Literatura científica selecionada sobre o tema "Blue Mountains National Park"

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Artigos de revistas sobre o assunto "Blue Mountains National Park"

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Armstrong, E. Kate, e Christine L. Kern. "Demarketing manages visitor demand in the Blue Mountains National Park". Journal of Ecotourism 10, n.º 1 (março de 2011): 21–37. http://dx.doi.org/10.1080/14724040903427393.

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Vilcins, I., M. Krockenberger, H. Agus e D. Carter. "Environmental sampling forCryptococcus neoformansvar.gattiifrom the Blue Mountains National Park, Sydney, Australia". Medical Mycology 40, n.º 1 (janeiro de 2002): 53–60. http://dx.doi.org/10.1080/mmy.40.1.53.60.

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Vilcins, I., M. Krockenberger, H. Agus e D. Carter. "Environmental sampling for Cryptococcus neoformans var. gattii from the Blue Mountains National Park, Sydney, Australia". Medical Mycology 40, n.º 1 (1 de fevereiro de 2002): 53–60. http://dx.doi.org/10.1080/714031079.

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Plummer, L. N., E. Busenberg, J. K. Böhlke, D. L. Nelms, R. L. Michel e P. Schlosser. "Groundwater residence times in Shenandoah National Park, Blue Ridge Mountains, Virginia, USA: a multi-tracer approach". Chemical Geology 179, n.º 1-4 (setembro de 2001): 93–111. http://dx.doi.org/10.1016/s0009-2541(01)00317-5.

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Otuokon, Susan, Shauna-Lee Chai e Marlon Beale. "Using tourism to conserve the mist forests and mysterious cultural heritage of the Blue and John Crow Mountains National Park, Jamaica". PARKS 18, n.º 2 (outubro de 2012): 145–54. http://dx.doi.org/10.2305/iucn.ch.2012.parks-18-2.so.en.

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Fryirs, Kirstie A., Kirsten L. Cowley, Natalie Hejl, Anthony Chariton, Nicole Christiansen, Rachael Y. Dudaniec, Will Farebrother et al. "Extent and effect of the 2019-20 Australian bushfires on upland peat swamps in the Blue Mountains, NSW". International Journal of Wildland Fire 30, n.º 4 (2021): 294. http://dx.doi.org/10.1071/wf20081.

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The devastating bushfires of the 2019–20 summer are arguably the most costly natural disaster in Australian recorded history. What is little known is that these fires severely affected the temperate highland peat swamps on sandstone (THPSS), a form of upland wetland that occurs in the water supply catchments of Sydney in the Greater Blue Mountains World Heritage Area and National Park. During the fires, 59% of THPSS was burnt and 72% of those by a high severity burn. Upland swamps at Newnes were the most affected, with 96% of swamps burnt and 84% of these experiencing a very high burn severity. We present an analysis of the spatial extent and severity of the bushfire on the THPSS and discuss some of the likely consequences on their geomorphological, hydrological and ecological structure, function and recovery potential.
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Quintas, Victor, Daniela M. Takiya, Isabele Côrte e Gabriel Mejdalani. "A remarkable new species of Cavichiana (Hemiptera: Cicadellidae: Cicadellinae) from southeastern Brazil". Zoologia 37 (13 de janeiro de 2020): 1–8. http://dx.doi.org/10.3897/zoologia.37.e38783.

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CavichianaMejdalani et al., 2014 was a formerly monotypic Cicadellinae genus exclusively found in bromeliads from southeastern Brazil. Here a new species is described, diagnosed, and illustrated from Itatiaia National Park, municipality of Itamonte, state of Minas Gerais (Mantiqueira mountain range); specimens were collected on Vriesea spp. (Bromeliaceae). Cavichiana alpina sp. nov. (male holotype in DZRJ) can be recognized by the following combination of features: (1) forewing clavus with basal portion and area along commissural margin orange, remainder of claval area blue (except dark brown apex); (2) corium with large blue area adjacent to claval sulcus, connected to blue area of clavus; (3) distal portion of female and male pygofer not sclerotized; (4) aedeagus with distinct basidorsal lobe and with apex narrowly rounded, not bearing crown of spines; and (5) female sternite VII with deep V-shaped posterior emargination. Notes on the distribution of the genus are provided and C. bromelicolaMejdalani et al., 2014 is newly recorded from southern Brazil.
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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, n.º 1 (30 de outubro de 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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Leki, Phuntsho Thinley, Rajanathan Rajaratnam e Rinjan Shrestha. "Establishing baseline estimates of blue sheep (Pseudois nayaur) abundance and density to sustain populations of the vulnerable snow leopard (Panthera uncia) in Western Bhutan". Wildlife Research 45, n.º 1 (2018): 38. http://dx.doi.org/10.1071/wr16218.

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Context Advances have been made in the development of reliable methods for estimating the abundance and density of large threatened mammalian predators, but there is little progress on developing population estimates for their principal prey. No standardised protocol for estimating prey populations exists, therefore different researchers use different methods. As such, there is little information on key prey species of the vulnerable snow leopard and this has hindered the preparation of effective snow leopard conservation plans. Aims This study aimed to establish an estimated seasonal baseline population abundance and density of blue sheep in the Lingzhi Park Range (LPR) of Bhutan’s Jigme Dorji National Park over winter (December to February) and summer (May to July). It also aimed to assess the number of snow leopard individuals that the current blue sheep population can sustain in the study area. Methods A refined double-observer survey method was used and involved walking transect lengths of 414 km in winter and 450 km in summer to estimate blue sheep abundance with the aid of 8 × 30 binoculars and 15 × 45 spotting scopes. Key results In total, 1762 (s.e. ± 199) blue sheep individuals were recorded in winter at a density of 8.51 individuals per km2 and 2097 (s.e. ± 172) individuals in summer at a density of 9.32 individuals per km2. Mean group size of blue sheep was 38.12 individuals (s.e. ± 6) in winter and 52.36 individuals (s.e. ± 4) in summer. LPR was estimated to sustain 11–17 snow leopards in winter and 15–21 in summer. Key conclusions LPR can be a hotspot for snow leopard conservation in western Bhutan and regionally in the eastern Himalayas, because the comparatively higher estimated blue sheep abundance and density supports possibly the highest density of snow leopards in Bhutan. The modified double-observer method used to assess blue sheep population estimates is inexpensive, robust and practical for the mountainous terrain of the Himalayas. Implications On the basis of this study, it is recommended that a refined double-observer method is adopted as a standard technique for estimating blue sheep populations in the snow leopard range countries of the Himalayas. Snow leopard conservation plans should, additionally, include efforts to minimise threats to blue sheep populations. This refined method is also highly applicable for future surveys of gregarious mammalian taxa, such as ungulates and primates, in difficult mountainous terrain elsewhere in the world.
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Broome, Linda S. "Density, home range, seasonal movements and habitat use of the mountain pygmy-possum Burramys parvus (Marsupialia: Burramyidae) at Mount Blue Cow, Kosciuszko National Park". Austral Ecology 26, n.º 3 (junho de 2001): 275–92. http://dx.doi.org/10.1046/j.1442-9993.2001.01114.x.

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Teses / dissertações sobre o assunto "Blue Mountains National Park"

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Kelleher, Matthew. "Archaeology of sacred space : the spatial nature of religious behaviour in the Blue Mountains National Park Australia". University of Sydney, 2002. http://hdl.handle.net/2123/4138.

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Doctor of Philosophy
This thesis examines the material correlates of religious behaviour. Religion is an important part of every culture, but the impact religion has on structuring material culture is not well understood. Archaeologists are hampered in their reconstructions of the past because they lack comparative methods and universal conventions for identifying religious behaviour. The principal aim of this thesis is to construct an indicator model which can archaeologically identify religious behaviour. The basis for the proposed model stems directly from recurrent religious phenomena. Such phenomena, according to anthropological and cognitive research, relate to a series of spatio-temporally recurrent religious features which relate to a universal foundation for religious concepts. Patterns in material culture which strongly correlate with these recurrent phenomena indicate likely concentrations of religious behaviour. The variations between sacred and mundane places can be expected to yield information regarding the way people organise themselves in relation to how they perceive their cosmos. Using cognitive religious theory, stemming from research in neurophysiology and psychology, it is argued that recurrent religious phenomena owe their replication to the fact that certain physical stimuli and spatial concepts are most easily interpreted by humans in religious ideas. Humans live in a world governed by natural law, and it is logical that the concepts generated by humans will at least partially be similarly governed. Understanding the connection between concept and cause results in a model of behaviour applicable to cross-cultural analysis and strengthens the model’s assumption base. In order to test the model of religious behaviour developed in this thesis it is applied to a regional archaeological matrix from the Blue Mountains National Park in New South Wales, Australia. Archaeological research in the Blue Mountains has tentatively identified ceremonial sites based on untested generalised associations between select artefact types and distinctive geographic features. The method of analysis in this thesis creates a holistic matrix of archaeological and geographic data, encompassing both qualitative and quantitative measures, which generates a statistical norm for the region. Significant liminal deviations from this norm, which are characteristic indicators of religious behaviour are then identified. Confidence in these indicators’ ability to identify ceremonial sites is obtained by using a distance matrix and algorithms to examine the spatial patterns of association between significant variables. This thesis systematically tests the associations between objects and geography and finds that a selective array and formulaic spatiality of material correlates characteristic of religious behaviour does exist at special places within the Blue Mountains. The findings indicate a wide spread if more pocketed distribution of ceremonial sites than is suggested in previous models. The spatial/material relationships for identified religious sites indicates that these places represent specialised extensions of an interdependent socio-economic system where ceremonial activity and subsistence activity operated in balance and were not isolated entities.
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Cohen, Daniel, University of Western Sydney, of Science Technology and Environment College e School of Engineering and Industrial Design. "Best practice mine water management at a coal mining operation in the Blue Mountains". THESIS_CSTE_EID_Cohen_D.xml, 2002. http://handle.uws.edu.au:8081/1959.7/430.

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This study covers the following aspects of mine water management at the Clarence Colliery, located at the headwaters of the Wollangambe River, N.S.W. The Wollangambe River flows through the World Heritage listed areas of the Blue Mountains and Wollemi National Parks. 1. Quantification of the impact of discharge of treated mine water on the Wollangambe River, through analysis of sediment metal concentrations. 2. Investigation of the possible sources and causes of acid mine drainage within the mine. 3. Review of the current treatment process employed at the mine, as well as a review of other possible treatment options for avoidance or treatment of acid mine drainage. 4. Recommendation of a strategy for improving the process of mine water management at the colliery. The study reveals problems discovered from the investigation and describes the findings and recommendations.
Master of Engineering (Hons.)
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Kern, Christine Luise, e n/a. "Demarketing as a tool for managing visitor demand in national parks: an Australian case study". University of Canberra. Languages, International Studies & Tourism, 2006. http://erl.canberra.edu.au./public/adt-AUC20061114.125254.

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Nature-based tourism and recreation is a growing phenomenon around the world. In Australia, nature-based tourism represents an important part of the tourism sector and is to a large extent dependent on protected areas such as World Heritage areas, marine parks and national parks. While tourism and recreation can benefit protected areas, some are under pressure from visitation and marketing should play a role in managing visitor demand. To this end, a number of authors have suggested demarketing as a management tool to address situations of excess visitor demand, however, research on demarketing in protected areas is limited. To address this research gap, this thesis examines the use of demarketing in Australian national parks that face excess visitor demand using a case study on the Blue Mountains National Park. The thesis investigates factors that contribute to high visitor demand for the park, the use of demarketing to manage demand and factors that influence when and how demarketing is applied. Demarketing is that aspect of marketing that deals with discouraging customers in general or a certain class of customers in particular on either a temporary or permanent basis. In protected areas specifically, demarketing is concerned with reducing visitor numbers in total or selectively and redistributing demand spatially or temporarily. Six factors that contribute to high visitor demand for the national park were identified including the attractiveness of the park, its proximity to Sydney and the fact that the park is a renowned destination with icon sites. It was established that no holistic demarketing strategy is currently employed in the park and that the demarketing measures that are applied are not consciously used as demarketing. The measures used in the Blue Mountains National Park were discussed according to their association with the marketing mix components (4 Ps). Demarketing measures related to �product� include limiting recreational activities by defining specific areas where they can be conducted, limiting the duration of activities and closures of sites or features in the park. The measures related to �place� are the use of a booking system, limiting visitor numbers and group sizes, commercial licensing and limiting signage. Measures related to �price� are not extensively used in the park. The promotional demarketing measures applied include stressing restrictions and appropriate environmental behaviour in promotional material and nonpromotion of certain areas or experiences in the park. Importantly, these demarketing measures are not employed across the whole park or for all user groups, but are used for certain experiences in specific contexts and circumstances. Three types of factors influence the use of demarketing in the Blue Mountains National Park: pragmatic considerations, resource considerations and stakeholder interests. Pragmatic considerations include the feasibility and effectiveness of certain demarketing measures, which are influenced by the specific context of the national park. Resource considerations relate to financial, human and temporal resources and the findings suggest that a lack of resources influences and at times inhibits the use of demarketing measures. It was also found that various stakeholders have a profound influence on the use of demarketing measures. The stakeholder groups have diverse interests and therefore influence the use of demarketing in different ways by supporting or impeding certain measures. Based on the findings and limitations of this study, recommendations for government and future research are made. These emphasise among others the need for more consistent and comprehensive collection of visitor information to tailor management actions more effectively. It is also suggested that a more conscious and holistic application of demarketing measures may help to manage visitor demand to parks proactively to ensure that the resource remains for future generations.
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Kelleher, Matthew H. "Archaeology of sacred space the spatial nature of religious behaviour in the Blue Mountains National Park Australia /". Connect to full text, 2002. http://ses.library.usyd.edu.au/handle/2123/4138.

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Thesis (Ph. D.)--University of Sydney, 2003.
Title from title screen (viewed April 6, 2009). Submitted in fulfilment of the requirements for the degree of Doctor of Philosophy to the Dept. of Archaeology, Faculty of Arts. Degree awarded 2003; thesis submitted 2002. Includes bibliographical references. Also available in print form.
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Nolfi, Daniel C. "National Park Service Cave and Karst Resources Management Case Study: Great Smoky Mountains National Park". TopSCHOLAR®, 2011. http://digitalcommons.wku.edu/theses/1053.

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As discussed in the National Parks Service’s (NPS) Directors Orders/Natural Resources Management Reference Manual #77 and the 2006 NPS Management Policy Handbook, implementing a management plan specifically for cave and karst resources within a national park is paramount to afford these resources appropriate protection. With support from the Federal Cave Resources Protection Act and the National Park Service Organic Act of 1906, management actions protecting caves has begun to place significant importance outside the traditional cave environment onto a broader karst landscape. The need to understand and protect the karst environment and caves as a karst resource has taken a much larger role in the scientific literature and has increased interest in its federal management application. Proactive management through the use of holistic karst wide management plans and programs is shown to provide superior measures for resource protection when compared to the shortcomings associated with reactive cave focused management. The use of Great Smoky Mountains National Park (GRSM) as a case study supports the need to develop and implement a proactive cave and karst management plan specific to their resources. Management decisions with regards to cave and karst resources currently follow the park's general directives and Superintendent's Compendium. GRSM’s caves and karst areas represent unique resources, such as extensive vertical relief and rare biota, requiring special management in order to effectively protect them and to manage those who study and recreate within them. Characteristics such as these necessitate holistically addressing management of these resources.
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Shriner, Susan Ann. "Distribution of Breeding Birds in Great Smoky Mountains National Park". NCSU, 2002. http://www.lib.ncsu.edu/theses/available/etd-20011107-134136.

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We assessed the utility of developing predictive models of species distribution within a large contiguous forest based solely on GIS (Geographic Information Systems) data. We conducted more than 7000 point count surveys of breeding birds at approximately 4000 locations throughout Great Smoky Mountains National Park (GSMNP). We combined these empirical data with habitat, topographic, and location variables to develop logistic regression models for 20 breeding bird species. The mean of observed points correctly classified for evaluation data was 74.3% with a range of 67.4% to 83.1%. Mean improvement in model classification rates with the addition of a trend surface was 0.9% with a range of ?0.4% to 2.0%. We also assessed the importance of controlling for differences in species detectability in different vegetation types. Comparisons of models based on unlimited radius plot data with models based on fixed width plot data that minimized detectability differences between vegetation types showed classification rates dropped an average of 0.9% with a range of -3.8% to 3.7% for fixed width plots. In the eastern U.S., invasion of hemlock wooly adelgid (Homoptera: Adelgidae: Adelges tsugae) is transforming species composition of native forests by causing extensive mortality in eastern hemlock (Tsuga canadensis) populations. We assessed the potential effects of hemlock loss in GSMNP by evaluating current hemlock distribution and abundance patterns and identifying environmental correlates of hemlock presence. We investigated potential effects of hemlock mortality on the park's avifauna by identifying bird species associated with hemlock. Our results indicate hemlock is widespread in all vegetation strata at low and mid elevations and is the second most common tree species in the park. Hemlock presence is significantly associated with elevation, total relative moisture index, disturbance history, vegetation type, and bedrock geology. Sixteen of 30 common breeding bird species showed significant correlations with hemlock presence. Hemlock loss will favor increased abundance of avian species associated with early successional and disturbed habitats and reduced abundance of avian species associated with late successional forests.We compared breeding bird community structure and composition in old growth and mature second growth (65-100 years old) forests in the southern Appalachians using paired point count. We found few differences in the two communities. Comparisons of relative abundance based on counts of individual bird species showed two species were significantly more abundant on old growth sites and one species was significantly more abundant on second growth sites. After incorporating differential detectability into relative abundance estimates, we found that 4 breeding bird species were significantly more abundant in old growth sites compared to second growth sites and that no breeding bird species was significantly more abundant in second growth sites. These results highlight the importance of incorporating detectability measures into sampling and analytic methods. Analysis of vegetation samples for the paired sites showed significant differences between old growth and second growth sites. Old growth sites had significantly more large trees for classes > 50 cm diameter at breast height. Vegetation composition comparisons showed old growth sites had significantly more late successional species and significantly fewer species associated with early successional forests. Nonetheless, measures of species richness, relative abundance, and number of standing snags did not differ between old growth and second growth sites. Breeding bird composition similarities between old growth and second growth sites in this study may not be typical of more fragmented landscapes because large remaining patches of old growth forest adjacent to second growth sites may ameliorate differences between the

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Turner, Linda Ann. "Vegetation and chimpanzee ranging in the Mahale Mountains National Park, Tanzania". 京都大学 (Kyoto University), 2000. http://hdl.handle.net/2433/151674.

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Bailey, Larissa Lynn. "Estimating detection probabilities for terrestrial salamanders in Great Smoky Mountains National Park". Connect to this title online, 2002. http://www.lib.ncsu.edu/theses/available/etd-08022002-111548/unrestricted/etd.pdf.

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Jobe, R. Todd White P. S. "Biodiversity and scale determinants of species richness in Great Smoky Mountains National Park /". Chapel Hill, N.C. : University of North Carolina at Chapel Hill, 2006. http://dc.lib.unc.edu/u?/etd,398.

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Thesis (Ph. D.)--University of North Carolina at Chapel Hill, 2006.
Title from electronic title page (viewed Oct. 10, 2007). "... in partial fulfillment of the requirements for the degree of Doctor of Philosophy in the Curriculum of Ecology." Discipline: Ecology; Department/School: Ecology.
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Das, Raja. "Debris-Slide Susceptibility Modelling Using GIS Technology in the Great Smoky Mountains National Park". Digital Commons @ East Tennessee State University, 2019. https://dc.etsu.edu/etd/3630.

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Debris-slides are one of the most frequently occurring geological hazards in metasedimentary rocks of the Anakeesta ridge in Great Smoky Mountains National Park (GRSM), which often depends on the influence of multiple causing factors or geo-factors such as geological structures, slope, topographic elevation, land use, soil type etc. or a combination of these factors. The main objective of the study was to understand the control of geo-factors in initiating debris-slides using different knowledge and data-driven methods in GIS platform. The study was performed in three steps: (1) Evaluation of geometrical relationship between geological discontinuity and topographic orientation in initiation of debris-slides, (2) Preparation of knowledge-driven debris-slide susceptibility model, and (3) Preparation of data-driven debris-slide susceptibility models and compare their efficacy. Performance of the models were evaluated mostly using area under Receiver Operating Characteristic (ROC) curve, which revealed that the models were statistically significant.
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Livros sobre o assunto "Blue Mountains National Park"

1

Daly, Lyn. Take a Walk in Blue Mountains National Park. Brisbane, Australia: Take a Walk Publications, 2000.

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2

O'Hara, Pat. Great Smoky Mountains National Park: The place of Blue Smoke. San Rafael, Calif: Woodlands Press in conjunction with the Great Smoky Mountains Natural History Association, 1986.

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3

Blue Ridge Parkway guide: Grandfather Mountain to Great Smoky Mountains National Park, 291.9-469 miles. Birmingham, AL: Menasha Ridge Press, 1992.

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4

Hiking North Carolina's Blue Ridge Mountains: Blue Ridge Parkway, Great Smoky Mountains National Park, Hickory Nut Gorge, Linville Gorge, NC State Parks, Pisgah National Forestand much more. Almond, NC: Milestone Press, 2012.

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5

1944-, Pratt H. Douglas, ed. Birds of the Blue Ridge Mountains: A guide for the Blue Ridge Parkway, Great Smoky Mountains, Shenandoah National Park, and neighboring areas. Chapel Hill: University of North Carolina, 1992.

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6

Hiking the Carolina mountains: Appalachian Trail, Blue Ridge Parkway, DuPont State Forest, Great Smoky Mountains National Park, Pisgah & Nantahala National Forests, upstate South Carolina and much more. Almond, NC: Milestone Press, 2007.

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7

The ultimate guide to Asheville & Hendersonville: Including the Great Smoky Mountains National Park and the Blue Ridge Mountains of North Carolina. Alexander, NC: WorldComm, 1998.

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Pantas, Lee James. The ultimate guide to Asheville & Hendersonville: Including the Great Smoky Mountains National Park and the Blue Ridge Mountains of North Carolina. 2a ed. Alexander, NC: Alexander Books, 2000.

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Mallonee, Walter W. Origin of the Skyline Drive through the Shenandoah National Park in the Blue Ridge Mountains of Virginia. [United States: W.W. Mallonee], 1995.

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Hinkel, James R. Parkway byways: Explore the charming countryside close to the Blue Ridge Parkway, the Shenandoah National Park, the Great Smoky Mountain National Park. Boone, NC: Parkway Publishers, 1998.

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Capítulos de livros sobre o assunto "Blue Mountains National Park"

1

Woodward, Nicholas B. "Day nine- Gatlinburg, TN- Great Smoky Mountains National Park". In Geometry and Deformation Fabrics in the Central and Southern Appalachian Valley and Ridge and Blue Ridge: Frederick, Maryland to Allatoona Dam, Georgia July 20–27, 1989, 77–84. Washington, D. C.: American Geophysical Union, 1989. http://dx.doi.org/10.1029/ft357p0077.

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Muehlberger, William R., Patricia W. Dickerson, J. Russell Dyer e David V. LeMone. "Day 8—Big Bend National Park". In Structure and Stratigraphy of Trans-Pecos Texas: El Paso to Guadalupe Mountains and Big Bend July 20–29, 1989, 27–29. Washington, D. C.: American Geophysical Union, 1989. http://dx.doi.org/10.1029/ft317p0027.

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Cunha, Stephen F. "Allah’s Mountains: Establishing a National Park in the Central Asian Pamir". In WorldMinds: Geographical Perspectives on 100 Problems, 25–30. Dordrecht: Springer Netherlands, 2004. http://dx.doi.org/10.1007/978-1-4020-2352-1_5.

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Nakamura, Michio. "Long-Term Field Studies of Chimpanzees at Mahale Mountains National Park, Tanzania". In Long-Term Field Studies of Primates, 339–56. Berlin, Heidelberg: Springer Berlin Heidelberg, 2011. http://dx.doi.org/10.1007/978-3-642-22514-7_15.

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Muehlberger, W. R. "Geology of Big Bend National Park: II. Summary of the structural geology of Big Bend National Park and vicinity". In Structure and Stratigraphy of Trans-Pecos Texas: El Paso to Guadalupe Mountains and Big Bend July 20–29, 1989, 179–97. Washington, D. C.: American Geophysical Union, 1989. http://dx.doi.org/10.1029/ft317p0179.

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Chappelka, A., G. Somers e J. Renfro. "Visible Ozone Injury on Forest Trees in Great Smoky Mountains National Park, USA". In Forest Growth Responses to the Pollution Climate of the 21st Century, 255–60. Dordrecht: Springer Netherlands, 1999. http://dx.doi.org/10.1007/978-94-017-1578-2_18.

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Irwin, William P. "Terranes of the Klamath Mountains, California and Oregon". In Tectonic Evolution of Northern California: Sausalito to Yosemite National Park, California, June 28–July 7, 1989, 19–32. Washington, D. C.: American Geophysical Union, 1989. http://dx.doi.org/10.1029/ft108p0019.

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Tuttle, Julie P., e Peter S. White. "Structural and Compositional Change in Great Smoky Mountains National Park since Protection, 1930s–2000s". In Natural Disturbances and Historic Range of Variation, 263–94. Cham: Springer International Publishing, 2016. http://dx.doi.org/10.1007/978-3-319-21527-3_10.

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Tauvers, P. R., e W. R. Muehlberger. "Geology of Big Bend National Park: I. Persimmon Gap in Big Bend National Park, Texas; Ouachita facies and Cretaceous cover deformed in a laramide overthrust". In Structure and Stratigraphy of Trans-Pecos Texas: El Paso to Guadalupe Mountains and Big Bend July 20–29, 1989, 171–78. Washington, D. C.: American Geophysical Union, 1989. http://dx.doi.org/10.1029/ft317p0171.

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Grigorescu, Ines, Monica Dumitraşcu, Gheorghe Kucsicsa, Mihai Doroftei, Mihaela Năstase e Carmen-Sofia Dragotă. "Predicting the Potential Distribution of Ailanthus altissima, an Invasive Terrestrial Plant Species in Măcin Mountains National Park (Romania)". In Sustainable Mountain Regions: Challenges and Perspectives in Southeastern Europe, 159–72. Cham: Springer International Publishing, 2016. http://dx.doi.org/10.1007/978-3-319-27905-3_12.

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Trabalhos de conferências sobre o assunto "Blue Mountains National Park"

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Lazar, Marius Gabriel, Honoriu Valean, Neagu Madalin e Liviu Miclea. "Biodiversity management system in Rodna Mountains National Park". In 2010 IEEE International Conference on Automation, Quality and Testing, Robotics (AQTR 2010). IEEE, 2010. http://dx.doi.org/10.1109/aqtr.2010.5520779.

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O'Shea, Thomas, Samantha Farmer e Arpita Nandi. "COMMUNICATING ROCKFALL HAZARDS IN GREAT SMOKY MOUNTAINS NATIONAL PARK". In Joint 69th Annual Southeastern / 55th Annual Northeastern GSA Section Meeting - 2020. Geological Society of America, 2020. http://dx.doi.org/10.1130/abs/2020se-344268.

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Robinson, R. B., C. Roby, J. Buchanan, T. Barnett e S. E. Moore. "Storm Event Monitoring in the Great Smoky Mountains National Park". In World Water and Environmental Resources Congress 2005. Reston, VA: American Society of Civil Engineers, 2005. http://dx.doi.org/10.1061/40792(173)331.

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Robinson, R. B., J. C. Roby, J. R. Buchanan, T. W. Barnett e S. E. Moore. "Storm Event Monitoring in the Great Smoky Mountains National Park". In World Water and Environmental Resources Congress 2004. Reston, VA: American Society of Civil Engineers, 2004. http://dx.doi.org/10.1061/40737(2004)295.

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Millaku, Bedri, Adem Dreshaj e Elvis Elezaj. "NATURAL RESOURCES MANAGEMENT: THE CASE OF NATIONAL PARK OF �NEMUNA� MOUNTAINS". In 20th International Multidisciplinary Scientific GeoConference Proceedings SGEM 2020. STEF92 Technology, 2020. http://dx.doi.org/10.5593/sgem2020/5.1/s20.072.

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Odom, K. R., e R. B. Robinson. "Spatial Optimization of the Synoptic Sampling Network in the Great Smoky Mountains National Park". In World Water and Environmental Resources Congress 2004. Reston, VA: American Society of Civil Engineers, 2004. http://dx.doi.org/10.1061/40737(2004)400.

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Willis, Anna, Cheryl Waters-Tormey, David Kinner, Daniel Edwards, Courtney Hartman, Parker Lewis, Sean Price et al. "TRAIL-SCALE SLOPE FAILURE RISK MAPS: A PILOT STUDY IN GREAT SMOKY MOUNTAINS NATIONAL PARK". In 68th Annual GSA Southeastern Section Meeting - 2019. Geological Society of America, 2019. http://dx.doi.org/10.1130/abs/2019se-327129.

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Neff, Keil J., e John S. Schwartz. "Relations between Basin Characteristics and Stream Chemistry in the Great Smoky Mountains National Park, USA". In World Environmental and Water Resources Congress 2011. Reston, VA: American Society of Civil Engineers, 2011. http://dx.doi.org/10.1061/41173(414)194.

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Aksenova, Marina Y., Galina E. Kalacheva e Natalya Y. Letyarina. "THEORY AND ESTABLISHING PRACTICE OF ECOLOGICAL TOURIST TRAIL EXEMPLIFIED BY THE NATIONAL PARK «SENGILEY MOUNTAINS»". In Treshnikov readings – 2021 Modern geographical global picture and technology of geographic education. Ulyanovsk State Pedagogical University named after I. N. Ulyanov, 2021. http://dx.doi.org/10.33065/978-5-907216-08-2-2021-87-89.

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The paper presents the technology of creating an ecological-tourist trail. This technology includes several successive stages: organizational; theoretical; practical. This technology has been tested on the example of compiling the ecological-tourist trail “Walking along the Pushkin Trail” in the territory of the Sengileevsky Mountains National Park.
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Kumar, Jitendra, Jon Weiner, William W. Hargrove, Steven P. Norman, Forrest M. Hoffman e Doug Newcomb. "Characterization and Classification of Vegetation Canopy Structure and Distribution within the Great Smoky Mountains National Park Using LiDAR". In 2015 IEEE International Conference on Data Mining Workshop (ICDMW). IEEE, 2015. http://dx.doi.org/10.1109/icdmw.2015.178.

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Relatórios de organizações sobre o assunto "Blue Mountains National Park"

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Hop, Kevin, Andrew Strassman, Stephanie Sattler, Rickie White, Milo Pyne, Tom Govus e Jennifer Dieck. National Park Service Vegetation Mapping Inventory Program: Great Smoky Mountains National Park vegetation mapping project. National Park Service, julho de 2021. http://dx.doi.org/10.36967/nrr-2286888.

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Carpenter, Grace, e J. A. Beeco. Great Smoky Mountains National Park: Acoustic monitoring report 2016. National Park Service, junho de 2021. http://dx.doi.org/10.36967/nrr-2286646.

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Couture, R., e S. G. Evans. The East Gate Landslide, Beaver Valley, Glacier National Park, Columbia Mountains, British Columbia. Natural Resources Canada/ESS/Scientific and Technical Publishing Services, 2000. http://dx.doi.org/10.4095/211403.

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Evens, Julie, Kendra Sikes e Jaime Ratchford. Vegetation classification at Lake Mead National Recreation Area, Mojave National Preserve, Castle Mountains National Monument, and Death Valley National Park: Final report. National Park Service, setembro de 2020. http://dx.doi.org/10.36967/nrr-2278744.

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Henderson, Tim, Vincent Santucci, Tim Connors e Justin Tweet. National Park Service geologic type section inventory: Eastern Rivers and Mountains Inventory & Monitoring Network. National Park Service, abril de 2021. http://dx.doi.org/10.36967/nrr-2285263.

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Evans, Julie, Kendra Sikes e Jamie Ratchford. Vegetation classification at Lake Mead National Recreation Area, Mojave National Preserve, Castle Mountains National Monument, and Death Valley National Park: Final report (Revised with Cost Estimate). National Park Service, outubro de 2020. http://dx.doi.org/10.36967/nrr-2279201.

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Vegetation inventory and mapping is a process to document the composition, distribution and abundance of vegetation types across the landscape. The National Park Service’s (NPS) Inventory and Monitoring (I&M) program has determined vegetation inventory and mapping to be an important resource for parks; it is one of 12 baseline inventories of natural resources to be completed for all 270 national parks within the NPS I&M program. The Mojave Desert Network Inventory & Monitoring (MOJN I&M) began its process of vegetation inventory in 2009 for four park units as follows: Lake Mead National Recreation Area (LAKE), Mojave National Preserve (MOJA), Castle Mountains National Monument (CAMO), and Death Valley National Park (DEVA). Mapping is a multi-step and multi-year process involving skills and interactions of several parties, including NPS, with a field ecology team, a classification team, and a mapping team. This process allows for compiling existing vegetation data, collecting new data to fill in gaps, and analyzing the data to develop a classification that then informs the mapping. The final products of this process include a vegetation classification, ecological descriptions and field keys of the vegetation types, and geospatial vegetation maps based on the classification. In this report, we present the narrative and results of the sampling and classification effort. In three other associated reports (Evens et al. 2020a, 2020b, 2020c) are the ecological descriptions and field keys. The resulting products of the vegetation mapping efforts are, or will be, presented in separate reports: mapping at LAKE was completed in 2016, mapping at MOJA and CAMO will be completed in 2020, and mapping at DEVA will occur in 2021. The California Native Plant Society (CNPS) and NatureServe, the classification team, have completed the vegetation classification for these four park units, with field keys and descriptions of the vegetation types developed at the alliance level per the U.S. National Vegetation Classification (USNVC). We have compiled approximately 9,000 existing and new vegetation data records into digital databases in Microsoft Access. The resulting classification and descriptions include approximately 105 alliances and landform types, and over 240 associations. CNPS also has assisted the mapping teams during map reconnaissance visits, follow-up on interpreting vegetation patterns, and general support for the geospatial vegetation maps being produced. A variety of alliances and associations occur in the four park units. Per park, the classification represents approximately 50 alliances at LAKE, 65 at MOJA and CAMO, and 85 at DEVA. Several riparian alliances or associations that are somewhat rare (ranked globally as G3) include shrublands of Pluchea sericea, meadow associations with Distichlis spicata and Juncus cooperi, and woodland associations of Salix laevigata and Prosopis pubescens along playas, streams, and springs. Other rare to somewhat rare types (G2 to G3) include shrubland stands with Eriogonum heermannii, Buddleja utahensis, Mortonia utahensis, and Salvia funerea on rocky calcareous slopes that occur sporadically in LAKE to MOJA and DEVA. Types that are globally rare (G1) include the associations of Swallenia alexandrae on sand dunes and Hecastocleis shockleyi on rocky calcareous slopes in DEVA. Two USNVC vegetation groups hold the highest number of alliances: 1) Warm Semi-Desert Shrub & Herb Dry Wash & Colluvial Slope Group (G541) has nine alliances, and 2) Mojave Mid-Elevation Mixed Desert Scrub Group (G296) has thirteen alliances. These two groups contribute significantly to the diversity of vegetation along alluvial washes and mid-elevation transition zones.
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Truett, L. F. Strategic Plan for Coordinating Rural Intelligent Transportation System (ITS) Transit Development in the Great Smoky Mountains National Park. Office of Scientific and Technical Information (OSTI), dezembro de 2002. http://dx.doi.org/10.2172/885720.

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McLaughlin, Jr., S. (Growth and physiology of red spruce in relationship to acidic deposition in the Great Smoky Mountains National Park, USA). Office of Scientific and Technical Information (OSTI), outubro de 1989. http://dx.doi.org/10.2172/5520227.

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Buene, Eivind. Intimate Relations. Norges Musikkhøgskole, agosto de 2018. http://dx.doi.org/10.22501/nmh-ar.481274.

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Blue Mountain is a 35-minute work for two actors and orchestra. It was commissioned by the Ultima Festival, and premiered in 2014 by the Danish National Chamber Orchestra. The Ultima festival challenged me – being both a composer and writer – to make something where I wrote both text and music. Interestingly, I hadn’t really thought of that before, writing text to my own music – or music to my own text. This is a very common thing in popular music, the songwriter. But in the lied, the orchestral piece or indeed in opera, there is a strict division of labour between composer and writer. There are exceptions, most famously Wagner, who did libretto, music and staging for his operas. And 20th century composers like Olivier Messiaen, who wrote his own poems for his music – or Luciano Berio, who made a collage of such detail that it the text arguably became his own in Sinfonia. But this relationship is often a convoluted one, not often discussed in the tradition of musical analysis where text tend to be taken as a given, not subjected to the same rigorous scrutiny that is often the case with music. This exposition is an attempt to unfold this process of composing with both words and music. A key challenge has been to make the text an intrinsic part of the performance situation, and the music something more than mere accompaniment to narration. To render the words meaningless without the music and vice versa. So the question that emerged was how music and words can be not only equal partners, but also yield a new species of music/text? A second questions follows en suite, and that is what challenges the conflation of different roles – the writer and the composer – presents? I will try to address these questions through a discussion of the methods applied in Blue Mountain, the results they have yielded, and the challenges this work has posed.
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Barton, Andrew, e Helen Poulos. Evaluating conditions and trends for Sky Island forests in the Chisos Mountains, Big Bend National Park: Focused condition assessment report. National Park Service, agosto de 2021. http://dx.doi.org/10.36967/nrr-2287094.

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