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Journal articles on the topic 'South Luangwa National Park'

Author: Grafiati

Published: 9 July 2021

Last updated: 1 February 2022

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1

Williams, N. Leader. "Black rhino in South Luangwa National Park: their distribution and future protection." Oryx 19, no. 1 (January 1985): 27–33. http://dx.doi.org/10.1017/s0030605300019517.

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It became clear in 1979 that commercial poaching was drastically reducing the numbers of rhino in Luangwa Valley and the Zambian Government, through its National Parks and Wildlife Service (NPWS) and the World Wildlife Fund, responded by setting up Save the Rhino Trust (SRT). Neither past nor present numbers and distribution of these animals were sufficiently known to provide a baseline for monitoring the effects of the poaching and the author carried out research on behalf of NPWS and SRT during 1981–82 to assess the status of the rhinos in the Luangwa Valley; FFPS was among the financial supporters of the work. Here he describes the problems that the task presented and the development of a technique that will provide a way of assessing the effectiveness of future anti-poaching operations. The study's findings that 72 per cent of rhinos that die in Luangwa do so from poachers' bullets led to a recommendation for a change in patrol policy; this was adopted by SRT in 1983 and its success is being monitored.

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2

Chabwela, Harry, Chansa Chomba, Gilson Kaweche, and Ackme Mwenya. "Habitat Selection by Large Mammals in South Luangwa National Park, Zambia." Open Journal of Ecology 07, no. 03 (2017): 179–92. http://dx.doi.org/10.4236/oje.2017.73013.

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3

Bercovitch, Fred B., and Philip S. M. Berry. "Giraffe birth locations in the South Luangwa National Park, Zambia: site fidelity or microhabitat selection?" African Journal of Ecology 53, no. 2 (January 22, 2015): 206–13. http://dx.doi.org/10.1111/aje.12209.

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4

Wilkinson, P. J., R. G. Pegram, B. D. Perry, J. Lemche, and H. F. Schels. "The distribution of African swine fever virus isolated from Ornithodoros moubata in Zambia." Epidemiology and Infection 101, no. 3 (December 1988): 547–64. http://dx.doi.org/10.1017/s0950268800029423.

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SUMMARYAfrican swine fever (ASF) has been reported in the Eastern Province of Zambia since 1912 and is now considered to be enzootic there. A survey of the distribution of ASF virus in Zambia was carried out by virus isolation from Ornithodoros moubata ticks collected from animal burrows in National Parks and Game Management Areas in northern, eastern, central and southern Zambia. ASF virus was isolated from ticks in all areas examined. The prevalence of infection in O. moubata was between 0·4% in South Luangwa National Park and 5·1% in Livingstone Game Park and mean infectious virus titres ranged from 103–4 HAD50/tick in Kakumbe Game Management Area to 105·9 HAD50/tick in Chunga and Nalusanga Game Management Areas. The prevalence of infection in adult ticks was between 4·7% and 5·3% in all areas examined except Sumbu National Park and Livingstone Game Park, where the prevalence was 15·1% and 13·2% respectively in adult ticks. The ratio of infected females to males for all the infected adult ticks in all areas of Zambia was 3·2:1.

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5

Chidakel, Alexander, Brian Child, and Shylock Muyengwa. "Evaluating the economics of park-tourism from the ground-up: Leakage, multiplier effects, and the enabling environment at South Luangwa National Park, Zambia." Ecological Economics 182 (April 2021): 106960. http://dx.doi.org/10.1016/j.ecolecon.2021.106960.

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6

Mvula, Cheryl D. "Fair trade in tourism to protected areas- A micro case study of wildlife tourism to South Luangwa National Park, Zambia." International Journal of Tourism Research 3, no. 5 (September 2001): 393–405. http://dx.doi.org/10.1002/jtr.349.

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7

Nakayama, Shouta M. M., Yoshinori Ikenaka, Kaampwe Muzandu, Kennedy Choongo, Ethel M'kandawire, Jun Yasuda, and Mayumi Ishizuka. "Metal and metalloid levels and bio-accumulation characteristics in soil, sediment, land plants and hippopotami (Hippopotamus amphibius L) from the South Luangwa National Park, Zambia." Ecotoxicology and Environmental Safety 80 (June 2012): 333–38. http://dx.doi.org/10.1016/j.ecoenv.2012.04.003.

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8

MZUMARA, TIWONGE I., ROWAN O. MARTIN, HEMANT TRIPATHI, CHAONA PHIRI, and ARJUN AMAR. "Distribution of a habitat specialist: Mopane woodland structure determines occurrence of Near Threatened Lilian’s Lovebird Agapornis lilianae." Bird Conservation International 29, no. 03 (April 29, 2019): 413–22. http://dx.doi.org/10.1017/s0959270918000370.

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SummaryThe near-threatened Lilian’s Lovebird Agapornis lilianae is a small parrot endemic to the Zambezi basin in south-east Africa. The species has a fragmented distribution predominantly within mopane woodlands and is widely referred to as a mopane specialist. The harvesting of mopane trees for charcoal production and timber are having widespread impacts on this woodland habitat, raising concerns over its capacity to support biodiversity. This study aimed to understand the key drivers determining the occurrence of Lilian’s Lovebird in the mopane woodlands of Zambia, focusing particularly on aspects of woodland structure, including the size and density of trees. We used a MaxEnt species distribution model based on historical species occurrence data, to inform selection of 116 survey plots in the Luangwa, Luano and Zambezi valleys. Each plot was sampled for Lilian’s Lovebirds and woodland structure described. Occurrence of Lilian’s Lovebird was found to be positively associated with the size of mopane trees (both height and diameter at breast height) suggesting that large ‘cathedral’ mopane trees provide a key resource for the species and that conservation efforts should focus on the protection of sites containing large trees. No Lilian’s Lovebirds were recorded in areas where they previously occurred to the west of Lower Zambezi National Park, and there was an absence of ‘cathedral’ mopane habitat in this area.

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9

Herrero, Southworth, Bunting, Kohlhaas, and Child. "Integrating Surface-Based Temperature and Vegetation Abundance Estimates into Land Cover Classifications for Conservation Efforts in Savanna Landscapes." Sensors 19, no. 16 (August 7, 2019): 3456. http://dx.doi.org/10.3390/s19163456.

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Southern African savannas are an important dryland ecosystem, as they account for up to 54% of the landscape, support a rich variety of biodiversity, and are areas of key landscape change. This paper aims to address the challenges of studying this highly gradient landscape with a grass–shrub–tree continuum. This study takes place in South Luangwa National Park (SLNP) in eastern Zambia. Discretely classifying land cover in savannas is notoriously difficult because vegetation species and structural groups may be very similar, giving off nearly indistinguishable spectral signatures. A support vector machine classification was tested and it produced an accuracy of only 34.48%. Therefore, we took a novel continuous approach in evaluating this change by coupling in situ data with Landsat-level normalized difference vegetation index data (NDVI, as a proxy for vegetation abundance) and blackbody surface temperature (BBST) data into a rule-based classification for November 2015 (wet season) that was 79.31% accurate. The resultant rule-based classification was used to extract mean Moderate Resolution Imaging Spectroradiometer (MODIS) NDVI values by season over time from 2000 to 2016. This showed a distinct separation between each of the classes consistently over time, with woodland having the highest NDVI, followed by shrubland and then grassland, but an overall decrease in NDVI over time in all three classes. These changes may be due to a combination of precipitation, herbivory, fire, and humans. This study highlights the usefulness of a continuous time-series-based approach, which specifically integrates surface temperature and vegetation abundance-based NDVI data into a study of land cover and vegetation health for savanna landscapes, which will be useful for park managers and conservationists globally.

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10

Smith, P. P. "A reconnaissance survey of the vegetation of the North Luangwa National Park, Zambia." Bothalia 28, no. 2 (October 6, 1998): 197–211. http://dx.doi.org/10.4102/abc.v28i2.641.

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A comprehensive survey of the vegetation of the North Luangwa National Park (NLNP) was carried out over a period of two years. The main aims of the survey were to describe the major vegetation communities in the park and to produce a vegetation map of the NLNP Initial differentiation of vegetation units was established by the appearance of the vegetation on aerial photographs Further information was derived from 353 ground plots in which 20 000 woody plants were identified and measured Thirteen broad vegetation types were recognised in the NLNP Details of their physiognomy, species composition, distribution, topography and edaphic associations are given.

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11

Garoon, Joshua. "The Nature of Success: The Making of Ecological Citizens Around Zambia's North Luangwa National Park." Proceedings of the African Futures Conference 2, no. 1 (June 2018): 154–55. http://dx.doi.org/10.1002/j.2573-508x.2018.tb000020.x.

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12

HOOGEWERF, ANTONIA. "SAFARI THROUGH SOUTH AFRICA - II KRUGER NATIONAL PARK." Science and Culture 86, no. 5-6 (June 7, 2020): 175. http://dx.doi.org/10.36094/sc.v86.2020.safari_south_africa.hoogewerf.175.

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13

Adesalu, Taofikat Abosede. "Freshwater diatoms diversity of national parks in Nigeria I: Okomu national park, South-South, Nigeria." Ife Journal of Science 19, no. 2 (November 14, 2017): 269. http://dx.doi.org/10.4314/ijs.v19i2.7.

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14

Brain, C. K., Il�ma Fouriel, and R. J. Shiel. "Rotifers of the Kalahari Gemsbok National Park, South Africa." Hydrobiologia 313-314, no. 1 (November 1995): 319–24. http://dx.doi.org/10.1007/bf00025964.

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15

Keller, Robert. "Haida Indian Land Claims and South Moresby National Park." American Review of Canadian Studies 20, no. 1 (March 1990): 7–30. http://dx.doi.org/10.1080/02722019009481518.

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16

PERKINS, PHILIP D. "A revision of the Australian humicolous and hygropetric water beetle genus Tympanogaster Perkins, and comparative morphology of the Meropathina (Coleoptera: Hydraenidae)." Zootaxa 1346, no. 1 (October 30, 2006): 1. http://dx.doi.org/10.11646/zootaxa.1346.1.1.

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The Australian endemic humicolous and hygropetric water beetle genus Tympanogaster Perkins, 1979, is revised, based on the study of 7,280 specimens. The genus is redescribed, and redescriptions are provided for T. cornuta (Janssens), T. costata (Deane), T. deanei Perkins, T. macrognatha (Lea), T. novicia (Blackburn), T. obcordata (Deane), T. schizolabra (Deane), and T. subcostata (Deane). Lectotypes are designated for Ochthebius labratus Deane, 1933, and Ochthebius macrognathus Lea, 1926. Ochthebius labratus Deane, 1933, is synonymized with Ochthebius novicius Blackburn, 1896. Three new subgenera are described: Hygrotympanogaster new subgenus (type species Tympanogaster (Hygrotympanogaster) maureenae new species; Topotympanogaster new subgenus (type species Tympanogaster (Topotympanogaster) crista new species; and Plesiotympanogaster new genus (type species Tympanogaster (Plesiotympanogaster) thayerae new species. Seventy-six new species are described, and keys to the subgenera, species groups, and species are given. High resolution digital images of all primary types are presented (online version in color), and geographic distributions are mapped. Male genitalia, representative spermathecae and representative mouthparts are illustrated. Scanning electron micrographs of external morphological characters of adults and larvae are presented. Selected morphological features of the other members of the subtribe Meropathina, Meropathus Enderlein and Tympallopatrum Perkins, are illustrated and compared with those of Tympanogaster. Species of Tympanogaster are typically found in the relict rainforest patches in eastern Australia. Most species have very limited distributions, and relict rainforest patches often have more than one endemic species. The only species currently known from the arid center of Australia, T. novicia, has the widest distribution pattern, ranging into eastern rainforest patches. There is a fairly close correspondence between subgenera and microhabitat preferences. Members of Tympanogaster (s. str.) live in the splash zone, usually on stream boulders, or on bedrock stream margins. The majority of T. (Hygrotympanogaster) species live in the hygropetric zone at the margins of waterfalls, or on steep rockfaces where water is continually trickling; a few rare species have been collected from moss in Nothofagus rainforests. Species of T. (Plesiotympanogaster) have been found in both hygropetric microhabitats and in streamside moss. The exact microhabitats of T. (Topotympanogaster) are unknown, but the morphology of most species suggests non-aquatic habits; most specimens have been collected in humicolous microhabitats, by sifting rainforest debris, or were taken in flight intercept traps. Larvae of hygropetric species are often collected with adults. These larvae have tube-like, dorsally positioned, mesothoracic spiracles that allow the larvae to breathe while under a thin film of water. The key morphological differences between larvae of Tympanogaster (s. str.) and those of Tympanogaster (Hygrotympanogaster) are illustrated. New species of Tympanogaster are: T. (s. str.) aldinga (New South Wales, Dorrigo National Park, Rosewood Creek), T. (s. str.) amaroo (New South Wales, Back Creek, downstream of Moffatt Falls), T. (s. str.) ambigua (Queensland, Cairns), T. (Hygrotympanogaster) arcuata (New South Wales, Kara Creek, 13 km NEbyE of Jindabyne), T. (Hygrotympanogaster) atroargenta (Victoria, Possum Hollow falls, West branch Tarwin River, 5.6 km SSW Allambee), T. (Hygrotympanogaster) barronensis (Queensland, Barron Falls, Kuranda), T. (s. str.) bluensis (New South Wales, Blue Mountains), T. (Hygrotympanogaster) bondi (New South Wales, Bondi Heights), T. (Hygrotympanogaster) bryosa (New South Wales, New England National Park), T. (Hygrotympanogaster) buffalo (Victoria, Mount Buffalo National Park), T. (Hygrotympanogaster) canobolas (New South Wales, Mount Canobolas Park), T. (s. str.) cardwellensis (Queensland, Cardwell Range, Goddard Creek), T. (Hygrotympanogaster) cascadensis (New South Wales, Cascades Campsite, on Tuross River), T. (Hygrotympanogaster) clandestina (Victoria, Grampians National Park, Golton Gorge, 7.0 km W Dadswells Bridge), T. (Hygrotympanogaster) clypeata (Victoria, Grampians National Park, Golton Gorge, 7.0 km W Dadswells Bridge), T. (s. str.) cooloogatta (New South Wales, New England National Park, Five Day Creek), T. (Hygrotympanogaster) coopacambra (Victoria, Beehive Falls, ~2 km E of Cann Valley Highway on 'WB Line'), T. (Topotympanogaster) crista (Queensland, Mount Cleveland summit), T. (Hygrotympanogaster) cudgee (New South Wales, New England National Park, 0.8 km S of Pk. Gate), T. (s. str.) cunninghamensis (Queensland, Main Range National Park, Cunningham's Gap, Gap Creek), T. (s. str.) darlingtoni (New South Wales, Barrington Tops), T. (Hygrotympanogaster) decepta (Victoria, Mount Buffalo National Park), T. (s. str.) dingabledinga (New South Wales, Dorrigo National Park, Rosewood Creek, upstream from Coachwood Falls), T. (s. str.) dorrigoensis (New South Wales, Dorrigo National Park, Rosewood Creek, upstream from Coachwood Falls), T. (Topotympanogaster) dorsa (Queensland, Windin Falls, NW Mount Bartle-Frere), T. (Hygrotympanogaster) duobifida (Victoria, 0.25 km E Binns, Hill Junction, adjacent to Jeeralang West Road, 4.0 km S Jeerelang), T. (s. str.) eungella (Queensland, Finch Hatton Gorge), T. (Topotympanogaster) finniganensis (Queensland, Mount Finnigan summit), T. (s. str.) foveova (New South Wales, Border Ranges National Park, Brindle Creek), T. (Hygrotympanogaster) grampians (Victoria, Grampians National Park, Epacris Falls, 2.5 km WNW Halls Gap), T. (Hygrotympanogaster) gushi (New South Wales, Mount Canobolas Park), T. (s. str.) hypipamee (Queensland, Mount Hypipamee National Park, Barron River headwaters below Dinner Falls), T. (s. str.) illawarra (New South Wales, Macquarie Rivulet Falls, near Wollongong), T. (Topotympanogaster) intricata (Queensland, Mossman Bluff Track, 5–10 km W Mossman), T. (s. str.) jaechi (Queensland, Running Creek, along road between Mount Chinghee National Park and Border Ranges National Park), T. (Topotympanogaster) juga (Queensland, Mount Lewis summit), T. kuranda (Queensland, Barron Falls, Kuranda), T. (s. str.) lamingtonensis (Queensland, Lamington National Park, Lightening Creek), T. (s. str.) magarra (New South Wales, Border Ranges National Park, Brindle Creek), T. (Hygrotympanogaster) maureenae (New South Wales, Back Creek, Moffatt Falls, ca. 5 km W New England National Park boundary), T. (Hygrotympanogaster) megamorpha (Victoria, Possum Hollow falls, W br. Tarwin River, 5.6 km SSW Allambee), T. (Hygrotympanogaster) merrijig (Victoria, Merrijig), T. (s. str.) millaamillaa (Queensland, Millaa Millaa), T. modulatrix (Victoria, Talbot Creek at Thomson Valley Road, 4.25 km WSW Beardmore), T. (Topotympanogaster) monteithi (Queensland, Mount Bartle Frere), T. moondarra (New South Wales, Border Ranges National Park, Brindle Creek), T. (s. str.) mysteriosa (Queensland), T. (Hygrotympanogaster) nargun (Victoria, Deadcock Den, on Den of Nargun Creek, Mitchell River National Park), T. (Hygrotympanogaster) newtoni (Victoria, Mount Buffalo National Park), T. (s. str.) ovipennis (New South Wales, Dorrigo National Park, Rosewood Creek, upstream from Coachwood Falls), T. (s. str.) pagetae (New South Wales, Back Creek, downstream of Moffatt Falls), T. (Topotympanogaster) parallela (Queensland, Mossman Bluff Track, 5–10 km W Mossman), T. (s. str.) perpendicula (Queensland, Mossman Bluff Track, 5–10 km W Mossman), T. plana (Queensland, Cape Tribulation), T. (Hygrotympanogaster) porchi (Victoria, Tarra-Bulga National Park, Tarra Valley Road, 1.5 km SE Tarra Falls), T. (s. str.) precariosa (New South Wales, Leycester Creek, 4 km. S of Border Ranges National Park), T. (s. str.) protecta (New South Wales, Leycester Creek, 4 km. S of Border Ranges National Park), T. (Hygrotympanogaster) punctata (Victoria, Mount Buffalo National Park, Eurobin Creek), T. (s. str.) ravenshoensis (Queensland, Ravenshoe State Forest, Charmillan Creek, 12 km SE Ravenshoe), T. (s. str.) robinae (New South Wales, Back Creek, downstream of Moffatt Falls), T. (s. str.) serrata (Queensland, Natural Bridge National Park, Cave Creek), T. (Hygrotympanogaster) spicerensis (Queensland, Spicer’s Peak summit), T. (Hygrotympanogaster) storeyi (Queensland, Windsor Tableland), T. (Topotympanogaster) summa (Queensland, Mount Elliott summit), T. (Hygrotympanogaster) tabula (New South Wales, Mount Canobolas Park), T. (Hygrotympanogaster) tallawarra (New South Wales, Dorrigo National Park, Rosewood Creek, Cedar Falls), T. (s. str.) tenax (New South Wales, Salisbury), T. (Plesiotympanogaster) thayerae (Tasmania, Liffey Forest Reserve at Liffey River), T. (s. str.) tora (Queensland, Palmerston National Park), T. trilineata (New South Wales, Sydney), T. (Hygrotympanogaster) truncata (Queensland, Tambourine Mountain), T. (s. str.) volata (Queensland, Palmerston National Park, Learmouth Creek, ca. 14 km SE Millaa Millaa), T. (Hygrotympanogaster) wahroonga (New South Wales, Wahroonga), T. (s. str.) wattsi (New South Wales, Blicks River near Dundurrabin), T. (s. str.) weiri (New South Wales, Allyn River, Chichester State Forest), T. (s. str.) wooloomgabba (New South Wales, New England National Park, Five Day Creek).

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17

Getman, V. "NATIONAL NATURE PARK “DZHARYLGATSKYI”." Bulletin of Taras Shevchenko National University of Kyiv. Geography, no. 70-71 (2018): 50–53. http://dx.doi.org/10.17721/1728-2721.2018.70.8.

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National Natural Park (NPP) “Dzharylgatskyi” was established by Decree of the President of Ukraine from December 11, 2009, on the territory of Skadovsky district of Kherson region. This was preceded by the creation of Dzharylgatskyi botanical reserve of national importance in 1974. According to the physical-geographical zoning of Ukraine, the territory of the NPP “Dzharylgatskyi” refers to the Nizhnedneprovsky terraced-delta landscape of the Black Sea-Pryazovsky dry-steppe region. The main territorial area of the National Park “Dzharylgatskyi” is the Dzharylgach island with a narrow spit in its western part. The geomorphologic location of the park belongs to the region of the coastal zone of the Nizhnedneprovsk oblast plain, which includes the Oleshkivski Sands and the Kinburn Spit. Island surroundings represent the psamophytic steppe and it is one of the great features of the nature reserve in the south of Ukraine. Island isolation – the remoteness from the settlements of the mainland – is the greatest natural value of Dzharylgach. This is the largest uninhabited island in Europe. Flora of the NPP “Dzharylgatskyi” includes about 500 species of higher plants. The uniqueness of the Dzharylgatsky natural complex, the mild climatic conditions in the winter and the location along the Azov-Black Sea migration corridor have created some favourable conditions for the abundance of a significant number of birds species in different seasons of the year. Dzharylhach Island is an important link between the coastal environmental corridor. It is a place for birds to rest and nest during seasonal migrations. The territory of the national park is the part of one of the largest wetlands of international importance – “Karkinitskaya and Dzharilgatska Gulfs”. NPP “Dzharylgatsky” belongs to the Skadovsk resort zone with its warm sea, sandy beaches, long swimming season, which characterizes the park as a unique area for recreation and tourism. Discovered on Dzharylgach put peloids in their characteristics meet the highest requirements for therapeutic mud. This article analyzes the features of the natural environment and resources of the National Park “Dzharylgatskyi.” Attention is drawn to the geomorphological features of island spit. The article also raises the question of developing nature reserve agencies, such as the natural laboratory (bank) to conserve rare animals and plants.

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18

Hoffman, George. "Vegetation Distribution in Badlands National Park." UW National Parks Service Research Station Annual Reports 12 (January 1, 1988): 7–11. http://dx.doi.org/10.13001/uwnpsrc.1988.2685.

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This study concerns the vegetation distribution in habitat types of Badlands National Park, South Dakota. Phase I of the study is that of reconnaissance and determining potential habitat types present. Phase II includes intensive sampling of sites which represent minimally disturbed vegetation. Sites on more disturbed vegetation also will be established. Phase III will include mapping of habitat types and additional sampling to fully substantiate results of Phase II. Study sites established in the Park should be thought of as long-term monitoring sites at which effects of animal grazing, climate changes and fire can affect the vegetation.

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19

Wojewoda, Władysław. "Macromycetes of the Ojców National Park. I." Acta Mycologica 10, no. 2 (November 21, 2014): 181–265. http://dx.doi.org/10.5586/am.1974.007.

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A floristic-ecological manograph of the macromycetes of the Ojców National Park (South Poland, Cracow-Wieluń Upland - Cracow Jurassic Region) is made. In this first part regional features of the investigated area and a list of 715 macromycetes are given. Some species are new to Poland, and 273 species are new to Cracow-Wieluń Upland.

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20

James, I., T. Hoffman, A. Munro, P. O'Farell, and R. Smart. "The economic value of flower tourism at the Namaqua National Park, South Africa." South African Journal of Economic and Management Sciences 10, no. 4 (May 22, 2014): 442–56. http://dx.doi.org/10.4102/sajems.v10i4.1058.

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The travel cost method was used to estimate the economic recreational value of flower viewing at the Namaqua National Park. Demographic, time, expenditure, preference and route information was collected from interviews with 160 SA nationals who visited the park in their own car. Visitors spent an average of $US108 on transportation and $US84 on accommodation in the region. A zonal travel cost model was developed which suggests that the economic recreational value of flower viewing at the park makes to the region is far larger than the annual net loss of $US50 000 which the park makes when only the expenses and revenue of the park are considered.

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21

Ellis, Murray, and Klaus Henle. "The mammals of Kinchega National Park western New South Wales." Australian Zoologist 25, no. 1 (December 1988): 1–6. http://dx.doi.org/10.7882/az.1988.005.

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22

Sandoval-Denis, Marcelo, Wijnand J. Swart, and Pedro W. Crous. "New Fusarium species from the Kruger National Park, South Africa." MycoKeys 34 (June 1, 2018): 63–92. http://dx.doi.org/10.3897/mycokeys.34.25974.

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Three new Fusarium species, F.convolutans, F.fredkrugeri, and F.transvaalense (Ascomycota, Hypocreales, Nectriaceae) are described from soils collected in a catena landscape on a research supersite in the Kruger National Park, South Africa. The new taxa, isolated from the rhizosphere of three African herbaceous plants, Kyphocarpaangustifolia, Melhaniaacuminata, and Sidacordifolia, are described and illustrated by means of morphological and multilocus molecular analyses based on sequences from five DNA loci (CAL, EF-1 α, RPB1, RPB2 and TUB). According to phylogenetic inference based on Maximum-likelihood and Bayesian approaches, the newly discovered species are distributed in the Fusariumbuharicum, F.fujikuroi, and F.sambucinum species complexes.

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23

Durrheim, David N., Leo Braack, Douw Grobler, Helena Bryden, Rick Speare, and Peter A. Leggat. "Safety of Travel in South Africa: The Kruger National Park." Journal of Travel Medicine 8, no. 4 (March 8, 2006): 176–91. http://dx.doi.org/10.2310/7060.2001.24239.

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24

Pooley, Simon. "National Park Science: a Century of Research in South Africa." African Journal of Range & Forage Science 35, no. 2 (June 29, 2018): 148–50. http://dx.doi.org/10.2989/10220119.2018.1494042.

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25

Baard, J. A., and T. Kraaij. "Alien flora of the Garden Route National Park, South Africa." South African Journal of Botany 94 (September 2014): 51–63. http://dx.doi.org/10.1016/j.sajb.2014.05.010.

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26

Worster, Donald. "National Park Science: A century of research in South Africa." Transactions of the Royal Society of South Africa 73, no. 2 (March 22, 2018): 207–8. http://dx.doi.org/10.1080/0035919x.2018.1449769.

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27

Lindenmayer, David B., Christopher MacGregor, Darren Brown, Rebecca Montague-Drake, Mason Crane, Damian Michael, and Bruce D. Lindenmayer. "Aves, Booderee National Park, Jervis Bay territory, south-eastern Australia." Check List 5, no. 3 (August 1, 2009): 479. http://dx.doi.org/10.15560/5.3.449.

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A large-scale, long-term study is being conducted to describe the bird assemblages inhabiting a 6500 ha area at Booderee National Park, south-eastern Australia. In this paper, we provide a list of birds recorded within rainforest, forest, woodland, shrubland, heathland and sedgeland during surveys conducted each spring between 2003 and 2007. Of particular interest was the contrast between the birds of sites burned in a wildfire in 2003 and sites that remained unburned. We recorded a total of 103 species from 35 families. We found that after the major fire, the vast majority of individual species and the bird assemblage per se in most vegetation types recovered within two years. Exceptions occurred in structurally simple vegetation types such as sedgeland and wet heathland in which reduced levels of species had not returned to pre-fire (2003) levels by 2007.

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Rubin, F., A. R. Palmer, and C. Tyson. "Patterns of endemism within the Karoo National Park, South Africa." Bothalia 31, no. 1 (September 17, 2001): 117–33. http://dx.doi.org/10.4102/abc.v31i1.510.

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A checklist of 864 plant taxa representing 355 genera and 93 families is given for the Karoo National Park. A total of 121 species are endemic to the Nama-Karoo, with Asteraceae the most common with 33 taxa. followed by Mesembryanthemaceae with 26 taxa. Phytochorological affinities indicate that 19.8% of the species are from the Nama- Karoo Biome only, another 19.8% are distributed over two biomes, and 41% of the species have a widespread distribution. The Karoo National Park conserves 30% of the recognized endemics of the Nama-Karoo Biome.

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Sánchez Piñero, F., R. L. Aalbu, and J. M. Herrera-Vega. "Tenebrionidae (Coleoptera) of the Khnifiss Lagoon National Park, South Morocco." African Entomology 17, no. 1 (March 2009): 106–9. http://dx.doi.org/10.4001/003.017.0112.

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PUSPITANINGTYAS, DWI MURTI. "Orchid inventory in Bantimurung-Bulusaraung National Park, South Sulawesi, Indonesia." Biodiversitas, Journal of Biological Diversity 18, no. 1 (February 1, 2017): 341–50. http://dx.doi.org/10.13057/biodiv/d180145.

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31

Yessoufou, Kowiyou. "Potential carbon stock in the Kruger National Park, South Africa." Botany Letters 164, no. 4 (October 2, 2017): 425–32. http://dx.doi.org/10.1080/23818107.2017.1383306.

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32

Mustoe, Simon H., David R. Capper, James C. Lowen, Jonathan D. Leadley, and Domoina Rakotomalala. "Zombitse-Vohibasia: a new national park in south-west Madagascar." Bulletin of the African Bird Club 5, no. 1 (March 1998): 39–45. http://dx.doi.org/10.5962/p.309543.

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33

National Park Service Research Center, University of Wyoming. "National Park Service Areas Cooperating with U.W.-N.P.S." UW National Parks Service Research Station Annual Reports 9 (January 1, 1985): 234–39. http://dx.doi.org/10.13001/uwnpsrc.1985.2531.

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34

Jha, Parveen Kumar. "Common Birds of Chitwan National Park, Nepal." Journal of Advanced Academic Research 1, no. 2 (February 11, 2017): 19–26. http://dx.doi.org/10.3126/jaar.v1i2.16585.

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This research paper gives checklist of common birds of Chitwan National Park, which is a wild-life protected area in south-central Nepal. It covers tropical and sub-tropical vegetation. It is first protected area and includes 932 sq. km. Common birds observed are about 170 belonging to 48 Avian families during 2013-2014. Present investigator has very minutely observed birds in habitat conditions. Bird species were recognized by very high binocular. Birds were thoroughly studied from point of view of Taxonomy. Machans were also erected for observing birds.

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35

Butler, Jack. "Exotic Plants of Theodore Roosevelt National Park." UW National Parks Service Research Station Annual Reports 16 (January 1, 1992): 175–76. http://dx.doi.org/10.13001/uwnpsrc.1992.3109.

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The 1992 field season began in early May with a meeting between the principal investigator and NPS Unit Technical Representatives. The primary objectives of the second field season was to 1) continue with the initial survey so that the number and distribution of exotic plant species within the Park could be estimated, 2) take low-level aerial photographs (slides) of the South Unit so that general areas of leafy spurge infestations could be mapped, 3) continue to evaluate the existing ecological effects of exotics on the native constituents, and 4) estimate density and composition of exotics within the soil seed bank.

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36

Harper, Kimball, Stewart Sanderson, and E. McArthur. "Vegetation Communities of Zion National Park." UW National Parks Service Research Station Annual Reports 11 (January 1, 1987): 191–96. http://dx.doi.org/10.13001/uwnpsrc.1987.2673.

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The overall objectives of this study are to 1) provide a map of the current vegetation of Zion National Park (ZNP), 2) provide a listing of all vascular plants known for the Park, 3) list all rare, endangered and exotic plant species growing within the Park and describe the distribution and habitat preferences of each as fully as possible, 4) list representative locations for examples of undisturbed stands of each of the major vegetational types, and 5) present our basic field data to the Park on computer disks with software programs that will permit employees to access data files easily and systematically. These objectives are being satisfied through systematic sampling of the vegetation at 1. 6 km intervals. Ideally, the samples should be taken at all section corners using cadastral survey maps, but some remote portions of the park have never been surveyed. As a consequence, we have established a master grid system overlaying the entire Park. Where survey lines do exist our grid system is completely congruent with them. For ease of identifying grid intersection points for data retrieval, we have assigned alphabetical letters to the north-south lines and arabic numbers to the east-west lines. A master map is on file at ZNP headquarters at Springdale, Utah.

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Ray, Rena-Rebecca, C. Stommel, and Dennis Rödder. "Home ranges, activity patterns and habitat preferences of leopards in Luambe National Park and adjacent hunting area in the Luangwa Valley, Zambia." Mammalian Biology 81 (September 2016): 14. http://dx.doi.org/10.1016/j.mambio.2016.07.041.

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38

Wakka, Abd Kadir, Nurhaedah Muin, and Rini Purwanti. "TOWARD COLLABORATIVE MANAGEMENT OF BANTIMURUNG BULUSARAUNG NATIONAL PARK, SOUTH SULAWESI PROVINCE." Jurnal Penelitian Kehutanan Wallacea 4, no. 1 (April 30, 2015): 41. http://dx.doi.org/10.18330/jwallacea.2015.vol4iss1pp41-50.

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Attwood, C. G., J. Allen, and P. J. Claassen. "Nearshore surface current patterns in the Tsitsikamma National Park, South Africa." South African Journal of Marine Science 24, no. 1 (June 2002): 151–60. http://dx.doi.org/10.2989/025776102784528448.

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Steyn, H. M., S. P. Bester, and H. Bezuidenhout. "An updated plant checklist for Tankwa Karoo National Park, South Africa." South African Journal of Botany 88 (September 2013): 247–51. http://dx.doi.org/10.1016/j.sajb.2013.07.018.

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Knight, M. H., M. Kshatriya, A. S. Van Jaarsveld, A. O. Nicholls, and A. J. Hall-Martin. "Evaluating herbivore extinction probabilities in Addo Elephant National Park, South Africa." African Zoology 36, no. 1 (April 2001): 13–22. http://dx.doi.org/10.1080/15627020.2001.11657109.

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42

侯, 邦飞. "The Idea of Establishing a National Park in South Hubei Province." Sustainable Development 07, no. 02 (2017): 71–76. http://dx.doi.org/10.12677/sd.2017.72009.

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43

Taru, Phillip, Wisemen Chingombe, and Geoffrey Mukwada. "South Africa’s Golden Gate Highlands National Park management plan: Critical reflections." South African Journal of Science 109, no. 11/12 (2013): 1–3. http://dx.doi.org/10.1590/sajs.2013/a0039.

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44

Pienaar, D. J., J. du P. Bothma, and G. K. Theron. "White rhinoceros range size in the south-western Kruger National Park." Journal of Zoology 229, no. 4 (April 1993): 641–49. http://dx.doi.org/10.1111/j.1469-7998.1993.tb02661.x.

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45

Safari, Chrispine, and Dominic Byarugaba. "Control ofLantana camaraL. in Bwindi Impenetrable National Park, south-western Uganda." African Journal of Ecology 46, no. 3 (September 2008): 456–58. http://dx.doi.org/10.1111/j.1365-2028.2007.00878.x.

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46

Ivancic, Paul C., and Chun-Yi Sun. "Hippopotamuses at Dawn in Lake Panic, Kruger National Park, South Africa." Spine 34, no. 21 (October 2009): i. http://dx.doi.org/10.1097/01.brs.0000361527.68069.94.

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47

Mphepya, J. N., C. Galy-Lacaux, J. P. Lacaux, G. Held, and J. J. Pienaar. "Precipitation Chemistry and Wet Deposition in Kruger National Park, South Africa." Journal of Atmospheric Chemistry 53, no. 2 (February 2006): 169–83. http://dx.doi.org/10.1007/s10874-005-9005-7.

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48

Boonzaier, Emile. "Local responses to conservation in the Richtersveld National Park, South Africa." Biodiversity and Conservation 5, no. 3 (March 1996): 307–14. http://dx.doi.org/10.1007/bf00051776.

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49

Vadala, Carin E., Robert D. Bixler, and William E. Hammitt. "A Public's Awareness of Regional Parks and Park Management Agencies with Implications for Management-oriented Interpretation." Journal of Interpretation Research 11, no. 2 (November 2006): 59–64. http://dx.doi.org/10.1177/109258720601100207.

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South Florida summer residents (n=1806) from five counties (Broward, Collier, Lee, Miami-Dade, and Monroe Counties) were asked to recall the names of two units of the National Park Service and, when prompted, to recognize each of the four national park units located in south Florida. Only 8.4% of respondents could name two units of the National Park Service, yet when prompted many more stated that they had at least heard of the national parks in south Florida. Interpreters may be able to help raise visitor awareness of resource management issues by including information about the role of the agency in their talks or as part of their interpretive theme. Suggestions for further research and evaluation strategies are provided.

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50

Shaw, Scott. "Studies of Parasitic Wasps (Braconidae) In Grand Teton National Park." UW National Parks Service Research Station Annual Reports 26 (January 1, 2002): 47–59. http://dx.doi.org/10.13001/uwnpsrc.2002.3505.

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A survey of braconid wasps in GTNP and south YNP recognizes 71 genera and at least 150 species. Of these, 100 are new distribution records and at least nine are new (undescribed) species. The species richness of Braconidae in GYE (150 species) is substantially greater than the maximum species richness of all herbaceous plants, shrubs, trees, birds and mammals in lodgepole pine communities of YNP (112 species). This total also substantially exceeds the number of braconid species recorded in fireÂdisturbed habitats of south YNP (109 species).

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