Pup Retrieval in the African Bush Karoo Rat
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29 Figure8. the Limited Rank Hydrophilic Sedge and Grass Patches Within the Central Valley Bottom Wetland Provide Suitable Roost
Figure8. The limited rank hydrophilic sedge and grass patches within the central valley bottom wetland provide suitable roosting and foraging habitat for African Grass Owls. The high levels of human disturbances on the site including hunting with dogs; severely restricts the likelihood of any nests and limits potential roosting suitability. The annual burning of the site restricts the vegetative cover along the valley bottom wetland. Off-road bikes, quads and vehicle tracks transverse the entire site as well as helicopter training and landing on the site and open areas to the south of the site adjacent to the Waterval cemetery. African Grass Owls are found exclusively in rank grass, typically, although not only, at fair altitudes. Grass Owls are secretive and nomadic breeding in permanent and seasonal vleis, which it vacates while hunting or post-breeding, although it will breed in any area of long grass and it is not necessarily associated with wetlands. It marshlands it is usually outnumbered by the more common Marsh Owl (Asio capensis) 10:1 (Tarboton et al. 1987). Grass Owls nest on the ground within a system of tunnels constructed in mostly tall grass; peak-breeding activity (February- April) tends to coincide with maximum grass cover (Steyn 1982). Grass Owls specialise in large rodent prey, particularly Otomys vlei rats, although a wide range of rodent prey species, including Rhabdomys, Praomys, Mus, and Suncus, are taken (Earle 1978). Some local and nomadic movements in response to fluctuating food supplies, fire and the availability of suitable habitat can be expected (Steyn 1982). The ecological requirements of this species make it susceptible to many land-use changes impacting contemporary South Africa. -
The Ecology of Large-Spotted Genets Within an Urban Landscape and to Determine What Factors Facilitate Their Ability to Persist in an Urban Environment
i The ecology of large-spotted genets within an urban landscape Craig D. Widdows Submitted in fulfilment of the academic requirements for the degree of Doctor of Philosophy In the Discipline of Ecological Sciences School of Life Sciences College of Agriculture, Science and Engineering University of KwaZulu-Natal Pietermaritzburg Campus 2015 i ABSTRACT Urbanization is one of the most damaging and rapidly expanding forms of anthropogenic landscape modification and is having profound consequences on biodiversity worldwide. The global increase in urbanization has resulted in exclusion of many carnivore species from human- altered landscapes due to a variety of anthropogenic impacts. However, despite the negative impacts of urbanization on carnivores, certain species such as large-spotted genets (Genetta tigrina) exhibit an ability to persist within urban areas. Despite their extensive distribution range, large-spotted genets are poorly studied in comparison to other African carnivores, with a handful of studies conducted on genetics, activity patterns and diet. Furthermore, no studies have focused on their ecology in an urban environment. There have been increasing reports of large-spotted genets within urban areas throughout KwaZulu-Natal, South Africa. The mosaic of patches of native vegetation within this urban landscape provides habitats for a variety of wildlife species. The main aim of the study was to investigate the ecology of large-spotted genets within an urban landscape and to determine what factors facilitate their ability to persist in an urban environment. Residential interviews were conducted to ascertain information pertaining to behavioural observations, land use as well as wildlife conflict and public perceptions of genets. Chi-square (2) goodness-of-fit tests were used to determine significant differences in the frequency of responses. -
Karoo Bush Rat
Otomys unisulcatus – Karoo Bush Rat threats that could cause widespread population decline. However, there are potentially synergistic effects of climate change drying up wetlands and overgrazing/ browsing removing at least part of the plant food and cover that this species relies upon. Such effects on subpopulation trends and population distribution should be monitored. Regional population effects: This species is endemic to the assessment region. Its dispersal abilities are not well known. Subpopulations seem to be patchily distributed at the landscape level, according to the presence of favourable habitats. While it is likely that movements and possibly rescue effects exist between subpopulations, Emmanuel Do Linh San others might be physically and genetically isolated. Regional Red List status (2016) Least Concern Distribution National Red List status (2004) Least Concern This species occurs throughout the semi-arid Succulent Reasons for change No change Karoo and Nama-Karoo of South Africa (Monadjem et al. 2015), specifically in the Eastern, Northern and Western Global Red List status (2016) Least Concern Cape provinces, with some limited occurrence in the TOPS listing (NEMBA) (2007) None Fynbos Biome (Vermeulen & Nel 1988; Figure 1). It may marginally occur in southern Namibia but further surveys CITES listing None are required to confirm this. Regardless, the bulk of the Endemic Yes population occurs in South Africa. Kerley and Erasmus (1992) argued that the lodges built by this species are In southern Africa the Karoo Bush Rat vulnerable to destruction by fire. As a result, they is the only rodent that constructs and occupies hypothesised that this shelter-building strategy is only large, dome-shaped stick nests or “lodges”, viable in the absence of frequent burning, and therefore it generally at the base of bushes. -
The Effects of Fire Regime on Small Mammals In
The Effects of Fire Regime on Small Mammals Abstract: Small mammal species richness, abundance and biomass were determined in repre- in S.W. Cape Montane Fynbos (Cape sentative S.W. Cape montane fynbos habitats of 1 Macchia various post-fire ages, and in riverine and rocky outcrop habitats respectively too wet and too poorly vegetated to burn. In fynbos the para- 2 meters measured displayed bimodal distributions, K. Willan and R. C. Bigalke with early (2,4 years) and late (38 years) peaks and intervening troughs (10-14 years). Correla- tions with plant succession are discussed. In comparison with other ecotypes, recolonisation of burns by small mammals occurs more slowly in fynbos. Species richness, abundance and biomass of small mammals was consistently higher in riverine habitats than on rocky outcrops. The former may serve as major sources of recolonisa- tion after fire. There is no published information on the sites in each area which were analogous to sites effects of fire on small mammals in fynbos in other areas. In this way area effects although ecosystem dynamics cannot be fully resulting from differences in aspect, slope, understood without knowledge of these effects. rockiness and proximity to surface water were more Three studies have been undertaken (Toes 1972; or less eliminated. Unavoidable variation Lewis In prep; Bigalke and Repier, Unpubl.),and occurred in season, altitude and vegetation Bond and others (1980) commented on potential floristics and physiognomy. In the 2-14—year-old fire effects in the Southern Cape mountains. The areas, trapping sites included vegetation present pilot study took place in S.W. -
Sistema De Túneles Del Jerbo Iraní (Alloctaga Firouzi Womochel, 1978)
ISSN 0065-1737 Acta Zoológica Mexicana (n.s.) 26(2): 457-463 (2010) BURROW SYSTEMS OF IRANIAN JERBOA (ALLACTAGA FIROUZI WOMOCHEL, 1978) Saeed MOHAMMADI1*, Mohammad KABOLI2, Mahmoud KARAMI2 and Gholamreza NADERI3 1 Department of Environmental Sciences, Sciences & Research Branch, Islamic Azad University, Tehran, IRAN, E-mail: [email protected] 2 Department of Environmental, Faculty of Natural Resources, University of Tehran, Karaj, IRAN, E-mail: [email protected] E-mail: [email protected] 3 Department of Environmental Sciences, Sciences & Research Branch, Islamic Azad University, Tehran, IRAN, E-mail: [email protected] * Corresponding author: Saeed Mohammadi Mohammadi, S., M. Kaboli., M. Karami & Gh. Naderi. 2010. Borrow systems of Iranian jerboa (Allactaga firouzi Womochel, 1978). Acta Zool. Mex. (n.s.), 26(2): 457-463. ABSTRACT. Iranian jerboa was recorded as a new species for Iran near village of Shah-Reza, Isfahan province. It is considered as a data deficient species according to IUCN criteria. Since, No data have been yet reported, on the relationship between architecture of burrows and the social organization of this species, this study aimed to identify the burrow systems of the species. We excavated 15 burrows of Iranian jerboa in the type locality of the species. The burrow system of Iranian jerboa is composed of three types including: temporary, summer and winter burrows. The length of tunnels were significantly different (P=0.00) in winter burrows. General burrow described for Small Five-toed jerboa Allactaga elater was similar with these burrows except having reproduction burrow. Results show that depth of nest chamber in third type of burrow was deeper than in temporary and summer (P=0.00, P=0.003 respectively). -
The Cryptic Case of Otomys Sloggetti (Sloggett's Vlei Rat)
The cryptic case of Otomys sloggetti (Sloggett’s AUTHORS: Thalassa Matthews1 vlei rat): Interpreting murid molar morphology in Turid H. Nel2 the fossil record AFFILIATIONS: 1Centre of Excellence in Palaeosciences, Iziko Museums of South Africa, Cape Town, Vlei rats (Family: Muridae; Subfamily: Otomyinae) have a widespread distribution in southern Africa. They South Africa 2SFF Centre for Early Sapiens are favoured prey of barn and spotted eagle owls, and frequently become associated with archaeological Behaviour (SapienCE), University of deposits when the owls roost in cave sites. The phylogeny of several Otomyinae species is enigmatic, Bergen, Bergen, Norway and Otomys sloggetti (Sloggett’s vlei rat) is no exception. This species has been referred to as the ‘ice rat’ CORRESPONDENCE TO: and present distribution ranges are seemingly limited to mountainous areas, at high altitude, in Lesotho, Thalassa Matthews Drakensberg and the Karoo. It was thus surprising and unexpected when specimens closely resembling Otomys sloggetti (identification was based on molar morphology) were found in several archaeological EMAIL: sites on the south and west coasts of South Africa, and also in modern owl pellet assemblages – all [email protected] extralimital to the current reported distribution. However, further examination of and comparison between DATES: these specimens, as well as extensive differences observed between comparative Otomys sloggetti Received: 10 Sep. 2019 specimens from museum collections, highlighted potential problems associated with the common Revised: 01 June 2020 Accepted: 17 July 2020 practice of using tooth morphology to identify fossil murid species. We identified six molar morphotypes Published: 29 Jan. 2021 from the fossil and modern material, all of which bore a morphological resemblance to O. -
Otomys Auratus – Vlei Rat
Otomys auratus – Vlei Rat Assessment Rationale This near-endemic grassland species is becoming increasingly threatened by grassland contraction and wetland loss, with niche modelling showing that it will undergo a 47–61% reduction in suitable habitat between 1975 and 2050 from climate change (6–8% per decade). Already one major subpopulation, that of the Soutpansberg Mountains, Limpopo Province, has been completely replaced at a key contact zone by the savannah species O. angoniensis over the past 90 years due to thicket habitats replacing grasslands. Ongoing grassland and wetland loss, primarily from agricultural and Ara Monadjem settlement expansion, may synergise with climate change to accelerate area of occupancy (AOO) reduction. Since this species is localised to montane grassland patches, it Regional Red List status (2016) Near Threatened A4c* is more sensitive to habitat loss as it probably cannot National Red List status (2004) Not Evaluated utilise modified habitats. Nationally, there has been 32.8% decline in natural wetlands from 1990–2013/14, which is a Genuine change Reasons for change combination of both genuine wetland loss through Global Red List status Not Evaluated anthropogenic activities and the generally drier conditions currently than in 1990. Specifically, most distribution None TOPS listing (NEMBA) (2007) records (36%) are located in the Mesic Highveld CITES listing None Grassland Bioregion, where there has been a 19% loss of moist grasslands since 1990 (A. Skowno unpubl. data). In Endemic Near KwaZulu-Natal specifically, there was a loss of 7.6% of the *Watch-list Threat natural habitat between 2005 and 2011 (1.3% per annum), which, when extrapolated, equates to a 13% loss of Over the past 90 years (1923 to 2015), O. -
Trophic Ecology of Rusty-Spotted Genet Genetta Maculata and Slender
Trophic ecology of rusty-spotted genet Genetta maculata and slender mongoose Herpestes sanguineus in Telperion Nature Reserve, with a focus on dietary segregation as a possible mechanism of coexistence By Julia Zemouche 595534 A dissertation submitted in fulfilment of the requirements for the degree of MASTER OF SCIENCE (ZOOLOGY) in the School of Animal, Plant and Environmental Sciences at the University of the Witwatersrand 2018 Supervisor: Dr Zimkitha Madikiza Co-supervisors: Prof. Emmanuel Do Linh San (UFH) Dr W. Maartin Strauss (UNISA) Declaration I, Julia Zemouche (595534), hereby declare that this dissertation is my own unaided work. It is being submitted for the Degree of Master of Science at the University of the Witwatersrand, Johannesburg. It has not been submitted before for any degree or examination at any other university. Signature: ________________________________ 29/05/2018 i Acknowledgements First and foremost, I would like to acknowledge my supervisor, Dr Kim Madikiza, and co- supervisors, Prof. Emmanuel Do Linh San and Dr Maartin Strauss. You have provided endless support and guidance throughout this study, for which I am incredibly grateful. Your assistance in the field was always welcome and I learned a great deal from all of you. I would also like to thank the Oppenheimer family for allowing me to conduct my research at Telperion Nature Reserve. Special thanks go out to the various staff at Telperion who always made my visits pleasant and assisted me on many occasions. Ms. Rouxlyn Roux and Ms. Diana Moyo also deserve a special mention for assisting me with fieldwork and providing me with company. -
Chapter 15 the Mammals of Angola
Chapter 15 The Mammals of Angola Pedro Beja, Pedro Vaz Pinto, Luís Veríssimo, Elena Bersacola, Ezequiel Fabiano, Jorge M. Palmeirim, Ara Monadjem, Pedro Monterroso, Magdalena S. Svensson, and Peter John Taylor Abstract Scientific investigations on the mammals of Angola started over 150 years ago, but information remains scarce and scattered, with only one recent published account. Here we provide a synthesis of the mammals of Angola based on a thorough survey of primary and grey literature, as well as recent unpublished records. We present a short history of mammal research, and provide brief information on each species known to occur in the country. Particular attention is given to endemic and near endemic species. We also provide a zoogeographic outline and information on the conservation of Angolan mammals. We found confirmed records for 291 native species, most of which from the orders Rodentia (85), Chiroptera (73), Carnivora (39), and Cetartiodactyla (33). There is a large number of endemic and near endemic species, most of which are rodents or bats. The large diversity of species is favoured by the wide P. Beja (*) CIBIO-InBIO, Centro de Investigação em Biodiversidade e Recursos Genéticos, Universidade do Porto, Vairão, Portugal CEABN-InBio, Centro de Ecologia Aplicada “Professor Baeta Neves”, Instituto Superior de Agronomia, Universidade de Lisboa, Lisboa, Portugal e-mail: [email protected] P. Vaz Pinto Fundação Kissama, Luanda, Angola CIBIO-InBIO, Centro de Investigação em Biodiversidade e Recursos Genéticos, Universidade do Porto, Campus de Vairão, Vairão, Portugal e-mail: [email protected] L. Veríssimo Fundação Kissama, Luanda, Angola e-mail: [email protected] E. -
Ecological Basic Assessment Report
ECOLOGICAL BASIC ASSESSMENT REPORT THE PREVIOUSLY APPROVED KRUISVALLEI HYDROELECTRIC POWER GENERATION SCHEME IN THE ASH RIVER, FREE STATE PROVINCE February 2018 Prepared by: Prepared for: Gerhard Botha (Pri Sci Nat: Ecology & Botany) Savannah Environmental (Pty) Ltd 1st Floor, Block 2, 5 Woodlands Drive Office Park PO Box 12500, Brandhof, 9324 Cnr Woodlands Drive & Western Service Road Cell: 084 207 3454 Woodmead Email: [email protected] KRUISVALLLEI HYDROELECTRIC POWER GENERATION SCHEME, CLARENS ECOLOGICAL BASIC ASSESSMENT REPORT FEBRUARY 2018 TABLE OF CONTENTS Declaration of Consultant’s Independence .................................................... iii 1 Introduction ........................................................................................ 1 1.1 Project Background ........................................................................ 1 1.2 Proposed Activity ........................................................................... 2 1.3 Location ........................................................................................ 3 1.4 Terms of reference ......................................................................... 4 1.5 Conditions of this report ................................................................. 4 1.6 Limitations and Assumptions of the Study Approach ........................... 5 1.2.1. General assumptions ................................................................. 5 1.2.2. Limitations ............................................................................... 5 1.7 Relevant -
Otomys Laminatus – Laminate Vlei Rat
Otomys laminatus – Laminate Vlei Rat Assessment Rationale This endemic species is restricted to moist grasslands and shrublands and occurs in two isolated populations in the Western Cape (Paarl and Cape Town areas) and eastern grasslands of the Drakensberg of KwaZulu-Natal and Photograph Mpumalanga provinces, as well as occasionally occurring in coastal forests. These two populations may represent wanted separate species and should be reassessed following taxonomic resolution. The estimated area of occupancy (AOO), based on remaining natural fynbos and grassland habitat in all occupied grid cells, is 5,293 km2. However, since it relies on moist areas, effective AOO could be as low as 95 km2 based on a 32 m buffer of natural vegetation around remaining wetlands. There has been a 32.8% decline in natural wetlands nationally from 1990– Regional Red List status (2016) Near Threatened 2013/14, which is a combination of both genuine wetland B2ab(i,ii,iii,iv); loss through anthropogenic activities and the generally C1+C2a(i)*† drier conditions currently than in 1990. There is also a National Red List status (2004) Least Concern continuing loss of habitat from agricultural expansion, human settlement sprawl and mining. In KwaZulu-Natal Reasons for change Genuine change: alone, there was a 1.2% loss per annum of natural habitat Habitat decline from 1994 and 2011, which means there has been/will be Global Red List status (2008) Least Concern a 12% loss of habitat over a ten year time period. Climate change is also an emerging threat predicted to TOPS listing (NEMBA) None significantly reduce area of occupancy in the future (P. -
Micromammal Paleoecology
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by CU Scholar Institutional Repository University of Colorado, Boulder CU Scholar Anthropology Graduate Theses & Dissertations Anthropology Spring 1-1-2011 Micromammal Paleoecology: Theory, Methods, and Application to Modern and Fossil Assemblages in The rC adle of Humankind World Heritage Site, South Africa Jennifer Nicole Leichliter University of Colorado at Boulder, [email protected] Follow this and additional works at: http://scholar.colorado.edu/anth_gradetds Part of the Biological and Physical Anthropology Commons Recommended Citation Leichliter, Jennifer Nicole, "Micromammal Paleoecology: Theory, Methods, and Application to Modern and Fossil Assemblages in The Cradle of Humankind World Heritage Site, South Africa" (2011). Anthropology Graduate Theses & Dissertations. Paper 7. This Thesis is brought to you for free and open access by Anthropology at CU Scholar. It has been accepted for inclusion in Anthropology Graduate Theses & Dissertations by an authorized administrator of CU Scholar. For more information, please contact [email protected]. Micromammal Paleoecology: Theory, Methods, and Application to Modern and Fossil Assemblages in The Cradle of Humankind World Heritage Site, South Africa by Jennifer Leichliter B.A., Colorado College, 2008 A thesis submitted to the Faculty of the Graduate School of the University of Colorado in partial fulfillment of the requirement for the degree of Master’s of Anthropology Department of Anthropology 2011 This thesis entitled: Micromammal Paleoecology: Theory, Methods, and Application to Modern and Fossil Assemblages in The Cradle of Humankind World Heritage Site, South Africa written by Jennifer Nicole Leichliter has been approved for the Department Anthropology ________________________________________________ Dr.