First International Hedgehog Workshop
European Hedgehog Research Group
25.-28.4.1996,  in Arendal, Norway.

ABSTRACTS OF PAPERS PRESENTED

The first results of the hedgehog survey in Latvia
Kampe, G. 
Faculty of Biology, University of Latvia, Kronvalda bulv.4, LV-1842, Riga, Latvia

Study of the distribution and ratio between Erinaceus europaeus and Erinaceus concolor in Latvia is described. This study was carried out as part of a Latvian mammal atlas project from 1992 to 1995. Questionnaires were the main source of information. Latvia lies on the distribution edge of both hedgehogs species. The main distribution area of E. europaeus is situated to the north, but E. concolor's to the south. E. europaeus is found in northern, western, and central regions of the country. In eastern region E. europaeus is not found. E. concolor dominate; E. europaeus is rare in Latvia. Distribution map is based on the standard European UTM-grid system. 
 
 

How many hedgehogs are there, how can we count them? 
P A Morris 
Royal Holloway College, University of London 

Hedgehogs live at a relatively low population density, so conventional mark and recapture methods of estimating population size over a large area would require considerable trapping effort. Hedgehogs can easily be caught by hand, using a torch to find them but a study in New Zealand indicates that overestimates result from sampling a study area that is too small. We have attempted to use transect sampling to estimate population density, but even 80 m of transects provided insufficient captures to make a statistically reliable population estimate. However, the estimate did more or less agree with capture-mark-recapture estimates made using the same animals. Densities of around one animal per hectare are normally found, but these are in study areas where there are plenty of hedgehogs present and easily seen. It would be even more difficult to obtain reliable estimates from habitats and areas where hedgehogs were harder to see the possibility of using roadkills as an index of relative abundance has also been investigated. A much higher incidence of roadkills was found in New Zealand, compared to Britain. This suggests that traffic density is not a complicating factor as there are far fewer vehicles on the roads in New Zealand. Within Britain, regional differences were consistent from year to year, with the north east having more kills per 100 miles of road than the south east (where traffic densities are higher). However, there is evidence that the method is fundamentally flawed. It appears that once an observer has seen one hedgehog, he is more likely to notice another. Thus the sampling intensity is not consistent. 
 
 

Demographis variables of a hedgehog (Erinaceus europaeus) population and road mortality
Marcel P. Huijser(l), Piet J.M. Bergers(2), Bart A. Nolet(1) & Luc T.J. Meuwissen(1)
1 Vereniging voor Zoogdierkunde en Zoogdierbescherming (VZZ) Emmalaan 41, 3581 HP Utrecht, The Netherlands 
2 Institute for Forestry and Nature Research (IBN-DLO), Department of Landscape Ecology, P.0. Box 23, 6700 AA Wageningen, The Netherlands 

Demographic variables and road mortality in a (sub)adult hedgehog population were studied in a small scale 150 ha agricultural landscape located near Elburg, The Netherlands. Animals were captured using traps after which they were individually marked with ear- and spine marks. In 1994 6 trapping sessions took place, and an additional 4 in 1995. At the same time all roads in and around the study area were intensively checked for traffic victims. 
(Sub)adult males and females differed in survival rate, and were therefore analyzed separately. Males had relatively low survival rates in summer (0.42, females 1.00) whereas female survival rates were lower in winter (0.65, males 0.92). This pattern may be related to exhaustion of the males during the mating season when they show great activity. Females may have insufficient fat reserves to last them through winter, which may be caused by the limited time available to store reserves between weaning their young and the start of hibernation. The yearly survival rate was estimated at 0.70 for both sexes. 
The highest number of (sub)adult males and females during the study period was estimated at 24 males and 32 females, leading to a maximum density of 16 males and 21 females 100 ha-1 . Losses (deaths and emigration) were estimated at 15 males and 19 females during the period losses were estimated. The number of traffic victims during the study was 5, and 2 in the period in which population size and losses were estimated. When all losses would have concerned dead hedgehogs, 5.9 % of the total population was killed by traffic. When population size is concerned, 4.1-9. 1 % of the male, and 3.6-11.0 of the female population was killed by traffic at one point in time. The number of juveniles present in 1994 was estimated separately, but no juvenile traffic victims were found. 
The percentage of male traffic victims was determined at 60-80 % which seemed rather high. Far more males (11, 8) than females (3, 2) were shown to cross the two roads in the study area. Thus it is concluded that males are more vulnerable to traffic than females. 
 
 

Variations among British Hedgehogs 
P A Morris 
Royal Holloway College, University of London

The British hedgehog was described as a distinct. subspecies earlier this century, but the features that distinguish it are greatly affected by age changes. It is likely that 'our' hedgehog is not significantly different from those elsewhere in north west Europe, except perhaps in having a smaller average size. Within Britain, the animal seems to vary little. Many have significant numbers of white spines, a variation that has not been eliminated by natural selection, presumably because the spines offer sufficient protection from predators that there is no disadvantage in being different from normal. Albino hedgehogs are reported fairly often in the popular press, from many parts of the country. Leucistic hedgehogs are extremely rare on the mainland, but on the island of Alderney, 25% of the population are of this type. Melanistic hedgehogs have never been reported in Britain. A preserved spineless hedgehog exhibited at a 19th century scientific meeting was probably a fake. However, two recent examples of hedgehogs lacking spines were quite dissimilar. One had an almost total failure of keratin production and an unpigmented skin. This was probably a genetic abnormality. The other animal had a dark skin and some hairs with a very few, distorted spines. It had been normal until about 6 weeks old, then lost its spines. It is not clear why. It lived to be six years old. 
 
 


 

X-Ray measures of long bones as an aid to the age-determination in hedgehogs
(Erinaceus europaeus) 
Nigel J. Reeve (1), Beverley Love (1) and Richard Shore (2)
1 School of Life Sciences, Roehampton Institute London, West Hill, London SW15 3SN. UK 
2 Institute of Terrestrial Ecology, Monkswood Experimental Station, Abbots Ripton, Huntingdon, Cambridgshire, PE17 2LS. UK. 

The determination of the age of wild animals is an especially key component of demographic studies but it is also very important in many other kinds of enquiry. In the present study the aim was to find an expedient and accurate method of age determination for a sample of 68 road-killed hedgehogs as part of an ecotoxicological investigation. Various methods suitable for both live and dead animals were reviewed but the study concentrated on determining the usefulness of ulna and dentary length measures to aet as a cross-check against two age- determination methods commonly used in hedgehogs: i) periosteal growth line counts from stained sections of the dentary bone - a potentially absolute method; ii) the categorisation of the stages of epiphyseal fusion in the manus - a relative method. Inter-rater reliability in the determination of periosteal growth line counts was also studied. X-ray radiographs were used for both the categorisation of epiphyseal fusion stage and for the ulna length measures. Dentary length was measured directly from the dissected out jaw. 
All measures (periosteal line count, epiphyseal fusion category, ulna length, dentary length) were highly correlated with one another (typically p<0.001) however, both natural variability and rater unreliability clearly indicated that it was unsafe to rely on any one method. It is recommended that when using power relationships derived from linear regression analysis in the prediction of age from bone length measures, first summer animals (not yet hibernated) which vary greatly in their measurements, are treated separately from older animals. 
 
 


 

Radio-tracking and home range studies of hedgehogs
Nigel J. Reeve 
(School of Life Sciences, Roehampton Institute London, West Hill, London SW15 3SN) 

This paper provides a synthetic review of radio-tracking and home range studies of 
hedgehogs. Almost all studies have been of the European hedgehog (Erinaceus europaeus) but there has been one study of both Erinaceus concolor and Hemiechinus auritus in Israel. Radio-tracking studies in several habitats and various countries have now revealed much about ranging behaviour and nest use in European hedgehogs. The general picture is that of an active, wide ranging animal, capable of covering a track of several kilometres per night, with sexually active males exploiting home ranges 2 to 3 times the area used by females. There is little evidence for defense of range area or spatial exclusivity (territoriality) and individual home ranges often overlap completely (both sexes). The low observed frequencies of conspecific encounters suggests that hedgehogs avoid direct competition by mutual avoidance mechanisms (maintaining a 'personal' space). Patterns of day nest use tend to differ between the sexes, however both may maintain and use several nests. Non-simultaneous nest sharing (ie. the use of other individuals nest sites) has also been recorded. Radio-tracking has brought many benefits to the field study of mammals but it requires rigorous protocols if it is to yield the maximum useful information about the behaviour of subjects. Methodological problems are discussed and the rôle of spool and line tracking in providing supplementary information is considered. 
 
 


 

Juvenile dispersal and survival of sub-urban hedgehogs in Trondheim, Norway 
Hanne Mari Saether 
Dept. of zoology NTNU 7055 Dragvoll Norway 

In Scandinavia there has been a very few studies of juvenile hedgehogs. I wanted to study out what happened to the juveniles from the moment they left the nest and five weeks forward and to study dispersal and especially the mortality factors and rate. The mortality among juvenile hedgehogs in Trondheim is especially interesting because during the last 10 to 50 years the population has decreased. The reason to this decrease would have been very interesting to find out. 
During my field research I colourmarked 27 juvenile individuals of hedgehogs and 22 individuals of them where also radiomarked. This was done when they came out of the nest at age four weeks. This individuals where localised once at daytime and three times at night for four to five weeks. I also measured their weight for one to two times every week. A lot of individuals were dying, and for those who died I tried to find the cause of their death. And from this I think I can conclude that badgers loves to eat small, sweet and nice hedgehogs babies. 
1 have just started to look at the dispersal data, and it seems that the dispersal distance successively increases from week to week, And the home-range area increases significant with time and weight. There is no sex differences among juvenile hedgehogs in respect to homerange, size and weight. 
 
 


 

Smallscale distribution and habitat use as determined by food dispersal: 
"The Hedgehog-Earthworm System" 
B. 0. Föger** & M. H. Cassini*
BBSRC/NERC Ecology and Behaviour Group (former AFRC Unit of Ecol. and Behav.), Department of Zoology, University of Oxford, OXI 3PS Oxford, UK. 
(Present addresses: * PROFAUNA Organisation, Corrientes 1145, 49, Of 47, (1043) Buenos Aires, Argentina (profauna@fauna.org.ar). 
** Beingasse3/24,A-1150Wien, Austria (a8804082@unet.univie.ac.at).) 

At a local scale the spatial distribution and foraging behaviour of hedgehogs (Erinaceus europaeus) were analyzed to investigate the influence of food availability and social organisation on the pattern of distribution and abundance. The factors that can determine the local distribution of foraging hedgehogs were studied, including prey distribution, foraging success, food searching behaviour and size, age and sex of hedgehogs. It was found that the relative increase in the density of hedgehogs was directly proportional to the relative increase in the density of earthworms and that the intake rate was systematically higher in sites with high densities of worms than in poor sites. Heavy females used more intensively the better sites and spent more time per night in the habitat indicating a differential access to those sites by individual hedgehogs. 
 
 


 

Habitat use of hedgehogs (Erinaceus europaeus) in a small scale agricultural landscape
Marcel P. Huijser, Mathy P.A. Lips, Johan A. Buitenkamp & Anita C. Dulos 
Vereniging voor Zoogdierkunde en Zoogdierbescherming (VZZ) 
Emmalaan 41, 3581 HP Utrecht, The Netherlands 

Habitat use of five male and five female adult hedgehogs was studied in a small scale 150 ha agricultural landscape located near Elburg, The Netherlands. Animals were captured using traps after which they were equipped with radio-transmitters. Individual animals were tracked during 1-6 nights between July and November 1995. Every 10 minutes a location (N=774), obtained through actual sighting, was plotted on a habitat map. Habitat selection was determined by comparing habitat use with the relative area of the habitat types that were present, both on the map as a whole, and within the home ranges of the individuals. 
The study area was dominated by grasslands (57%), wooded banks (11 %), and forest patches (8%). Of all habitats grasslands were used most often (49%). Nevertheless the animals used this habitat less than 'expected'. Wooded banks (24%) were positively selected. Forest (4%) was negatively selected at the habitat map level, but at the home range level the animals used it in accordance with its relative area. Other habitats were relatively scarce. Nevertheless a positive selection for ditches could be demonstrated. Premises, gardens, buildings, and paved roads were negatively selected. Arable land was not selected in either way at habitat map level, whereas the animals usually avoided it within their home range. Water was both positively and negatively selected: as the dry and hot summer progressed, some sections were transformed into habitats similar to ditches. Finally, unpaved roads were used in accordance with their relative area. 
The difference in habitat selection between wooded banks (positive) and forest (negative, or no selection), is interesting since the only basic difference concerns the linear pattern of wooded banks with grasslands or arable land on either side. At this time we can only speculate on the cause of this positive selection of wooded banks. The banks may be used for spatial orientation, resulting in a 'road function'. An attractive food source, which may be related to the nearby presence of grasslands or arable land, is another possibility. 
Practical implications of the results of this study lie within the area of mitigation. If habitat use of hedgehogs is strongly related to linear elements in the landscape, we can expect the locations of road victims to be near these elements. Whether or not this relation to linear elements is strong remains to be investigated: grasslands were the most frequently used habitat type by far. Further analyses of habitat selection within grasslands should be able to answer this question. 
 
 


 

Some data about Eastern hedgehog (Erinaceus concolor Martin, 1838) in Lithuania. 
Dr. Reda Mazeikyte
Eduardas Mickevicius 

The data of two projects which had been undertaken in 1959/61 and 1982/83 as well as other available information on hedgehog in Lithuania were summarized. 
The questionnaires sent to respondents in various places of Lithuania revealed that hedgehogs are common in the vicinity of farms (32,2% of all sightings) and in small private gardens (19,4% of all sightings). The most common hibernation sites were in barns under hay or planks (34,4% of all sites) as well as in woodsheds under logs and peat (16.1% of all sites). The importance of sinantropic habitats and hibernation sites is overestimated because respondents recorded mainly their accidental sightings of hedgehogs as well as accidental findings of hibernation sites and the number of such cases was surely higher in sinantropic habitats. 
All hedgehogs found in Lithuania belonged to species Erinaceus concolor. The average weight of females in Lithuania is 871 g, (range 608 - 960, n=7) and of males is 740 g (range 732 - 1020, n=13) (R. Mazeikyte, 1988). Females usually gave birth for one - two litters per year. The first litters are born in late May, the second litters - probably in August. Females with blind nestlings usually are found in early June. Average number of nestlings per litter is 4.2 (range 1-9, 40 litters). 
A few hedgehogs were examined in search of endoparasites. 1 species of Trematodes (Euparyphium melis) and 5 species of Nematodes (Crenosoma striatum, Thominx aerophilus, Capillaria erinacei, Physaloptera clausa, Physocephalus sexalatus) had been found. 
Attempts to ascertain hedgehog mortality on the roads off Lithuania were made. A greater number of killed hedgehogs was usually found on the roads in settlements and in gardens when comparing it with the number of mortalities on other roads. It was revealed that hedgehog losses can be rather high. In one case 6 hedgehogs were killed by traffic on 11 km long road segment (1.8 hedgehog/km) during one rainy night in the middle of August, 1982. 
 
 


 

Hedgehog Rehabilitation in Perspective 
P.A. Morris
Royal Holloway College, University of London

Several thousand British hedgehogs are taken into care each year; mostly injured animals or small, late-born young unlikely to survive hibernation. Those which survive are released back into the wild, mostly in spring, but until recently there was little information on their post-release welfare, behaviour and survival. A number of studies have now been undertaken in different regions of Britain which show that the majority, both adults and juveniles who had never experienced independent life in the wild, survived surprisingly well. They found both food and nest sites, made nests and very rapidly leamed their way about. All lost weight intially but, after two to three weeks, they stabilised at a similar weight to wild caught animals. Those which were heaviest at release lost the greatest percentage of their weight. This suggests that they were heavier than normal at the end of their captivity but this may facilitate their survival during the intial period of life in the wild. Those hedgehogs which did not survive (22%) included two road casualties and three eaten by badgers; misfortunes which might happen to any hedgehog. It is possible that their susceptibility to badger predation may be increased by tameness acquired during captivity. Nevertheless, all these hedgehogs would have died anyway had they not been taken into care. That so many survived, so successfully, after release indicated that the work of carers is certainly beneficial. 
 
 


 

The survival and welfare of hedgehogs (Erinaceus europaeus) after release back into the wild
Nigel J. Reeve 
(School of Life Sciences, Roehampton Institute London, West Hill, London SW15 3SN) 

The fate of rescued hedgehogs released back into the wild after a period of captive care has now been the subject of a few follow-up radio-tracking studies. Despite being subject to a number of hazards, released hedgehogs clearly show essential 'life-skills'. However, all studies have involved releases into hedgehog-rich areas and the observed long-range dispersal movements shown by some subjects could be a consequence of local intraspecific competition. The present study has reduced a number of potentially confounding subject variables and provides follow-up data on 12 age-matched female hedgehogs with similar histories. A main group (n--10) was released into a rural woodland area (Surrey, UK) of low natural hedgehog density and low badger activity, and were radio-tracked for up to 108 days. A pilot release of 2 animals in an urban area with an established hedgehog population also took place (tracked for 109-131 days). Most of the main study group dispersed from the release site, those in the urban site did not. This suggests that dispersal is not specifically the result of intraspecifie competition. Observed behaviour and patterns of weight change were similar to those previously reported. Overall survival at 8 weeks was 6 (50%) plus two lost animals; comparable with previous studies but down to 3 (25%) plus 2 lost animals by week 15. Of 7 recorded deaths, only one was the result of a failure to thrive and all other deaths (4 road deaths, 1 drowned in a pond, 1 badger predation) were accidental. The study concludes that the hazards of the human environment seriously threaten the welfare and survival of both released and wild hedgehogs in the area. Further studies involving the release of similar groups with concurrent monitoring of a matched cohort of wild hedgehogs are planned. 
 
 


 

Heavy metals in the European hedgehog Erinaceus europaeus 
Richard F. Shore (1), Nigel Reeve (2), Paul Freestone (1), David G. Myhill (1), Beverley Love (2), Mathew Grafton (1) 
1 Institute of Terrestrial Ecology, Monks Wood, Abbots Ripton, Huntingdon, Cambridgeshire PE17 2LS, UK. 
2 Biological and Chemical Sciences, Roehampton Institute, Whitelands College, West Hill, London SW15 3SN, UK. 

Many invertebrate species are good metal accumulators. As a result, mammals which prey on invertebrates can ingest a metal-rich diet in contaminated areas. Hedgehogs have a predominantly invertebrate diet and can be relatively long-lived; some heavy metals, such as cadmium, accumulate with age. Therefore, it is possible that hedgehogs may accumulate large amounts of heavy metals. However, there do not appear to be any published data on heavy metal residues in the Erinaceidae. In the present study, we collected 67 dead hedgehogs from three sources, road kills in the Cambridgeshire area (n=38), animals which died in rehabilitation hospitals (n=19) and road-kills from the Avonmouth/Bristol area (n=10). All animals were aged by assessing the degree of epiphyseal fusion in the bones of the manus and forelimbs and counting the number of growth lines in sections of the lower jaw. The concentrations of the pollutant metals cadmium (Cd), lead (Pb), mercury (Hg), and the essential trace elements copper (Cu) and zinc (Zn) were measured in the liver, kidney and femur of each animal. Heavy metal residues in/on the prickles were also measured to determine whether these were correlated with levels in the body organs. Residues varied significantly in magnitude between the different tissues analysed for all five elements. The highest median concentrations (m g g-1 DW) were in the kidney for Cd (7.52) and Hg (4.2) and in the liver for Cu (85.3) and Zn (281); median Pb concentrations were highest in the femur (18.9) although they were similar in the liver (12.5). Although median levels of the pollutant metals were generally low, some individual animals had high kidney burdens, the maximum concentrations detected being 290, 100 and 780 m g g-1 DW for Cd, Pb and Hg respectively. These concentrations are above those associated with adverse physiological effects in mammals. There were no consistent differences between males and females in residue magnitude. Cd and Hg increased significantly with age in the liver and kidneys as did Pb in the kidney and femur. Cd concentrations also varied significantly between animals from different locations and were highest in males from the Avonmouth/Bristol area, an area of known Cd contamination. Cu and Zn levels were significantly correlated with the levels of the pollutant metals in both the liver and the kidney. Residue levels in unwashed prickles were significantly correlated with concentrations in the body organs but only for Pb (all three tissues) and for Cu (kidney only). The results of this study demonstrate that hedgehogs are exposed to and accumulate heavy metals, that Cd, Pb and Hg burdens increase with age (presumably because of increased length of exposure) and that some animals are likely to suffer adverse physiological effects as a result of their heavy metal burdens. The study has also demonstrated that analysis of prickles may be of use in predicting the body organ concentrations of Pb (but not Cd and Hg) and so might potentially be a useful biomonitor of Pb pollution. 
 
 


 

Does road mortality affect hedgehogs (Erinaceus europaeus)?
Marcel P. Huijser (l) & Piet J.M. Berger (2) 
1 Vereniging voor Zoogdierkunde en Zoogdierbescherming (VZZ) Emmalaan 41, 3581 HP Utrecht, The Netherlands 
2 Institute for Forestry and Nature Research (IBN-DLO), Department of Landscape Ecology, P.0. Box 23, 6700 AA Wageningen, The Netherlands 

Hedgehogs are one of the most common road victims among mammals. Only a limited number of studies have focused on quantifying road mortality in combination with population size and losses. However, these studies do not address the question whether the size, presence or structure of populations is affected by road mortality or not. There are two basic strategies to answer this important question: 1. to build a population model on which road mortality may be simulated (bottom-up), and 2. to determine whether the size or presence of the populations is affected to such an extend that we are able to measure it in the field (top-down). 
The first strategy involves great effort. Many 'hard to get' data have to be collected, and in many cases frequency diagrams are needed in addition to estimates or averages. Some examples of the data required are estimates on the number of road victims per km road and their relation to traffic intensity and road type, population densities in various landscapes, population structure with respect to sex and age, reproductive success, and survival rates. Only a combination of the results of several studies may one time lead to a situation where enough data will have been collected to build such a model. 
The second strategy may require less effort and time. If a relatively simple method can be developed to determine (relative) population size, a number of locations can be visited in a relatively short amount of time. Relative population sizes on locations in the direct proximity of (main) roads can be compared with those where we can expect the influence of road mortality to be negligible. 
Both approaches have advantages and disadvantages. As far as the model approach is concerned, we may make an inventory at this workshop on who would like to contribute, and what data are available at this time. A pilot study, in which relative population sizes are determined (second approach), will by carried out by the VZZ this summer. A short introduction to our materials and methods will be given, and is open to discussion. 
 
 


 

Some remarks for raising orphaned hedgehog babies
Monika Neumeier
pro Igel e.V., Germany 

In 1995 we got new facts about the composition of hedgehog mother's milk by a dissertation of a German vet. This is essential to find out the best substitute milk for orphaned hedgehog babies. Details about the natural mother's milk and the substitute milk will be given in that talk. The results of practical experiences of various nurses from all over Germany and the difference between handraised babies and babies raised by the natural mother will be shown and explained by overhead diagrams. 
 
 


 

Tasks of the FG 
Marking problems for identification 
Manfred Schubert
Forschungsgruppe Igel, Germany 

The main task of the FG was originally to clarify if hibernation in human care is useful, a contrivers question among experts. Besides we wanted to find out how strong the conflict was between protectors of species and protectors of animals in the former German Democratic Republic.
The species protectors turned strictly hibernation in human care. They pointed out that this would damage the populations more than it would help. The animal protectors approved it vehemently. They argued that the taking in of those in need is only responsibility of animal protectors, but not of species protectors.
To be able to give a sound statement we started to make our own tests with various groups of hedgehogs under different owning conditions. But very soon it turned out that our tests wouldn't leed us to a useful result. We had to investigate more details about
· integration into existing populations 
· participation in reproduction 
· life expectancy 
· age structures of the observed population. 
For this purpose a great number of longtermed data's were necessary, if possible during the whole lifetime of an individual and with as much animals as possible. This required an incontestable identification of the individuum over a long period of time.
In this talk we will discuss various methods from our point of view, explain the method we have chosen, the pros and cons and we will talk about our experiences.
 
 


 

Recapture rates 
Manfred Schubert
Forschungsgruppe Igel, Germany 

This report shows that safe markings make it possible to obtain facts about essential biological datas. The observation area is characterized and the difficulties working in settlement areas are described. Feeding methods and the preparation of diet are explained. 
From the veterinary medical point of view dangers for the hedgehogs by mass and/or intensive owning are pointed out. The importance of desinfection is mentioned. 
Problems how to get enough people at any time for the long-term observations are explained. Cumulative and annual recapture rates are discussed with examples of transparencies. 
For the first time data's of so-called long-term recaptures are shown and discussed. This concerns 58 findings from the years 1984/89, which means a period of 6 years with a difference of 9 months between the findings. 
 
 


 

How does hibernation vary with latitude? 
P A Morris
Royal Holloway College, University of London 

Hedgehogs arouse during hibernation, even in constant laboratory conditions. In the wild (at least in Britain) it is unusual for them to remain in the same nest throughout the winter, again suggesting that they awake normally, perhaps in response to warmer weather, then resume hibernation. It is reported in the popular press that hedgehogs are becoming active in February as a result of global warming, but this is nothing new. Many books give dates for hibernation, but it is not clear what is the scientific basis for such statements, when the animal's behaviour seems to be quite variable. It is possible that the average dates of starting and ending hibernation vary according to latitude (reflecting different climatic conditions, particularly longer winters further north). An attempt has been made to use roadkill data to investigate regional variations within Britain. The results suggest that there may be small differences between the north and south of Britain in hibernation behaviour, but these are probably not statistically significant. However, a similar study across Europe might yield more conclusive results. Longer hibernation means a shorter breeding season. This has an impact on life strategies. Perhaps shorter breeding seasons mean few litters can be raised and litters need to have a higher mean size. Again, comparative data would be interesting. There must be a limit to the way that increased litter size can compensate for fewer litters. Perhaps the squeezing of the breeding season, and limited maximum litter size are factors that control distribution in northern Europe? Conversely, in New Zealand, hibernation is barely necessary at all in the North Island. Two litters, perhaps even three may be raised in a year. Perhaps as a result, the average hedgehog population density in New Zealand is probably at least 5 times higher than in Britain. 
 
 


 

Breeding biology of hedgehogs in Britain 
P A Morris
Royal Holloway College, University of London 

In captivity, hedgehogs can produce three litters in a year, especially if they lose an early litter. In the wild it is unlikely that they ever do so, because the breeding season is not long enough. In Britain, there are a significant number of litters born late in the year (eg in September), but it is not clear whether these are second litters or the first litters born to animals that were too young to breed earlier that year. Anyway, these late born young must attain a weight of at least 450g to be fat enough to survive the winter. Many fail to do so and die. Thus, late litters probably do not add significantly to the size of the breeding population in the following year. Mean litter size is about 4.6 in Britain, based on embryo counts. Does it differ elsewhere in Europe? A simple study was initiated, asking the public for observations on the size of litters found in accidentally- discovered hedgehog nests. The observations were divided into 'early' and 'late' young, based on appearance. Family size was also noted where babies were seen with their mother. This study suggests that nearly 20% of young hedgehogs die before weaning, with the possibility that large litters may be lost entirely. Pre-weaning mortality has rarely been studied in other mammals. However, this study could easily be repeated in other European countries to obtain comparative information about hedgehog reproductive success. 
 
 


 

Breeding, mate selection & courtship behaviour in the hedgehog (Erinaceus europaeus)
Nigel J. Reeve 
(School of Life Sciences, Roehampton Institute London, West Hill, London SW15 3SN) 

There remain serious gaps in our knowledge of the breeding biology and sexual behaviour in hedgehogs and many ideas and predictions remain to be tested with field data. In England, sexual activity in hedgehogs occurs principally from May to mid-August, although courtship or pregnancies may occur from March to October. It is widely stated that hedgehogs in Britain may sometimes bear two litters in a season, but no field studies have ever confirmed this. Preliminary studies have shown that both sexes may court multiple partners but over M of 76 observed courtships did not result in mating. Mate-guarding was never observed. This, and other preliminary research has raised many questions about mate selection, the possibility that females may accept multiple matings, the likelihood of competitive exclusion of rivals by male suitors and many other key issues. This paper discusses the limited information gathered so far, and considers the requirement for further work. Previous captive studies have indicated the apparent deployment of odour cues during courtship but such behaviours have never been systematically observed in a natural context. The possible role of self-anointing is also considered. There is an urgent need for more rigorously collected physiological and behavioural data that could improve our functional interpretation of breeding biology, courtship behaviour and its adaptive consequences. Such data would improve our ability to make population viability assessments of hedgehogs where their populations are under threat from factors such as predation, road mortality, or habitat degradation. 
 
 


 

Urban hedgehogs in Zurich, Switzerland: spatial distribution and habitat use. 
Bontadina, Fabio: Gloor, Sandra & Hotz, Therese 
Arbeitsgemeinschaft Stadtökologie Zürich, Hohlstrasse 86a, CH-8004 Zürich, Switzerland. 

An urban hedgehog population was studied by means of radio tracking in the city of Zurich (360'000 inhabitants, 6500 ha urban area) in 1992. In order to get information on spatial distribution and habitat use, 11 individuals were fitted with a transmitter and followed during 35 complete nights. Additionally in a public inquiry of 20'000 inhabitants interested in nature and animals 1383 observations of hedgehogs were collected. These observations showed, that hedgehogs are distributed over a large part of the city (69% of the total urban area). Estimations in two core study areas showed, that hedgehogs can be quite abundant (0.5 - 1 hedgehog / ha). On the other hand in the city centre there are areas with very few or no hedgehogs at all. The low abundance of hedgehogs in those areas is correlated with a very high degree of build over space with lots of houses, streets, places etc. and very little open space such as parks, gardens etc. 
The observations of the radio tracked individuals showed, that during their nightly activity 
hedgehogs prefer to stay in backgardens, on green lawn around apartment houses, in courtyards with open space (lawn, garden etc.) and in large gardens or parks with hedgerows and trees. Normally hedgehogs search for food on lawns and short cut meadows, but also under bushes or near compost heaps. The average maximal nightly radius of urban hedgehogs (237+-169m, n= 16 nights of 9 males) was substantially shorter than the distances of rural hedgehogs, therefore the home ranges of urban hedgehogs were smaller than those of rural hedgehogs.