Population status and feeding habits of the translocated sub-population of Hunter's antelope or hirola (Beatragus hunteri,Sclater, 1889) in Tsavo East National Park,Kenya

The population status and feeding habits of Hunter's antelope or hirola (Beatragus hunteri) in Tsavo East National Park were determined in this study in 1995. This is the first study that has ever been undertaken on the hirola population of about 20 animals that were translocated to Tsavo East National Park from South Garissa District in 1963. Relevant data and information were collected using different ecological research techniques. A total of eight nursery herds (5–11 individuals per herd) comprising 60 individuals, five lone bulls and 11 lone sub-adults was observed. This gave a total population estimate of 76 animals in the entire study area. Adult animals dominated the population (60.53%), indicating a population skew towards adults. The adult sex ratio was biased towards females (43.42%). Hirola were observed to feed mainly on short, green grasses. The dominant feed species were Panicum infestum, Digitaria rivae, Latipes senegalensis and Cenchrus ciliaris. Occasionally, hirola was observed to feed on forbs (e.g. Portulaca oleraceae, Tephrosia subtriglora and Commelina erecta). Results of this study show that the population growth of the hirola sub-population in the Park has been low (1.8 individuals per year). Factors thought to contribute to this low growth include predation and low genetic variability.     

THE USE OF GAME TRAILS AS A POSSIBLE MEASURE OF HABITAT UTILISATION BY LARGER MAMMALS

Percentage cover of game trails is discussed as a possible measure of total habitat utilisation by larger mammals and a technique for its measurement is described. Game trail cover in Tsavo National Park (East) at Voi has been analysed in two areas, woodland and grassland. Of these the woodland had the higher trail cover (10.69%) and grassland the lower (7.57%). The interpretation of these results is discussed.     

STUDIES ON THE FOOD HABITS OF LESSER KUDU IN TSAVO NATIONAL PARK, KENYA

As part of a broader ecological investigation, in the framework of the Tsavo Research Project, food habits of lesser kudu have been studied during 2 y in Tsavo National Park (East). Free-ranging lesser kudu were observed, from a Land Rover, while feeding in different habitats and at different times of the year. Each time one animal fed on one individual plant was noted as one “food record”; some 2000 records are analysed in this paper. Leaves of trees and shrubs constitute the main bulk of the diet of lesser kudu. Creepers and vines, herbs, grasses, fruits and tubers of some root succulents contribute variable but relatively small proportions of the food. Pronounced local and seasonal variations in the composition of the diet were found. Local variations are mainly a result of differences in the vegetation of the different habitats. Seasonal variations are caused by changes in the vegetation's condition, depending on rainfall. Deciduous trees and bushes, herbs, climbers and grasses account for much smaller proportions of the diet during the dry season, when evergreen species are crucial for survival. Lesser kudu feed on a wide variety of plants, utilizing all layers of the vegetation that they can reach, at least to some extent. A total of 105 plant species have so far been recorded as being eaten by lesser kudu. With regard to food only, the vegetation changes in Tsavo National Park do not appear to have had any adverse effects on the population of lesser kudu. However, the amount of suitably structured habitat has been substantially reduced in recent years. If present trends continue, it may decrease further, to the point of jeopardizing the future of lesser kudu in large parts of Tsavo National Park.     

FOOD PREFERENCES OF BLACK RHINOCEROS IN THE TSAVO NATIONAL PARK

Food preferences of the black rhinoceros population in Tsavo National Park, Kenya were studied from 1967 to 1969. Feeding rhinoceros were watched for a period of 1 h, and the plants which they selected and rejected were identified, either as they were feeding or when they had moved on. A technique was used which provided an indication of the relative importance of certain plants in the diet during the wet and dry seasons. A total of 70 h was spent actually watching feeding rhinoceros in six habitat types representative of the changing ecosystem; 3,600 feeding stations were examined. Black rhinoceros were observed eating 102 species from 32 botanical families. In all habitat types the rhinoceros is very selective for herbs and shrubs, and shows a marked preference for legumes. Available grasses are very rarely eaten. Results of food preference studies in other areas of East Africa are compared with the present study. It is suggested that the abundance and distribution of certain kinds of leguminose flora may be the key to an optimum black rhinoceros habitat.     

The forgotten Grevy's zebra Equus grevyi population along the Kasigau Corridor ranches,SE Kenya: recent records and conservation issues

Since the 1970s, the globally endangered Grevy's zebra Equus grevyi has suffered a substantial reduction in range and population size. Grevy's zebra was introduced into the Tsavo ecosystem in two translocations: 22 individuals released in Tsavo East National Park in 1964 and 30 individuals released in Tsavo West National Park in 1977. This study focuses on the Tsavo East subpopulation within the Kasigau Corridor REDD+ Project Area. Data were collected from 2011 to 2014 using systematic and ad lib methods, while vegetation stratification was based on tonnes of CO₂e per hectare. Cumulatively, 785 Grevy's zebra were seen in 210 encounters. The largest single group comprised of 24 individuals; mean group size was 4 ± 3. Foals comprised 10% of all individuals seen and were recorded across most months, suggesting year‐round breeding. The range core for the Grevy's zebra in this area was estimated to be 400 km². Its density was estimated at 0.09 ± 0.038 individuals per km², translating to a population of 36 ± 15 individuals (range: 6–67) based on the estimated core range. Grasslands and sparse Acacia–Commiphora vegetation strata were used significantly more than expected. Despite constituting only about 2–3% of the global Grevy's zebra population, this subpopulation could still play a role as a – disconnected – reserve population.     

Distribution, abundance and niche breadth of birds: scale matters

We used local habitat niche breadth, local abundance and body size of non-passerine afrotropical birds in Tsavo East National Park (Kenya) to predict species distributional ranges in Kenya and across Africa. Univariate analysis revealed a significant positive correlation between local abundance and distribution only on the scale of Kenya. Performing a multiple regression analysis, local abundance, local habitat niche breadth and body size explained a significant part of the variance in bird distribution, again only on the Kenyan scale. From these results, we speculate that on continental scales distributions may be more influenced by macroclimatic conditions and historical factors, whereas distributions on regional scales are predominantly influenced by ecological factors.     

Implications of closed ecosystem conservation management: the decline of Rothschild’s giraffe (Giraffa camelopardalis rothschildi) in Lake Nakuru National Park,Kenya

Giraffe were historically free‐ranging across most of sub‐Saharan Africa but are now most often confined to national parks, conservation areas, or private ranches. Five viable populations of Rothschild’s giraffe (Giraffa camelopardalis rothschildi) remain in protected areas in Kenya and Uganda. The viable population in Uganda is Murchison Falls National Park and the four populations in Kenya are Lake Nakuru National Park (LNNP), Ruma National Park, Giraffe Manor, and Mwea Natural Reserve. The Kenya Wildlife Service queried a rapid decline in LNNP giraffe numbers falling from 153 individuals (1995) to 62 individuals (2002) and the failure of that population to recruit young in those years. Significantly reduced browse options, inbreeding depression and preferential lion predation were considered as potential reasons for this trend. Population genetic parameter estimates derived from multilocus genotype analyses suggest that the LNNP population was in good genetic health with respect to the likelihood of inbreeding depression. The population decline coincided with the drought attributed to the 1994 El Niño. Possible dietary complications from highly concentrated tannin levels because of forced over consumption of the park’s declining acacia trees may have compromised young giraffe, making them easy and opportunistic prey for the park’s lion population.     

Food habits of giraffe in Tsavo National Park, Kenya

In the context of a broader ecological investigation, food habits of giraffe were studied in Tsavo National Park (East). The only method employed was direct observation of feeding animals in the field. Each instance in which one animal fed on one individual plant was counted as one food record for this plant species; 4025 records are analysed. A total of sixty-six plant species was found to be eaten, the great majority being trees and shrubs, with a few creepers and vines. There were marked seasonal differences in the diet of giraffe, deciduous trees, shrubs and vines being dominant in the green season, evergreen plants (partly in riverine forest) in the dry season. All the trees and larger shrubs common in the study area were eaten by giraffe, while few records for very small shrubs and none for herbs and grasses were obtained. An analysis of the available vegetation was made in part of the dry-season habitat, and for twenty species the frequency in the habitat was compared with the frequency in the giraffe's diet, revealing selection for or against certain species. Giraffe utilized the upper vegetation layers, where available, but overall c. 50% of all browsing was below 2 m above ground, i.e. within reach of smaller browsers. Results of this study are compared with what is known on food habits of giraffe in other areas. Possible competition of giraffe with other browsers and the relationship between giraffe and their habitat are discussed. Continued survival of giraffe, and other browsers, in Tsavo National Park depends primarily on (1) adequate control of fire, and (2) the impact of future vegetation changes on the amount and variety of available browse plants.     

Relationship between group dynamics and spatial distribution of African elephants in a semi‐arid environment

Group dynamics related to distribution of African elephants in the semi‐arid environment of Tsavo East National Park, Kenya was studied between 2007 and 2010. I examined the seasonal distribution of lone bulls, bull groups, family units and mixed groups and group size. Lone bulls were widely distributed in the dry season and localized in the wet season, whereas bull groups were localized in both seasons. On average bull group size did not differ with seasons or areas, but larger groups were observed in preferred areas in the dry season. Family units were widely distributed in the dry season and localized in the wet season, whereas mixed groups were localized in both seasons. Although family units and mixed groups tended to be large in all areas in the wet season, large groups were also observed in the dry season. Large family units were widely distributed, whereas large mixed groups were localized. The relationship between group dynamics and distribution was attributed to the combination of social, ecological and poaching factors. This study provided insight into distribution patterns that can be applied to the security of the Tsavo elephant population.     

The Status of Wildlife in Protected Areas Compared to Non-Protected Areas of Kenya

We compile over 270 wildlife counts of Kenya''s wildlife populations conducted over the last 30 years to compare trends in national parks and reserves with adjacent ecosystems and country-wide trends. The study shows the importance of discriminating human-induced changes from natural population oscillations related to rainfall and ecological factors. National park and reserve populations have declined sharply over the last 30 years, at a rate similar to non-protected areas and country-wide trends. The protected area losses reflect in part their poor coverage of seasonal ungulate migrations. The losses vary among parks. The largest parks, Tsavo East, Tsavo West and Meru, account for a disproportionate share of the losses due to habitat change and the difficulty of protecting large remote parks. The losses in Kenya''s parks add to growing evidence for wildlife declines inside as well as outside African parks. The losses point to the need to quantify the performance of conservation policies and promote integrated landscape practices that combine parks with private and community-based measures.     

OBSERVATIONS ON THE CHANGING VEGETATION OF TSAVO NATIONAL PARK (EAST)

An analysis of woody vegetation in Tsavo National Park (East) by extensive variable-plot sampling indicates that the vegetation had been differentially destroyed up to 1966, but that by 1967 considerable local shrub regeneration had taken place. This may indicate that Commiphora woodland will become re-established over much of the park.     

De Brazza's monkeys (Cercopithecus neglectus) in Kenya: Census,distribution, and conservation

The population of De Brazza's monkeys (Cercopithecus neglectus) in Kenya, East Africa, was surveyed from May to September of 1983 to estimate its numbers, distribution, and conservation status. A small number of De Brazza's monkeys are protected within Saiwa National Park; however, the vast majority of the population is endangered because they are restricted to small, isolated pockets of forests amid expanding farmland within the Trans-Nzoia area of western Kenya. A few animals are found on the slopes of Mt. Elgon and on the Cherangani Hills, although these areas offer little protection. The pressures now facing this population are loss of habitat, reproductive isolation, and a decline in numbers as the result of being killed, either as a food source or as agricultural pests. If the current situation continues and no attempt is made to conserve the remaining De Brazza's monkeys, the species faces almost certain extinction in Kenya.     

Primate DNA suggests long‐term stability of an African rainforest

Red colobus monkeys, due to their sensitivity to environmental change, are indicator species of the overall health of their tropical rainforest habitats. As a result of habitat loss and overhunting, they are among the most endangered primates in the world, with very few viable populations remaining. Traditionally, extant indicator species have been used to signify the conditions of their current habitats, but they have also been employed to track past environmental conditions by detecting previous population fluctuations. Kibale National Park (KNP) in Uganda harbors the only remaining unthreatened large population of red colobus. We used microsatellite DNA to evaluate the historical demography of these red colobus and, therefore, the long‐term stability of their habitat. We find that the red colobus population throughout KNP has been stable for at least ~40,000 years. We interpret this result as evidence of long‐term forest stability because a change in the available habitat or population movement would have elicited a corresponding change in population size. We conclude that the forest of what is now Kibale National Park may have served as a Late Pleistocene refuge for many East African species.     

AGE CRITERIA AND VITAL STATISTICS OF A BLACK RHINOCEROS POPULATION

Tsavo National Park, in Kenya, probably contains the largest population of black rhinoceros (Diceros bicornis (L.)) left in existence. Large-scale damage of the vegetation initiated by elephants and aggravated by fire has changed considerable areas of the park. The ecology of the black rhinoceros in this changing environment has been studied; the present status and population structure is considered here, including the development of detailed ageing criteria for the species, an analysis of natural mortality and survivorship, and a record of the structure of the living populations within the major habitat types. Crania and mandibles were collected from 506 rhinoceros found dead in all areas of the park. This material was divided into 20 relative age classes based on dental characteristics. Crude chronological ages, based on an estimate of the maximum expectation of life and the examination of seven known-age dental records of captive animals, were assigned to each age class. These crude ages were then refined by examination of 16 dental records of known-age wild rhinoceros, and a chronological age scale established. A survivorship curve of the population was thus constructed. Annual mortality during the first and second year of life is about 16%, and the indicated mean annual mortality from 5–25 y is 9.8%. A theoretical model of the population structure is shown, and analysis of the annual mortality and recruitment at birth suggests that the population was stable during the 1960's. Assuming the data represent a stable population the mean expectation of life at birth is 8.4 y. Thirteen major habitat types are described. The characteristics of the rhinoceros population within each habitat type were established both from ground studies and aerial observations. Nearly 700 rhinoceros were identified and catalogued on the ground, in sample areas selected for intensive study. Population structures, cow: calf ratios, and recruitment appear to be average in most habitat types. The analysis of recruitment at birth and mortality during the first year of life, both from computations from the survivorship curve and from the structure of the living populations, support the validity of the ageing criteria, and further suggest that the population was stable during the 1960's. Finally, the relationship between the elephant and the rhinoceros in the changing environment is discussed with reference to recent findings in elephant ecology. In conclusion it is recommended that population reduction of the Tsavo elephants should be initiated.     

An investigation of habitat occupancy by the nightingale Luscinia megarhynchos with respect to population change at the edge of its range in England

The nightingale Luscinia megarhynchos has undergone population decline and range contraction at the north-western limit of its distribution in England during the last 25 years. We examine patterns of habitat occupancy and habitat availability across sites with a range of population histories to see whether habitat loss is a plausible explanation for these declines. The number of singing males in 1999 correlated with area of primary nightingale habitat in the East Midlands (where the species has declined), but not in East Anglia (where the population has been stable). Change in population size between 1980 and 1999 and current habitat availability were weakly correlated in the East Midlands but not in East Anglia. These results are consistent with habitat loss having contributed to the decline of the nightingale in the East Midlands, but suggest that other, wider-scale, factors may be at least partially responsible for determining the abundance of the species within England as a whole.     

基于无人机遥感的三江源国家公园藏野驴种群数量及生境时空变化研究

藏野驴（Asinus kiang）是青藏高原特有物种,我国一级野生保护动物。三江源国家公园黄河源园区是藏野驴的主要栖息地之一,而生物多样性保护也是国家公园的重要职能,准确了解藏野驴的种群数量及栖息地变化无论是从野生动物保护还是从国家公园建设指导来看均具有重要意义。以三江源国家公园黄河源园区为研究区,利用无人机遥感技术开展藏野驴种群数量调查工作,在此基础上利用选择指数与因子分析揭示藏野驴的生境选择偏好,识别其适宜栖息地范围。并深入探讨近20年藏野驴适宜栖息地的时空变化特征,探讨驱动因素。结果表明：（1）无人机可以有效识别藏野驴个体,在调查样带内共发现藏野驴252头,经过推算2017年春季三江源国家公园黄河源园区内共有藏野驴20989头。（2）藏野驴倾向于选择距居民点1 km以外,距道路1-3 km范围内,距水源1 km以内,且植被覆盖度介于0.4-0.8之间的坡度小于5°的平坦区域做为栖息地。（3）2000-2018年间,三江源国家公园黄河源园区内的藏野驴适宜生境面积增加了330.76 km²,达到4747.10 km²,面积占比增加1.73%,达到了24.85%。这主要是气候变化与人类活动协同作用下导致的水体扩张与植被覆盖度增加驱动的。此外,虽然道路的扩张仅限制了小面积的适宜栖息地增加,但可能造成栖息地连通性下降等更为严重的后果。本研究证明了无人机遥感技术在青藏高原等开阔区域进行野生动物调查及栖息地研究的可行性与优势,相关技术方法与研究成果可为三江源国家公园生物多样性保护工作提供参考与支撑。     

Variation of tsetse fly abundance in relation to habitat and host presence in the Maasai Steppe,Tanzania

Human activities modify ecosystem structure and function and can also alter the vital rates of vectors and thus the risk of infection with vector‐borne diseases. In the Maasai Steppe ecosystem of northern Tanzania, local communities depend on livestock and suitable pasture that is shared with wildlife, which can increase tsetse abundance and the risk of trypanosomiasis. We monitored the monthly tsetse fly abundance adjacent to Tarangire National Park in 2014–2015 using geo‐referenced, baited epsilon traps. We examined the effect of habitat types and vegetation greenness (NDVI) on the relative abundance of tsetse fly species. Host availability (livestock and wildlife) was also recorded within 100×100 m of each trap site. The highest tsetse abundance was found in the ecotone between Acacia‐Commiphora woodland and grassland, and the lowest in riverine woodland. Glossina swynnertoni was the most abundant species (68%) trapped throughout the entire study, while G. pallidipes was the least common (4%). Relative species abundance was negatively associated with NDVI, with greatest abundance observed in the dry season. The relationship with the abundance of wildlife and livestock was more complex, as we found positive and negative associations depending on the host and fly species. While habitat is important for tsetse distribution, hosts also play a critical role in affecting fly abundance and, potentially, trypanosomiasis risk.     

Population status and human impact on the endangered Swayne’s hartebeest (Alcelaphus buselaphus swaynei) in Nechisar Plains,Nechisar National Park,Ethiopia

The study on the population status and human impacts on the endemic and endangered Swayne’s hartebeest (Alcelaphus buselaphus swaynei) was carried out in Nechisar Plains, Nechisar National Park, between 2009 and 2010. Direct and total count methods were applied in the population census. Data collected since 1967 were also examined to indicate trends of Swayne’s hartebeest populations and their translocation status. In eight illegal Guji Oromo settlements, a total of 134 household samples were identified for group discussion and interview. A trend on livestock population was carried out. The total count of Swayne’s hartebeest was 12, 11 and 12 during the 1st, 2nd and 3rd counts, respectively. The population has been decreasing and nowadays only 12 individuals remain. Most respondents had a negative attitude towards conservation areas. The increase in livestock population from 1985 to 1996 was 47.8%. It also increased by 49.9% and 56.5% during 2006 and 2010, respectively. There were 12,531 heads of livestock that depended on the grass plains illegally. Overstocking rate of livestock, illegal resource exploitation and loss of wildlife habitat were the major problems encountered. Active measures have to be implemented to control the human impact and safeguard the future of Swayne’s hartebeest.     

Defaecation by African elephants (Loxodonta africana africana (Blumenbach))

A study of defaecation in the African elephant was carried out at the Voi headquarters of the Tsavo (East) National Park. Four orphaned animals aged between 1 and 10 years were observed for 4 days and 3 nights. During the day the time and weight of each individual's defaecation was recorded while at night only the time of defaecation. Details of all the records are presented. Analysis has shown that the amount of dung produced with each defaecation bears a similar characteristic to that of the growth curve of these animals. The rate of defaecation does not vary significantly with age. Records of defaecation arranged by time demonstrate an apparent periodicity with a low peak mid-morning and a high peak mid-afternoon. The potential use of this information in feeding and population studies is discussed.     

Patterns of social grouping in ungulates of Tsavo National Park, Kenya

The paper presents data on group size frequencies and mean group sizes in 11 species of ungulates and, for seven of them, more detailed information on the composition of groups in Tsavo East National Park, Kenya. In several species, mean group size was higher in a part of the study area with more open vegetation. No significant seasonal variations in mean group size were found, except in waterbuck which concentrated markedly in one location during the dry season. Minor local or seasonal variations in the proportions and/or sizes of different group types were evident in most species. In general, grouping patterns were consistent with the type of social organization found in other areas for the species concerned. Frequencies and types of interspecific associations, and the possible factors underlying their formation, are also discussed.