Phenology of figs in Budongo Forest Uganda and its importance for the chimpanzee diet

This paper reports on the phenological patterns of figs in Budongo Forest, Uganda, and how it relates to chimpanzee food availability in different seasons. In addition, we analysed the dung of chimpanzees to understand the composition of fruits in their diet. The aim of our study was to assess Ficus phenology and how it affects chimpanzee diet. Fifteen species of figs were monitored for fruit (syconium) and leaf phenology between June 2000 and 2001. Ficus fruit production varied significantly between and within species, and also with tree trunk and crown diameters. Fig fruit production was asynchronous and individual fig trees produced crops from one to five times in a year. In addition to fruits, chimpanzees fed on young leaves of some Ficus species. Shedding of old Ficus leaves coincided with the dry season, followed by appearance of young leaves. The dry season in Budongo is a period of general fruit scarcity. The combination of fig fruits and young leaves make up the most important food in the diet of chimpanzees. From the chimpanzee dung, more than 78% of seeds comprised fig ‘seeds’ (nutlets) and the rest of the diaspores were from other tree species. Our findings suggest that chimpanzees disperse large number of diaspores in their dung, thereby serving as important agents of natural forest regeneration.     

Binding of human complement C8 to C9: role of the N-terminal modules in the C8 alpha subunit

Human C8 is one of five components of the membrane attack complex of complement (MAC). It is composed of a disulfide-linked C8alpha-gamma heterodimer and a noncovalently associated C8beta chain. The C8alpha and C8beta subunits contain a pair of N-terminal modules [thrombospondin type 1 (TSP1) + low-density lipoprotein receptor class A (LDLRA)] and a pair of C-terminal modules [epidermal growth factor (EGF) + TSP1]. The middle segment of each protein is referred to as the membrane attack complex/perforin domain (MACPF). During MAC formation, C8alpha mediates binding and self-polymerization of C9 to form a pore-like structure on the membrane of target cells. In this study, the portion of C8alpha involved in binding C9 was identified using recombinant C8alpha constructs in which the N- and/or C-terminal modules were either exchanged with those from C8beta or deleted. Those constructs containing the C8alpha N-terminal TSP1 or LDLRA module together with the C8alpha MACPF domain retained the ability to bind C9 and express C8 hemolytic activity. By contrast, those containing the C8alpha MACPF domain alone or the C8alpha MACPF domain and C8alpha C-terminal modules lost this ability. These results indicate that both N-terminal modules in C8alpha have a role in forming the principal binding site for C9 and that binding may be dependent on a cooperative interaction between these modules and the C8alpha MACPF domain.     

Patterns of frugivory of the Budongo Forest chimpanzees, Uganda

Frugivory patterns of the chimpanzees in the Budongo Forest Reserve, Uganda were studied between June 2000 and August 2001. Chimpanzee feeding habitats, movement, group size and food eaten were assessed using focal and scan sampling. It was found that fruits were scarce during the dry season, when chimpanzees appeared and moved in large groups over long distances and raided farms at the forest edge. Chimpanzee movement out of the forest to forage was influenced by seasonal fluctuations in availability of preferred foods as some cultivated crops are perennial. Presence of chimpanzees in a specific feeding habitat was related to the availability of edible fruits both within and between months, suggesting that the presence of food may influence chimpanzee movement patterns. Therefore, a good understanding of patterns of frugivory is essential for making informed decisions about conservation of chimpanzees and other frugivores like birds and monkeys in Budongo as different forest habitats are under varying human pressure because of logging and other forms of utilization.     

The ecological changes of Echuya afromontane bamboo forest, Uganda

Echuya forest reserve was gazetted in 1939 and was then mainly a bamboo forest with very few hardwood trees. However, the current ecological situation shows that hardwood trees are replacing bamboo. This study analysed the current ecological situation in relationship to past ecological changes and influences. Line transects were laid systematically at 1000 m intervals across the forest in order to describe the current vegetation variation. Echuya forest has changed in size and composition from 1954 to the present. The area occupied by pure bamboo has decreased from 20.5% to 12.5%, bamboo–hard wood mixture decreased from 48.2% to 26.2% and pure hardwood stands increased from 16% to 51%. It can be suggested that the exclusion of fire, herbivores and human activities after reservation of Echuya have gradually led to the conversion of the grassland–bamboo ecosystem into a hardwood forest ecosystem. Macaranga kilimandscharia Pax. is the major colonizing hardwood tree species. Most of the gaps are covered with heavy loads of Mimulopsis species climbers, which suppress bamboo growth.     

Comparing seed removal rates in actively and passively restored tropical moist forests

High rates of seed removal can impede forest recovery, but tropical seed removal studies are few and mainly from the neotropics. Little is known about the comparative influences of active restoration (i.e. planting) and passive restoration (i.e. protection of natural regrowth) on seed removal. We conducted an evaluation of seed removal in grasslands, natural forests (tropical moist semideciduous forest), and actively (21‐, 17‐, 16‐, 11‐, 8‐, and 6‐year‐old) and passively (21‐year‐old) restored forests in Kibale National Park, Uganda. We wanted to compare the effect of vegetation type, time since restoration and restoration actions (i.e. active vs. passive) on removal of seeds of five animal‐dispersed tree species during wet and dry seasons. Seeds were either fully exposed or placed in closed mesh cages or under a mesh roof. We used differential removal rates between these treatments to attribute seed removal to different animal taxa. Seed removal rate (percentage of seed removed over a 4‐day period) was highest in passively restored forests, compared with actively restored forests, grasslands, and natural forests. We detected no significant relationship between time since restoration and seed removal rates within actively restored sites. Seed removal rate from roofed treatments was not significantly different from removal from open treatments but was significantly higher than removal from closed treatments, which we interpret as reflecting the greater effect of small mammals versus insects. Smaller seeds tended to be removed at a greater rate than larger seeds. We discuss the implications of these findings for forest regeneration.     

Colonization of woody seedlings in the understory of actively and passively restored tropical moist forests

The status of woody seedling colonization gives clues about the self‐sustainability of restored forests, a tenet of restoration success. Little is known about woody seedling colonization in restored afrotropical forests. We evaluated effects of restoration methods (active vs. passive), sampling year, restoration age, and distance from old‐growth forests on seedling colonization in restored afrotropical moist forests. Seedlings were measured in 2011 and 2014 in 71 clusters of 284 permanent sampling plots (12.6 m² each) in actively (initially 3–16 years old) and 21 clusters of 63 plots in passively restored forests (initially 16 years old) in Kibale National Park, western Uganda. Seedlings were also measured in nearby old‐growth forests in three clusters of five plots in 2014. We determined species diversity, richness, abundance per plot, and species composition as measures of seedling colonization in restored and old‐growth forests. We found that diversity, richness, and abundance of seedlings were significantly higher in passively than actively restored forests. Diversity and richness but not abundance significantly increased between sampling years and with restoration age. Distance from old‐growth forests did not significantly affect diversity, richness, and abundance. Species composition of actively and passively restored forests was different from that of old‐growth forests after 19 years since restoration started. Our results show that passive restoration should be the preferred method for recovering afrotropical forests, and highlight the effect of continued management on biodiversity of restored forests.     

Feeding patterns of sitatunga (Tragelaphus Speki) in the Rushebeya‐Kanyabaha wetland,south western Uganda

Feeding patterns and habits of sitatunga were assessed in Rushebeya‐Kanyabaha wetland between June 2006 and July 2007. Sixty transects were cut at intervals of 250 m along which sitatunga dung piles, habitats used and diet were identified from feeding signs or plant damage. Household interviews were also conducted in villages adjacent to the wetland to understand plants and crops known to be fed on by sitatunga, type of damage, frequency of sitatunga farm visits and their methods to control crop raiding. Sitatunga mostly fed on leaves (60%) and in the wetland edge (WE) habitat (49%). Forty plant species were recorded to be eaten with herbs as majority (33%) and of crops sweet potatoes were most raided. Sitatungas are basically solitary species with 73% of the sightings being of a single individual. They had mornings and late evenings as their movement peaks and preferred to feed on broad leaved plants. There were significant relationships between both habitat use and food preferences with seasons. We predict that because of seasonal food variations, crop raiding would increase and may result into more negative attitudes by farmers to sitatunga. More research on farmers’ sensitization, population census, behaviours and ecotourism are necessary for this species conservation.     

乌干达野生动物研究中心外来黑猩猩融入笼养群体的过程

1967至1997的30年间,生活在非洲热带地区自然栖息地的野生黑猩猩数量由60万降至不足20万,至今这个数字仍在减少,因此引起了全球的关注并急需要开展迁地保护。笼养黑猩猩与野外种群一样营群居生活,为了有效进行野生黑猩猩的迁地保护,将野外捕获的野生黑猩猩个体成功引入已在动物园的黑猩猩群体中十分必要。2004年10月至2005年3月,乌干达野生动物研究中心首先开展了这一实验。同时为更好地了解外来黑猩猩融入笼养群体的过程,2006年9月至2007年1月间收集其活动数据。选取5只黑猩猩个体并记录它们的食性、行为、体重变化及身体健康状况。除直接观察和记录外,与兽医和研究中心管理人员进行合作,以获取较多笼养个体的信息。我们发现,野生个体比笼养个体多病,因此影响了它们的取食、社会行为及活动水平。尽管笼养黑猩猩有人照料,但仍具备野生个体的行为,所以,理解外来黑猩猩融入笼养群体的过程对于黑猩猩的迁地保护和就地保护是非常重要的。