaceans. They can hunt like foxes, climb like cats and swim like an otter. They are semi aquatic and very adaptable.

An Invasive Species

As an invasive species, what has been their impact? Traditionally, successful incoming species upset the balance of nature by:

  • Increased predation
  • Resource competition
  • Hybridisation
  • Disease transmission

Of these the first two are of most relevance, though there have been some recorded cases of interbreeding between wild and released mink in North America.

The problem of increased predation is exacerbated by the higher proportion of carnivores among invasive species. Carnivores make up 5% of mammalian species, but when invasive mammals are examined, that proportion rises to19%.

Direct predation by mink is most notable in the UK in the case of water voles. Female mink are the right size to enter voles’ underwater holes and the water vole population is declining fast. This is, admittedly, for various reasons, but the presence of mink is not helping. There is no problem with water voles in Europe, incidentally, but rather the Pyrenean Desman instead is vulnerable and declining.

The Landscape of Fear”
Other vulnerable species are ground-nesting sea birds, for which the security of islands and rocky

outcrops are no protection against the semi-aquatic mink. On arrival in a colony mink will behave like ‘a kid in a candy store’ and take as many as 100 chicks per night, with no sense of forward planning or restraint. Indirect consequences follow, as birds leave their nests – in fear or to protect their young by attacking predators – and the chicks or eggs succumb to the cold or neglect. The very presence of fear can have further negative effects on the predated population.

Over-sized, Over-sexed and Over here”
A notable impact of resource competition has been on the European mink, which is now limited to Estonia and the Pyrenees, as the American mink is sufficiently well equipped to out-compete.

American European
1310.2 g v. 976.6 g
size of female = size of male
litter of 6 v. litter of 2.5

The American mink is voracious and adaptable, and its European cousin is unable to keep up.

Another measure of its success lies in the competition with polecats and otters. When these species were declining in the 1920s-50s, mink expanded into their vacated niches, on both land and water.

Horrible – but Interesting

American mink are semi-aquatic BUT …

  • They are small, with a large surface area, and so loose heat quickly
  • Their fur is neither buoyant nor insulative
  • Their propulsion is inefficient – they swim like dogs rather than otters
  • Their paws have little webbing (more than polecats, but less than otters)
  • They have poor eyesight, especially underwater.

Is swimming innate and instinctive? It seems the young have to be taught, as indicated by trials on captive mink. Other tests suggest mink will work harder to get to water than even to obtain food! And mink spend much of their time in the water, diving for food.

Diving Behaviour

How do we study diving animals? It has been difficult until now. Research has focussed onterrestrial behaviour, which is more readily observable and can be indicated by footprints, scat and camera traps. For wild mink only ‘surface events’ have been traceable in the water, and underwater behaviour monitored only in captivity. Joanna’s research was the first monitoring of mink diving in the wild. Indeed, the only previous study of mammals was one of the platypus in Australia. Since then there have been studies of water rats and beavers as new data-logging technology becomes available. Devices small enough to be attached to mink can measure time spans, temperatures, pressure and acceleration.

Such data logging was first developed in the 1950s, weighing as much as 1.5 kg, based on ‘egg timer’ technology and recording output on paper. The first devices were used on Weddell seals. They were accurate to about 20 m and therefore only useful for extensive depths at sea. Now devices are digital, weigh 1g and are accurate to 3 cm, so may be used effectively in the shallow water of British rivers.

Monitoring Programme
Joanna’s project monitored 16 distinct animals on the rivers Thames and Cherwell in Oxfordshire, generating 20 datasets, with a mix of males (six) and females. The programme was conducted over three seasons, spring being excepted on animal welfare grounds.

The method made use of mink rafts, by which an enticing ‘home’ or tunnel was placed on a floating platform away from the bank. Pliable clay would be spread on the base of the raft to receive the impression of foot prints should a mink investigate the tunnel. With the presence of mink thus established, the tunnel would be fitted with a trap and bait, and, if caught, the mink fitted with a collar and data-logger.

Quantitative Results
The collective results of the study indicated great variety in depth and duration, with a total range of 1 to 189 dives per day, with the greatest individual range between 5 and 143. It became notable that the smaller females were the more energetic divers, performing over 100 dives per day (as explained below). The time spent diving wasn’t long: a total of just 38.4 minutes per day on average, with 57.9 seconds the maximum individual dive-length recorded. Median depth times varied between 7.4 and 18.0 seconds.

(Previous studies had suggested even shorter times.) Diving was undertaken throughout the year, not just in summer as had been postulated, and 83% of dives took place in daylight – presumably in consequence of minks’ poor eyesight. The maximum depth of around 3 m was more an indication of river depth than diving ability.

Dive Clustering
The pattern of surfacing suggested that dives were clustered in bouts of activity and so was analysed according to the Hidden Markov Model (HMM). Three types of diving frequency were identified:

  • A “cluster” of multiple dives
  • Loosely aggregated: an “activity session”
  • Single or terminal dives

Temperature and Persistence
Mink experience a temperature range of 5-35 oC, in which temperature falls during activity. The body cools in water, and warms through when basking on the bank; it is typically 35 oC when sleeping, in the 20s when on land, and drops when diving. It is noticeable that dive effort is higher in females; female ‘persistence’ may extend to performing 80 dives in a row. Is this because they are excellent divers, or ineffective hunters who have to repeat dives to eat?

Either way, the smaller the mink the greater the persistence and this may be expressed as a negative relationship between temperature and bodyweight. Persistence is greater during the day, when temperatures are higher, and become more concentrated the shorter the day. That said, mink tend to be inactive 80% of the time, spending only 50 minutes or so in the water per day. Males are more nocturnal – perhaps, because of their size, they are less afraid of meeting otters?

Competition with Otters

Behaviour has altered over time, with the evidence of scat declining since the otter’s resurgence in the 1990. However, if other evidence such as footprints is taken into account, it appears that mink remain, but are no longer deliberately marking their territory. Otters are bigger, and may weigh 8 kg, so while the feisty mink might be prepared to fight, it wouldn’t,

wish to make a habit of it. So what seems to be happening is that when the nocturnal otter returns, mink behaviour adapts to the new circumstances and becomes diurnal, thus avoiding confrontation.

Conclusion

The survey testifies to the success of new TDR (Time Depth Recorder) technology and HMM techniques in monitoring the behaviour of otherwise difficult to observe species.

QUESTIONS

Have there been studies of the American mink in its natural habitat, North America?
Yes, in the 1940s and 50s, but mainly of terrestrial behaviour. There have been diving studies elsewhere, in Tierra Del Fuego for instance, where mink are diving in the sea, and of feeding in Sweden.

How long did the mink wear collars?
Joanna aimed to collect collars after three weeks, but if missed, they were designed to be readily biogradeable, rather than made of more durable leather.

Where do mink live?
They don’t excavate, but occupy existing holes. Sometimes these are in trees, but mink are particularly fond of rabbit warrens.

Are males and females mutually antagonisic?
Yes, males and females join only to mate. Mink of each sex maintain their own, linear, territories. The males occupy about 5 km, overlapping two of the smaller females’ 3km territories. Males will not tolerate each other. Mink are not social; apart from mothers and kits they do not share.

How related are they to the European mink?
Less so than previously thought; they are of a different genera. Indeed there is no knowledge of hybridisation. European mink used to be found in the Baltic states, Poland, Belarus and Russia south to northern Ukraine. No population is known to have existed in the British Isles.

Has the return of the otters in recent times deterred the mink?
It appears not, though it has affected the mink’s behaviour.



Monday, 5 September 2016

The contribution a small commercial reserve can make to Leopard Conservation in South Africa

A BMG Talk by Tara Pirie, 4 February 2016

Tara explained that she had spent ten years in South Africa, as a guide for the first seven and then embarking on a PhD toward the latter end of her time there, while working at Ingwe Leopard Research. (‘Ingwe’ means ‘Leopard’ in the local language.)

Leopard Conservation

Like other animals leopards are threatened by habitat loss, food depletion and conflict with humans, and Tara made the case for their conservation, and that of similar predator species. One argument is ecological – often the loss of an apex predator will cause a trophic cascade in the food chain, or a meso-predator release. Another is economic – leopards are highly charismatic animals and the tourism they support is economically beneficial to host societies.

Threats to leopards
Most important is conflict with farmers, though livestock deaths are not always caused by leopards: disease, accidents, etc can create an exaggerated impression. Even the presence of its spoor does not necessarily mean the leopard killed the livestock. (If the wound is not obvious it is possible to lift the skin to see where bruising occurs: leopards go for the throat.) Other human-related threats include:
  • Hunting. Permits for culling, taking out problem animals and trophy hunting
  • Trapping, snaring, poisoning – often for food
  • Road deaths – accidental and avoidable
Tara cited the instance of a road with tall grass growing on either side, on which four leopards had been killed a year; this was one of the triggers for Will Fox to set up Ingwe Leopard Research. When he arranged to have the grass cut there were no known deaths in the following three years.


Ingwe Leopard Research

Ingwe Leopard Research in Mpumalanga Province was set up in 2011 with a triple purpose: research to support conservation with evidence; raising awareness, and supporting sustainable tourism.

Research
Although Tara is back in the UK, the research work is ongoing, supported by the income from running safaris. Government sites offer legal protection, but contain only 25% of the leopard habitat in South Africa; up to 75% falls outside formally protected areas and leaopards are known to roam freely. Permits to kill leopards cost R10,000 (£500) and are relatively affordable. Ingwe undertakes the only leopard research in the province outside Kruger National Park, generating data to formulate informed decisions. It also gathers data on other carnivores such as genets and hyenas.

Raising awareness
One of the fundamental tasks is to encourage an interest in conservation among the local people, and an attitude where leopards are valued rather than perceived as a threat. Tara described a two-pronged approach:

School visits
Ingwe helped with fund-raising, offering lessons in computing, repairs to building etc. After some months of involvement in the school Tara finally discussed the purpose of Ingwe’s work with the headmaster, but only once he had raised the subject. It transpired the locals were concerned about the presence of leopards as a threat, much as with the lethal snakes that abound in Africa. Gradually Tara encouraged them take a more positive view.

Work with farmers
Influencing farmers was difficult to start with, but by listening to them in the pub – rather than preaching at them – and indicating she understood their wish simply to earn a living, she was given a month’s trial with one of the more prominent locals to demonstrate the leopards were not an active threat. The trial was successful and the leopards remained untouched thereafter! All permits have subsequently been rescinded.

Leopard Ecology

In describing the characteristics of leopards Tara quipped they often “hadn’t read the script”. Received wisdom suggests they are:

Highly adaptable.
They are known to eat as many as 92 prey species ranging up in size to eland calves and juvenile giraffes, and one has even taken on a 3m crocodile. They can carry their own body weight up into a tree. But the optimum size is the 25kg impala. Surprisingly, they will also eat fish.

Solitary
Not always. Though males usually are, mothers spend 90% of their time with cubs. However, Tara has also seen males spending time with their offspring (sons) up to three years old, even from different litters. Such behaviour has also been reported in the lower density populations of Namibia, so is not unique to Ingwe.

Territorial
Both males and females have their own, often overlapping, territories. Acquaintances are more likely to be accommodating, and submissive individuals will tolerate incursions. ‘Territory’ is not absolute: more of a ‘core area’, one that will be defended. They defecate in prominent places as a visual sign of their residence, and will claw trees, scent mark (their odour smells of popcorn) and call. The sound of the leopard call is like that of a saw, usually four repetitions for a female; as many as ten for a male.

Nocturnal
Not always. Though adult males seldom appear, females can be seen in the heat of the day, and are more likely to come out on overcast days or in winter.

Savannah dwellers
But they also live in rocky environments and they are the most widespread of the felines: from Cape Town to the Amur Valley in Siberia and down to Indonesia. The leopard is the last of the ‘Big five/ to remain free-roaming.

They were classed ‘near threatened’ in 2008, but are so elusive there are no accurate records. One estimate of 600,000 in South Africa has been dismissed as absurd. But there are 150 CITES in South Africa every year, and seven in the province. See Swanepoel 2013 for distribution of suitable habitat based on knowns populations both in the Transvaal provinces and the Cape.

The Thabo Tholo Wilderness Reserve

The work of Ingwe Leopard Research’s work in the reserve has helped establish density, calculate home ranges and characterise habitat selection.

Spoor/tracks
Tara trained volunteers to locate and identify leopard tracks. They have a three-lobe pad and four oval toes with no claw marks. Left and right are distinguishable. Trackers were to take photographs with a ruler included for scale (see page 4), but there was considerable difference in determining accurate measurements – typically the margin of error is between 1-2 cm.

Camera traps
Tara established a camera club to fund camera traps in return for access to the best photographs, and somewhat against expectation this was highly successful. As many as 50 cameras were obtained over a three-year period. They were placed 45cm above the ground, 2.5 km apart (the smallest leopard range is 3.2km), and were distributed accorded to biome: grassland (30%) or savannah (70%). Several of the traps were productive in generating evidence of leopards. However, other creatures were photographed too: samango monkey (a forest dweller), Cape fox (on the edge of his distribution), and several others. Interestingly the trackers found evidence of these creatures long before the cameras, the presence of leopards being the only exception!

ID Kits or ‘Spot the Difference’
Each animal has individual markings that can be checked against the ID guide, comparing say three or four areas of the pelt: neck, leg, flank, etc. Many leopards have a ‘necklace’. Often it is only the leg that is in sufficient focus in photographs, momentarily static when passing a camera trap.

Sex
Size or build is not always a reliable guide. The leopard known as Long Legs was large and muscular, and it was only later she was identified as a female when pictured with a cub.

Age
Their initially pink noses get blacker with age. Diamond Girl was about 8 or 9; Ru about 4 at the time (now 6 or 7). Look for scratches on the nose and tatty ears as a sign of age. The dewlap forms when older, though it was less noticeable at Ingwe where the leopards do not have much competition and so do not hoist their prey into trees, thus the neck muscles are less developed.

The local leopard population

Spatial Explicit Capture Recapture Model software was used to analyse data. 28 individual leopards were identified over the three-year period – 15 adults, 9 sub adults and 4 cubs – with four resident in the reserve. 11 cubs were born on site.

Diamond Girl - dominant female, with territory in the central area
Pippa - to the west
Ru - a young male, based in the south 
Big D - male with a large territory overlapping all three of the above

Six cameras displayed a lot of activity, including shots of otherwise unknown leopards. Tara thought this particular area could be a dispersal route for leopards passing through and the hypothesis was supported by groups of holes in the fence at NW and SE extremities.

Golden leopards
A sandy coloured leopard with brown spots appeared on three cameras over two nights. Another similar variant, a six-month-old born to normal-coloured Pippa, has also been seen. That’s two with a particularly rare colour variation, possibly caused by a recessive gene. There are only five records of similar creatures between 1900 and 1950 – all in India. The next was in 2012 in Madekwe. In total there have been 12 in the world; 7 in South Africa. Five of these (71% are in the Lydenburg area and 29% in Thaba Tholo. This suggests inbreeding.

Black panthers
These are caused by an excess, rather than insufficiency, of pigment. They appear in greater numbers and are to be found notably in Tanzania and Malaysia.

Summing up

Empathy and Education’. Combined with active research, KLR’s approach has paid off. Pippa was one of the leopards licensed to be shot, but is still alive. Hunting licences have now been banned for the year (despite their value as an income generator) and Mpumalanga Parks and Tourism Authorities wish to make use of Ingwe’s data.

DISCUSSION

Is the threat of poaching or even trophy hunting, exacerbated by the publication of research information? Yes, though on the other hand, conservation requires the cooperation of local people who won’t know if not informed. It is a balance; there is no easy answer.

Do leopards take livestock as easy prey or just when game is inadequate? Generally an individual sticks to a preferred species if the option is available. They seldom get a taste for sheep – indeed they are on camera as turning up their noses at sheep carcases. Problem animals are few and at Ingwe they all appear well fed.

Why the colour variation at Ingwe? White impala and black serval are also in the area inhabited by the golden leopards. The latter may have increased through isolation caused by key leopards being taken out.

Is the colour variation associated with health problems? Not known, but the black colouring of Malaysian leopards has equipped them well for the jungle.

Are the smaller leopards of the Cape a sub species? Not at present, though some scientists are pushing for this classification.

Do we know anything about the historical density trends; has there been a bottleneck? Not known.

There has been little dialogue between the various leopard projects being conducted, though that is starting to change.

The ratio of sexes is roughly even.

What is the level of human population at Ingwe? Low density; sparse farming at the borders.

The surrounding game fence is the normal type, but now has 1,500 holes, of which 900 are leopard sized. It is now thought best to keep the holes, as fences do not keep leopards out. One has even been through an electric fence!

25 kg of prey lasts for about a week, as the leopard changes from full to empty. Females hunt more frequently when they have cubs. If relying on guinea fowl, say, hunting may be required twice a day. But leopards are opportunists and if they gorge on kudu, will take a week and a half and more, to digest.

Listen, don’t talk!” – Tara reiterated her approach. Locals will tolerate a degree of loss, but only up to a point. Work with them to meet half way, she urged. At Ingwe many children have seen no wildlife locally and are now looking with fresh eyes.

Edwin A.R. Trout
Berkshire Mammal Group
 
identifying pelt markings

identifying pelt markings

Distinctive paw prints (above)

Photos courtesy of Tara Pirie