Expand View Figure 2 Distribution and extent of MVGs mapped in the National Vegetation Information System version 6.0 MVG = major vegetation group Notes: Each state and territory undertakes field ecological surveys and variously integrates with data from aerial photography and satellite remote sensing to interpret and map the extent of their native vegetation. Those data are aggregated at the national level using data standards developed under the National Vegetation Information System (NVIS Technical Working Group 2017). Each jurisdiction’s definition of native vegetation is different, resulting in differences in the mapped interpretation of remnant vegetation. Total area of remaining native vegetation: 664 million hectares (86.5% of the Australian continent). Numbers against native MVGs in the legend are the extent of that MVG as a percentage of the total remaining native vegetation. Area of Cleared, non-native vegetation, buildings: 102 million hectares (13.2% of the Australian continent). Area of Regrowth, modified native vegetation: 2 million hectares (0.3% of the Australian continent). Sources: DAWE (2020g), using highly variable dates for source datasets from different states; map projection: Australian Albers GDA94 (ICSM n.d.) For more information, go toNative vegetation Share on Twitter Share on Facebook Share on Linkedin Share this link
Expand View Figure 2 Distribution and extent of MVGs mapped in the National Vegetation Information System version 6.0
Expand View Figure 62 Indigenous trainees on Roebuck Plains station, Yawuru country, Western Australia (left); Tourists and visitors at the Talaroo Hot Springs on Ewamian Country, Queensland (right) Photos: Indigenous Land and Sea Corporation For more information, go toManagement approaches Share on Twitter Share on Facebook Share on Linkedin Share this link
Expand View Figure 62 Indigenous trainees on Roebuck Plains station, Yawuru country, Western Australia (left); Tourists and visitors at the Talaroo Hot Springs on Ewamian Country, Queensland (right)
Expand View Figure 20 Burned area frequency in forests and grasslands from Advanced Very High Resolution Radiometer satellite imagery, 1988–2020 Source: DISER (2021d); Fire Scar data overlay reproduced by permission of the Western Australian Land Information Authority For more information, go toCarbon Share on Twitter Share on Facebook Share on Linkedin Share this link
Expand View Figure 20 Burned area frequency in forests and grasslands from Advanced Very High Resolution Radiometer satellite imagery, 1988–2020
Expand View Figure 73 Harvesting mi marral (Kakadu plum) at Wadeye, Palngun Wurnangat Aboriginal Corporation, Northern Territory (left). Mamabulanjin Aboriginal Corporation (Western Australia) and Thamarrurr Development Corporation (Northern Territory) have freeze-dried Kakadu plum powder for wholesale (right) Photos: left – Northern Australia Aboriginal Kakadu Plum Alliance; right – Indigenous Land and Sea Corporation For more information, go toManagement of specific pressures Share on Twitter Share on Facebook Share on Linkedin Share this link
Expand View Figure 73 Harvesting mi marral (Kakadu plum) at Wadeye, Palngun Wurnangat Aboriginal Corporation, Northern Territory (left). Mamabulanjin Aboriginal Corporation (Western Australia) and Thamarrurr Development Corporation (Northern Territory) have freeze-dried Kakadu plum powder for wholesale (right)
Expand View Figure 66 Erosion control projects that rehabilitate large and active gullies (left – before; right – after) well connected to river systems are the most effective at improving water quality in the Great Barrier Reef lagoon Photos: NQ Dry Tropics and Queensland Government Landholders Driving Change Program Source: Figure 67 in Bartley et al. (2020). Used with permission. For more information, go toManagement approaches Share on Twitter Share on Facebook Share on Linkedin Share this link
Expand View Figure 66 Erosion control projects that rehabilitate large and active gullies (left – before; right – after) well connected to river systems are the most effective at improving water quality in the Great Barrier Reef lagoon
Expand View Figure 5 Ecological carrying capacity of terrestrial habitat in (a) New South Wales in 2013, and (b) for part of the Brigalow Belt South (BBS) bioregion, adjacent to the Sydney Basin (SYB) bioregion Notes: Bioregion codes are defined in Thackway & Cresswell (1995) and DoE (2016). This indicator of ecological carrying capacity uses connectivity to account for fragmentation. Sources: Adapted from DPIE (2020d), based on data from Love et al. (2020); map projection: Geographic GDA94 (ICSM n.d.) For more information, go toNative vegetation Share on Twitter Share on Facebook Share on Linkedin Share this link
Expand View Figure 5 Ecological carrying capacity of terrestrial habitat in (a) New South Wales in 2013, and (b) for part of the Brigalow Belt South (BBS) bioregion, adjacent to the Sydney Basin (SYB) bioregion
Expand View Figure 3 Extent of remnant, regrowth/modified and removed native vegetation for each MVG, labelled with the extent of remnant native vegetation in that group as a percentage of its pre-1750 extent MVG = major vegetation group Notes: The classification and extent of native MVGs derive from pre-1750 mapping (DAWE 2020h). The current status of each pre-1750 MVG is assessed by comparing with the extant MVG mapping (DAWE 2020g) using the following categories: ‘Remnant’ is the area within the extent of each pre-1750 MVG (DAWE 2020i) that remains extant native vegetation (i.e. any one of the MVGs listed as ‘remnant native vegetation’ in Figure 2). ‘Removed’ is the area within the extent of each pre-1750 MVG (DAWE 2020i) that is now in the following extant MVG (DAWE 2020j): Cleared, non-native vegetation, buildings. ‘Regrowth/modified’ is the area within the extent of each pre-1750 MVG (DAWE 2020i) that is now in the following extant MVG (DAWE 2020j): Regrowth, modified native vegetation. MVGs not shown: Unclassified forest, Unclassified native vegetation, Sea and estuaries, and Unknown/no data. Sources: Based on DAWE (2020g), DAWE (2020h) Download Go to data.gov For more information, go toNative vegetation Share on Twitter Share on Facebook Share on Linkedin Share this link
Expand View Figure 3 Extent of remnant, regrowth/modified and removed native vegetation for each MVG, labelled with the extent of remnant native vegetation in that group as a percentage of its pre-1750 extent
Expand View Figure 59 Extent of Indigenous Protected Areas as of October 2020, and native title as of June 2021 ha = hectare Notes: 1 – Nantawarrina (58,347 ha); 2 – Preminghana (529 ha); 3 – Risdon Cove (79 ha); 4 – Putalina (38 ha); 5 – Deen Maar (427 ha); 6 – Yalata (464,397 ha); 7 – Watarru (1,657,183 ha); 8 – Walalkara (1,068,856 ha); 9 – Mount Chappell Island (323 ha); 10 – Badger Island (1,243 ha); 11 – Guanaba (99 ha); 12 – Warul Kawa (43 ha); 13 – Dhimurru (135,771 ha); 14 – Wattleridge (645 ha); 15 – Mount Willoughby (420,680 ha); 16 – Paruku (428,560 ha); 17 – Ngaanyatjarra (9,974,049 ha); 18 – Tyrendarra (237 ha); 19 – Toogimbie (4,114 ha); 20 – Anindilyakwa (261,053 ha); 21 – Laynhapuy - Stage 1 (478,248 ha); 22 – Ninghan (46,835 ha); 23 – Northern Tanami (4,003,654 ha); 24 – Warlu Jilajaa Jumu (1,616,606 ha); 25 – Kaanju Ngaachi Wenlock and Pascoe Rivers (179,889 ha); 26 – Babel Island (441 ha); 27 – Great Dog Island (354 ha); 28 – lungatalanana (8,159 ha); 29 – Pulu (15 ha); 30 – Tarriwa Kurrukun (0,929 ha); 31 – Angas Downs (320,385 ha); 32 – Warddeken (1,370,496 ha); 33 – Djelk (640,467 ha); 34 – Jamba Dhandan Duringala (38,294 ha); 35 – Kurtonitj (367 ha); 36 – Framlingham Forest (1,142 ha); 37 – Kalka–Pipalyatjara (558,522 ha); 38 – Boorabee and The Willows (2,713 ha); 39 – Lake Condah (1,522 ha); 40 – Marri-Jabin (Thamurrurr, Stage 1) (69,504 ha); 41 – Brewarrina Ngemba Billabong (261 ha); 42 – Uunguu (759,459 ha); 43 – Apara - Makiri - Punti (1,107,523 ha); 44 – Antara – Sandy Bore (842,623 ha); 45 – Dorodong (85 ha); 46 – Weilmoringle (4,073 ha); 47 – Yanyuwa (Barni – Wardimantha Awara) (130,412 ha); 48 – Minyumai (2,160 ha); 49 – Gumma (111 ha); 50 – Mandingalbay Yidinji (5,967 ha); 51 – Southern Tanami (10,153,508 ha); 52 – Angkum, Stage 1 (4,504 ha); 53 – Ngunya Jargoon (861 ha); 54 – Birriliburu (6,667,353 ha); 55 – Eastern Kuku Yalanji (20,515 ha); 56 – Bardi Jawi (126,967 ha); 57 – Girringun (14,865 ha); 58 – Wilinggin (2,438,911 ha); 59 – Dambimangari (617,211 ha); 60 – Balanggarra (1,090,905 ha); 61 – Thuwathu/Bujimulla (124,966 ha); 62 – Yappala (10,885 ha); 63 – Wardaman (224,696 ha); 64 – Karajarri (2,440,426 ha); 65 – Nijinda Durlga (186,330 ha); 66 – Warraberalgal and Porumalgal (63 ha); 67 – Kiwirrkurra (4,268,253 ha); 68 – Nyangumarta Warrarn (2,616,042 ha); 69 – Matuwa and Kurrara-Kurrara (596,642 ha); 70 – Katiti Petermann (5,043,754 ha); 71 – Ganalanga-Mindibirrina (1,093,286 ha); 72 – Wardang Island (3,930 ha); 73 – Marthakal (323,047 ha); 74 – South-East Arnhem Land (1,819,909 ha); 75 – Yawuru (115,828 ha); 76 – Mawonga (21,987 ha); 77 – Ngururrpa (2,962,988 ha); 78 – Ngadju (4,399,301 ha) Sources: DAWE (2021e), DAWE (2021ab), plus 2 additional Indigenous Protected areas gazetted October 2020 (Ngadju and Ngururrpa); NNTT (2021d); map projection: Australian Albers GDA94 (ICSM n.d.) For more information, go toManagement approaches Share on Twitter Share on Facebook Share on Linkedin Share this link
Expand View Figure 59 Extent of Indigenous Protected Areas as of October 2020, and native title as of June 2021
Stock Removed (ha) Remnant (ha) Regrowth/modified (ha) Not applicable (ha) Opening stock (NVIS 4.1 published in 2012) 100,480,723 665,380,436 1,047,420 2,491,405 Removed 0 −1,262,780 301,626 −32,091 Remnant 1,262,780 0 241,793 −141,480 Regrowth/modified −301,626 −241,793 0 −611,356 Not applicable 32,091 141,480 611,356 0 Closing stock (NVIS 6.0 published in 2020) 101,473,968 664,017,343 2,202,195 1,706,478 ha = hectare; MVG = major vegetation group; MVS = major vegetation subgroup; NVIS = National Vegetation Information System Notes: Areas are based on NVIS extant (‘present’) vegetation mapping. Specifically, NVIS v4.1 MVS (DSEWPaC 2012) and NVIS v6.0 MVG (DAWE 2020g), using the following categories: ‘Remnant’ is the area within the ‘present’ extent of MVSs in NVIS v4.1 (DSEWPaC 2012) or the MVGs in NVIS v6.0 (DAWE 2020g). In the case of NVIS v6.0, any one of the MVGs listed as ‘remnant native vegetation’ in Figure 2. ‘Removed’ is the area within the ‘present’ extent of MVSs in NVIS v4.1 (DSEWPaC 2012) or the MVG in NVIS v6.0 (DAWE 2020j): Cleared, non-native vegetation, buildings. ‘Regrowth/modified’ is the area within the ‘present’ extent of MVSs in NVIS v4.1 (DSEWPaC 2012) or MVG in NVIS v6.0 (DAWE 2020j): Regrowth, modified native vegetation. ‘Not applicable’ comprises Sea and estuaries, and Unknown/no data. 2. NVIS is an aggregation of each jurisdiction’s mapping of native vegetation extent, and the timestamps of these source datasets are highly variable. For more information, go toNative vegetation Share on Twitter Share on Facebook Share on Linkedin Share this link
Expand View Figure 1 Impacts of actions of varying ambitions on natural capital Note: Figure is an example based on DELWP (2017) Sources: Greaves (2021), DELWP (2017) For more information, go toLand and its natural capital values Share on Twitter Share on Facebook Share on Linkedin Share this link