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Bald Rock National Park Vegetation 1999 2006 VIS ID 4707
Bald Rock National Park vegetation mapping was undertaken by Dr John T. Hunter in 1999 by contract for the NPWS Northern Tableland Region along with Boonoo Boonoo National Park. The mapping was revised in 2006. Bald Rock National Park is located approximately 20 km north of Tenterfield and occurs in two sections. The vegetation of Bald Rock National Park is described and mapped (scale 1:25 000). This forms part one of the survey of lands within these two reserves with part two of the survey incorporating newly acquired lands. Ten communities are defined based on PATN analysis and one specialised community is as circumscribed by previous surveys. These eleven communities are mapped based on ground truthing, air photo interpretation and altitude. Most communities are of a Tall Open Forest structure, however Woodlands exist along with Heaths, Sedgelands, Shrublands and Closed Forest. The distribution of communities is related to drainage, aspect, slope and soil depth. Many of the communities show considerable variation and intergrade along common boundaries. A number of specialised communities are thought to be restricted to the reserve. VIS_ID 4707
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Boonoo Boonoo National Park Vegetation 1999 2006 VIS ID 4716
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Boonoo Boonoo National Park vegetation mapping was undertaken by Dr John T. Hunter in 1999 by contract for the NPWS Northern Tableland Region along with Bald Rock National Park. The mapping was revised in 2006. Boonoo Boonoo National Park is located approximately 30 km north east of Tenterfield. The vegetation of Boonoo Boonoo National Parks is described and mapped (scale 1:25 000). This forms part one of the survey of lands within these two reserves with part two of the survey incorporating newly acquired lands. Ten communities are defined based on PATN analysis and one specialised community is as circumscribed by previous surveys. These eleven communities are mapped based on ground truthing, air photo interpretation and altitude. Most communities are of a Tall Open Forest structure, however Woodlands exist along with Heaths, Sedgelands, Shrublands and Closed Forest. The distribution of communities is related to drainage, aspect, slope and soil depth. VIS_ID 4716
Kings Plain National Park Vegetation 2000 VIS ID 4741
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Kings Plain National Park vegetation mapping was undertaken by Dr John T. Hunter in 2000 by contract for the NPWS Northern Tableland Region. Kings Plain National Park approximately 50 km north west of Glen Innes. The full extent of the reserve is within the Inverell Shire, the County of Arrawatta and the Parish of Kings Plains. The vegetation of Kings Plains National Park is described and mapped (scale 1:25 000). Seven communities are defined based on PATN analysis and one specialised community is as circumscribed by previous surveys. Eight communities are mapped based on ground truthing, air photo interpretation and altitude. Most communities are of a Woodland structure, however Forests exist along with Shrublands. The distribution of communities is related to past disturbances, soil depth, soil type, physiography, aspect, slope, altitude, and protection from the south west. Many of the communities show considerable variation and intergrade along common boundaries. A number of specialised communities are thought to be endangered. VIS_ID 4741
Gibraltar Nature Reserve Vegetation 2002 VIS ID 4730
공공데이터포털
Gibraltar Nature Reserve vegetation mapping was undertaken by Dr John T. Hunter in 2002 by contract for the NPWS Northern Tableland Region. It is described in the Vegetation and Floristics of the Tenterfield Nature Reserves report which includes Bluff River, Bolivia Hill, Curry’s Gap, Gibraltar & Mt McKenzie. All reserves lie north of Glen Innes and south of Tenterfield on the Northern Tablelands of New South Wales and the New England Tablelands Bioregion. The local government area for all reserves is the Tenterfield Shire and the County of Clive. Gibraltar NR is located approximately 34 km west of Tenterfield. Incorporating 160 ha. The vegetation of five reserves within the Tenterfield area is described and mapped (scale 1:50 000). Fifteen communities are defined based on PATN analysis and an additional community is mapped based on information derived from previous investigations. These fifteen communities were mapped based on ground truthing, air photo interpretation and landform. Seven communities are considered of conservation importance with two of which were considered endangered and one should be considered vulnerable. Most communities are of woodland structure, although sedgelands, heaths, grasslands, open forests and tall open forests also occur. Many of the communities show considerable variation and intergrade along common boundaries and in particular on intermediate soil types. Physiography was the major correlative influence on community distribution, however protection from the north west and east, time since fire, grazing and geographic locality were also strongly correlated. VIS_ID 4730
Mount Mackenzie Nature Reserve Vegetation 2002 VIS ID 4747
공공데이터포털
Mount Mackenzie Nature Reserve vegetation mapping was undertaken by Dr John T. Hunter in 2002 by contract for the NPWS Northern Tableland Region. It is described in the Vegetation and Floristics of the Tenterfield Nature Reserves report which includes Bluff River, Bolivia Hill, Curry’s Gap, Gibraltar & Mt McKenzie. All reserves lie north of Glen Innes and south of Tenterfield in the New England Tablelands Bioregion. The local government area for all reserves is the Tenterfield Shire and the County of Clive. Mt McKenzie NR is approximately 5 km south west of Tenterfield. It encloses 141 ha. The vegetation of five reserves within the Tenterfield area is described and mapped (scale 1:50 000). Fifteen communities are defined based on PATN analysis and an additional community is mapped based on information derived from previous investigations. These fifteen communities were mapped based on ground truthing, air photo interpretation and landform. Seven communities are considered of conservation importance with two of which were considered endangered and one should be considered vulnerable. Most communities are of woodland structure, although sedgelands, heaths, grasslands, open forests and tall open forests also occur. Many of the communities show considerable variation and intergrade along common boundaries and in particular on intermediate soil types. Physiography was the majorcorrelative influence on community distribution, however protection from the north west and east, time since fire, grazing and geographic locality were also strongly correlated. VIS_ID 4747
Avondale State Conservation Area Vegetation 2014 VIS ID 4706
공공데이터포털
Avondale State Conservation Area vegetation mapping was undertaken by Dr John T. Hunter in 2014 by contract for the NPWS Northern Tableland Region. Avondale State Conservation Area is located approximately 36 km north east of Armidale and is accessed via the Rockvale Road. The reserve occurs on eastern side of the central New England Tablelands. The vegetation of Avondale State Conservation Area is described and mapped (scale1:10 000) based on ADS40 Imagery (2012). Six floristic communities are defined based on classification (Kulczynski association) and seven Plant Community Types (VIS) are mapped. These six floristic communities and seven PCTs were mapped based on ground truthing, ADS40 interpretation and landform. Two Threatened Ecological Communities (TECs) were recognised and mapped also. VIS_ID 4706
Cataract National Park & State Conservation Area 2006 VIS ID 4722
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Cataract National Park and State Conservation Area vegetation mapping was undertaken by Dr John T. Hunter in 2006 by contract for the NPWS Northern Tableland Region. Cataract NP and SCA are located approximately 20km north of Drake near Tenterfield and comprise around 4,000 ha of lands. The north eastern boundary of the study area is bordered by the Clarence River. The lands are mainly mountainous with many incised creeks and escarpment areas. The lands lie in the North Coast Botanical District. The vegetation of Cataract National Park and State Conservation Area is described and mapped (scale 1:25 000). Seven communities are defined based on classification (Kulczynski association). These seven communities were mapped based on ground truthing, air photo interpretation and landform. Much of the reserve is dominated by grassy forests and woodlands usually with Allocasuarina torulosa (Forest Oak), Eucalytpus biturbinata (Grey Gum) and Eucalytpus crebra (Ironbark) with an understorey of Cymbopogon refractus (Barbed-wire Grass), Imperata cylindrical (Blady Grass) and Poa sieberiana (Tussock Grass). Much of the reserve has been disturbed in the past, particularly by clearing, logging and grazing. No listed threatened communities or flora species were noted. A total of 437 vascular plant taxa were found from 108 families and 285 genera. VIS_ID 4722
Gibraltar Range National Park Vegetation 2002 VIS ID 4731
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Gibraltar Range and southern Washpool National Parks vegetation mapping was undertaken by Paul Sheringham and Dr John T. Hunter in 2002 by contract for the NPWS Northern Tableland Region. The study area includes Gibraltar Range National Park and the southern section of the Washpool National Park on the north coast and northern tablelands in north eastern New South Wales. The park is located on the Great Diving Range approximately 90 km east of Grafton and about 65 km east Glen Innes. The Gibraltar range straddles the northern tablelands and north coast botanical subdivisions. The vegetation of Gibraltar Range and southern Washpool National Parks is described and mapped (scale 1:25 000). Twelve communities are defined based on PATN analysis, a thirteen is defined based on previous investigations, ten broad community associations are mapped. These ten mapping communities were mapped based on ground truthing, air photo interpretation and landform. Two communities are considered vulnerable and three rare. Most communities are of open forest structure, although sedgelands, heaths, woodlands, mallee scrubs, tall open forests and closed forests also occur. Many of the communities show considerable variation and intergrade along common boundaries. VIS_ID 4731
Bluff River Nature Reserve Vegetation VIS ID 4714
공공데이터포털
Bluff River Nature Reserve vegetation mapping was undertaken by Dr John T. Hunter in 2002 by contract for the NPWS Northern Tableland Region. It is described in the Vegetation and Floristics of the Tenterfield Nature Reserves report which includes Bluff River, Bolivia Hill, Curry’s Gap, Gibraltar & Mt McKenzie. All reserves lie north of Glenn Innes and south of Tenterfield on the Northern Tablelands of New South Wales and the New England Tablelands Bioregion. The local government regions for all reserves are the Tenterfield Shire and the County of Clive. Bluff River NR is located approximately 35 km north of Deepwater and incorporates 1793 ha. The vegetation of five reserves within the Tenterfield area is described and mapped (scale 1:50 000). Fifteen communities are defined based on PATN analysis and an additional community is mapped based on information derived from previous investigations. These fifteen communities were mapped based on ground truthing, air photo interpretation and landform. Seven communities are considered of conservation importance with two of which were considered endangered and one should be considered vulnerable. Most communities are of woodland structure, although sedgelands, heaths, grasslands, open forests and tall open forests also occur. Many of the communities show considerable variation and intergrade along common boundaries and in particular on intermediate soil types. Physiography was the major correlative influence on community distribution, however protection from the north west and east, time since fire, grazing and geographic locality were also strongly correlated. VIS_ID 4714
Maryland National Park Vegetation 2006. VIS ID 4745
공공데이터포털
Maryland National Park vegetation mapping was undertaken by Dr John T. Hunter in 2006 by contract for the NPWS Northern Tableland Region. Maryland NP lies within NSW approximately 20km north east of Stanthorpe, Qld and comprises some 2,284 ha of lands. Parts of these reserved lands were once under the control and management of State Forests, while other more recent additions were free hold land used for grazing enterprises. The reserve lies along the NSW-Qld border and is half within the Northern Tablelands and half in the North Coast Botanical Divisions. The lands are incorporated entirely within the New England Tablelands Bioregion within the local government areas of the Parish of Marsh, County of Buller and Shire of Tenterfield. The vegetation of Maryland National Park is described and mapped (scale 1:25 000). Six communities are defined based on classification (Kulczynski association). These six communities were mapped based on ground truthing, air photo interpretation and landform. Almost all of the reserve is dominated by the Eucalyptus biturbinata, Eucalyptus campanulata and Lophostemon confertus. Much of the reserve has been disturbed in the past, particularly by Logging, clearing and grazing. The original mapping was recorded as VIS ID_457 and this version has the addition of PCT and fire veg classification fields. VIS_ID 4745
Mount Yarrowyck Nature Reserve Vegetation 2015 VIS ID 4748
공공데이터포털
Mount Yarrowyck Nature Reserve vegetation mapping was undertaken by Dr John T. Hunter in 2015 by contract for the NPWS Northern Tableland Region. Mount Yarrowyck Nature Reserve is located 30 km west of Armidale and was established in 1983. It covers an area of 589ha and protects a significant Aboriginal Site. The vegetation of Mt Yarrowyck Nature Reserve is described and mapped (scale 1:10 000) based on ADS40 Imagery (2012). Nine floristic communities are defined based on classification (Kulczynski association). Nine five communities were mapped based on ground truthing, air photo interpretation and landform. In addition eight Plant Community Types (VIS PCT) from within four Keith Classes are also mapped along with one Threatened Ecological Communities (TECs). The current mapping of the TEC is likely to be overestimated at this stage and would require specific on ground targeted work to more accurately delineate its potential boundaries. VIS_ID 4748