Land clearing impact on woody native vegetation
Key Finding
In 2016–2017, 356,000 hectares per year (ha/year) of woody vegetation was cleared, statewide. This represented a 9% decrease from 2015–2016. In 2017–2018, 392,000 hectares per year (ha/year) of woody vegetation was cleared, statewide. This represented a 10% increase from 2016–2017.
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Queensland
Land clearing is mapped annually in Queensland by the Statewide Landcover and Trees Study (SLATS). SLATS uses Landsat satellite imagery to map the location and extent of woody vegetation clearing that is the result of human removal of vegetation across the entire state of Queensland.
The total woody vegetation clearing rate for Queensland in 2016–2017 was 356,000ha/year. This represented a 9% decrease from the 2015–2016 woody vegetation clearing rate of 390,000ha/year. In 2017–2018, the clearing rate was 392,000ha/year, a 10% increase from the 2016–2017 reporting period.
Clearing of remnant woody vegetation decreased from 132,000ha/year in 2015–2016 to 78,000ha/year in 2016–2017, a 41% reduction. This represented 22% of the total statewide woody vegetation clearing in 2016–2017. Remnant woody vegetation clearing decreased a further 5% in 2017–2018 to 74,000ha/year. This represented 19% of the total statewide woody vegetation clearing.
In 2017–2018, the non-remnant woody vegetation clearing rate was 318,000ha/year, 14% higher than the 278,000ha/yr cleared in 2016–2017. In 2015–2016, the non-remnant woody vegetation clearing rate was 257,000ha/yr.
Pasture has historically been the dominant land cover replacement class in SLATS mapping of land clearing, and it remained as such in both the 2016–2017 and 2017–2018 reporting periods, representing approximately 91% and 93% of the total statewide clearing, respectively. Other land cover replacement classes including crops, forestry, mining, infrastructure and settlement comprised the remainder.
Brigalow Belt
The Brigalow Belt (BRB) bioregion recorded the highest rate of woody vegetation clearing of all bioregions in the state in 2016–2017 and 2017–2018.
The rate of 204,000 hectares per year (ha/year) in 2017–2018 made up 52% of the statewide total.
This was a 6% increase from the woody vegetation clearing rate in 2016–2017 (193,000ha/year). The 2017–2018 rate was slightly lower than that of 2015–2016 (207,000ha/year).
The rate of remnant woody vegetation clearing in 2017–2018 was 23,000ha/year compared with 37,000ha/year in 2016–2017 and 45,000ha/year in 2015–2016.
The non-remnant woody vegetation clearing in the BRB increased by 16% between 2016–2017 (156,000ha/year) and 2017–2018 (181,000ha/year).
Pasture was the dominant replacement land cover class, representing 94% of the total clearing for both 2016–2017 and 2017–2018. Cropping was the second highest land cover replacement class at 3% and 4% of total clearing for 2016–2017 and 2017–2018, respectively, within BRB.
Cape York Peninsula
The woody vegetation clearing rate for 2016–2017 in the Cape York Peninsula (CYP) bioregion was 4,000 hectares per year (ha/year), a 57% increase from 2015–2016.
In 2017–2018, the clearing rate was 2,000ha/year, a 32% decrease from 2016–2017.
Remnant woody vegetation clearing made up 57% of total clearing in CYP in 2017–2018. This compared with 78% of total clearing in 2016–2017.
Mining was the dominant replacement land cover class in CYP accounting for 84% of total clearing.
Central Queensland Coast
The woody vegetation clearing rate for the Central Queensland Coast (CQC) bioregion was 2,000 hectares per year (ha/year) for 2016–2017. This represented a 58% decrease in the clearing rate compared with the 2015–2016 SLATS reporting period.
In 2017–2018, there was a further 12% decrease in the clearing rate since 2016–2017.
Clearing of remnant woody vegetation decreased by 48% in 2016–2017 from 2015–2016. The clearing rate also decreased by 52% between 2016–2017 and 2017–2018.
Remnant clearing made up 38% and 21% of total clearing in CQC for 2016–2017 and 2017–2018, respectively.
Pasture dominated as a replacement land cover class, at 85% in 2016–2017 and 72% in 2017–2018.
Channel Country
The woody vegetation clearing rate in the Channel Country (CHC) bioregion was less than 1,000 hectares per year (ha/year) in 2016–2017 and 2017–2018.
While the total clearing rate for the CHC was relatively low compared to other bioregions, the rate of remnant woody vegetation clearing increased two-fold between 2016–2017 and 2017–2018. Clearing of remnant woody vegetation in 2016–2017 and 2017–2018 accounted for 61% and 96%, respectively, of total clearing in CHC. The CHC is generally dominated by non-woody vegetation communities.
Pasture remained the dominant replacement land cover class, accounting for 98% and 97% of total clearing in 2016–2017 and 2017–2018, respectively.
Desert Uplands
The woody vegetation clearing rate for the Desert Uplands (DEU) bioregion for 2016–2017 was 31,000 hectares per year (ha/year), slightly less than 2015–2016 (32,000ha/year). In 2017–2018 it was 21,000ha/year, a decrease of 32% from 2016–2017.
The remnant woody vegetation clearing rate was 8,000ha/year in 2016–2017, a decrease of 51% from the 2015–2016 remnant clearing rate (17,000ha/year). The remnant clearing rate decreased a further 23% in 2017–2018 to 6,000ha/year compared with the 2016–2017 rate.
Remnant woody vegetation clearing accounted for 30% of total clearing in 2017–2018 in DEU.
The pasture replacement land cover class accounted for almost all woody vegetation clearing in DEU in these reporting periods.
Einasleigh Uplands
The woody vegetation clearing rate for the Einasleigh Uplands (EIU) bioregion was 4,000 hectares per year (ha/year) in 2016–2017, similar to the previous reporting period.
In 2017–2018, the clearing rate was 2,000ha/year, a decrease of 41% in the clearing rate in 2016–2017.
In the 2016–2017 reporting period, the clearing rate of remnant woody vegetation decreased by 10% while non-remnant clearing increased by 47% from the previous period. The remnant woody vegetation clearing rate decreased by 52% between 2016–2017 and 2017–2018.
Remnant woody vegetation clearing made up 72% and 59% of total clearing in EIU in 2016–2017 and 2017–2018, respectively.
Pasture remained the dominant replacement land cover class for both reporting periods in the EIU bioregion.
Gulf Plains
The woody vegetation clearing rate for the Gulf Plains (GUP) bioregion was 4,000 hectares per year (ha/year) in 2017–2018. This represented a 19% decrease from 2016–2017 (5,000ha/year). The clearing rate in 2016–17 represented a 75% decrease compared with the 2015–2016 reporting period (20,000ha/year).
The remnant woody vegetation clearing rate in for 2016–2017 was 4,000ha/year (75% of total clearing). This was a 78% decrease from the 2015–2016 remnant clearing rate of 16,000ha/year.
In 2017–2018, the remnant woody vegetation clearing rate was 2,000ha/year, a 53% decrease from the remnant clearing rate in 2016–2017.
Pasture was the dominant replacement land cover class for all reporting periods in the GUP bioregion.
Mitchell Grass Downs
The woody vegetation clearing rate in the Mitchell Grass Downs (MGD) bioregion was 14,000 hectares per year (ha/year) in 2016–2017. This was 3% more than the clearing rate in 2015–2016 (13,000ha/year).
In 2017–2018, the woody vegetation clearing rate was 25,000ha/year, an increase of 83% from 2016–2017 (14,000ha/year).
Remnant woody vegetation clearing decreased by 25% from 6,000ha/year in 2015–2016 to 5,000ha/year in 2017–2018. In 2017–2018, remnant clearing was 8,000ha/year, a 60% increase from the 2016–2017 reporting period (5,000ha/year).
The non-remnant clearing rate in 2017–2018 was 18,000ha/year. This was a 96% increase compared with the previous reporting period (9,000ha/year in 2016–2017).
The pasture accounted for all woody vegetation clearing in MGD.
Mulga Lands
In 2017–2018, the Mulga Lands (MUL) bioregion recorded the second highest woody vegetation clearing rate of all bioregions across Queensland at 106,000 hectares per year (ha/year). This represented 27% of the total statewide clearing.
In 2016–2017, the woody vegetation clearing rate was 73,000ha/year while in 2015–2016, 82,000ha/year was cleared.
The rate of clearing of remnant woody vegetation in 2016–2017 was 14,000ha/year (19% of total clearing in MUL). This represented a 63% decrease in the remnant woody vegetation clearing rate from 2015–2016 (38,000ha/year).
In 2017–2018, the rate of clearing of remnant woody vegetation was 29,000ha/year (27% of total clearing in MUL). This represented a 110% increase in the remnant woody vegetation clearing rate from 2016–2017.
Non-remnant woody vegetation clearing increased from 45,000ha/year in 2015–2016 to 59,000ha/year in 2016–2017 and again increased to 77,000ha/year in 2017–2018.
The pasture replacement land cover class accounted for the majority of woody vegetation cleared in MUL.
New England Tableland
The New England Tableland (NET) bioregion recorded a woody vegetation clearing rate of 4,000 hectares per year (ha/year) in 2016–2017. This represented a 47% increase in the woody vegetation clearing rate from the previous period.
In 2017–2018, the woody vegetation clearing rate decreased by 20% from 2016–2017.
Remnant woody vegetation clearing in this bioregion was less than 1,000ha/year for both 2016–2017 and 2017–2018. The remnant clearing rate increased by 20% in 2016–2017 from the previous period and decreased by 8% between 2016–2017 and 2017–2018.
Non-remnant clearing increased by 52% from 2015–2016 to 3,000ha/year in 2016–2017.
Clearing of non-remnant vegetation decreased by 22% from 2016–2017 to 2017–2018.
Remnant woody vegetation clearing contributed 14% and 16% of total clearing in NET for 2016–2017 and 2017–2018, respectively.
Pasture was the dominant replacement land cover class for both periods.
Northwest Highlands
The total woody vegetation clearing rate for Northwest Highlands (NWH) bioregion was less than 1,000 hectares per year (ha/year) in both 2016–2017 and 2017–2018.
The clearing rate in 2016–2017 represented an increase of 2% from the previous 2015–2016 reporting period, while in 2017–2018 the clearing rate decreased by 63% from 2016–2017.
The rate of remnant woody vegetation clearing increased by 6% between 2015–2016 and 2016–2017 and decreased by 69% between 2016–2017 and 2017–2018. The majority of clearing in this bioregion was classed as remnant woody vegetation during 2016–2017 (99% of total clearing) and 2017–2018 (82% of total clearing).
Pasture was the dominant replacement land cover class of total woody vegetation clearing in NWH in both periods.
Southeast Queensland
The total woody vegetation clearing rate for the Southeast Queensland (SEQ) bioregion in 2017–2018 was 21,000 hectares per year (ha/year), a decrease of 15% from 2016–2017.
In 2016–2017, the total woody vegetation clearing rate was 24,000ha/year, a 16% increase on 2015–2016.
Remnant woody vegetation clearing decreased by 8% between 2015–2016 and 2016–2017. This represented 11% of total clearing for the 2016–2017 mapping period in SEQ. Non-remnant woody vegetation clearing increased by 20% between 2015–2016 and 2016–2017.
In 2017–2018, clearing of remnant woody vegetation decreased by 8% from 2016–2017. This represented 12% of total clearing in that reporting period. There was also a decrease of 16% in non-remnant woody vegetation clearing between 2016–2017 and 2017–2018.
In 2016–2017, forestry was the dominant replacement land cover class in SEQ, accounting for 50% of total clearing. Pasture made up a further 40% of the total clearing.
In 2017–2018, pasture replaced forestry as the dominant replacement land cover class at 46% of total clearing. Forestry was slightly less at 44% of the total clearing.
Wet Tropics
The total woody vegetation clearing rate in the Wet Tropics (WET) bioregion was 2,000 hectares per year (ha/year) in 2016–2017. This represented a 32% increase of woody vegetation clearing from 2015–2016 for the bioregion.
In 2017–2018, the total woody vegetation clearing rate was 1,000ha/year, a decrease of 35% from 2016–2017.
The rate of remnant woody vegetation clearing increased by 47% in 2016–2017 compared to the previous period. This was 15% of total clearing in the bioregion in 2016–2017. Non-remnant clearing increased by 30% between 2015–2016 and 2016–2017.
In contrast, remnant woody vegetation clearing decreased by 34% in 2017–2018 (16% of total clearing), and non-remnant clearing also decreased by 35% compared to the previous period.
Forestry continued to be the largest replacement land cover class in the WET bioregion, accounting for 78% of total clearing in 2016–2017 and 71% in 2017–2018.
More information:
Relevant Sustainable Development Goals’ targets
Extent of total woody vegetation clearing, by bioregion
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| Region | Brigalow Belt | Cape York Peninsula | Central Queensland Coast | Channel Country | Desert Uplands | Einasleigh Uplands | Gulf Plains | Mitchell Grass Downs | Mulga Lands | New England Tableland | Northwest Highlands | Southeast Queensland | Wet Tropics |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| 1988–1989 | 453,953 | 2,443 | 4,376 | 1,661 | 46,704 | 7,070 | 6,968 | 52,946 | 124,977 | 5,442 | 153 | 15,829 | 3,613 |
| 1989–1990 | 453,953 | 2,443 | 4,376 | 1,661 | 46,704 | 7,070 | 6,968 | 52,946 | 124,977 | 5,442 | 153 | 15,829 | 3,613 |
| 1990–1991 | 453,953 | 2,443 | 4,376 | 1,661 | 46,704 | 7,070 | 6,968 | 52,946 | 124,977 | 5,442 | 153 | 15,829 | 3,613 |
| 1991–1992 | 160,949 | 1,327 | 1,766 | 203 | 35,820 | 2,635 | 1,225 | 19,686 | 65,913 | 2,109 | 53 | 11,589 | 3,320 |
| 1992–1993 | 160,949 | 1,327 | 1,766 | 203 | 35,820 | 2,635 | 1,225 | 19,686 | 65,913 | 2,109 | 53 | 11,589 | 3,320 |
| 1993–1994 | 160,949 | 1,327 | 1,766 | 203 | 35,820 | 2,635 | 1,225 | 19,686 | 65,913 | 2,109 | 53 | 11,589 | 3,320 |
| 1994–1995 | 160,949 | 1,327 | 1,766 | 203 | 35,820 | 2,635 | 1,225 | 19,686 | 65,913 | 2,109 | 53 | 11,589 | 3,320 |
| 1995–1996 | 199,693 | 2,230 | 5,054 | 2,197 | 33,255 | 4,001 | 4,592 | 16,698 | 56,639 | 3,251 | 537 | 15,101 | 2,201 |
| 1996–1997 | 199,693 | 2,230 | 5,054 | 2,197 | 33,255 | 4,001 | 4,592 | 16,698 | 56,639 | 3,251 | 537 | 15,101 | 2,201 |
| 1997–1998 | 245,496 | 1,879 | 2,675 | 472 | 39,828 | 2,702 | 1,747 | 18,695 | 83,435 | 3,022 | 866 | 15,625 | 1,201 |
| 1998–1999 | 245,496 | 1,879 | 2,675 | 472 | 39,828 | 2,702 | 1,747 | 18,695 | 83,435 | 3,022 | 866 | 15,625 | 1,201 |
| 1999–2000 | 364,893 | 1,407 | 5,708 | 357 | 65,243 | 5,450 | 1,664 | 52,444 | 191,455 | 2,904 | 591 | 21,869 | 1,486 |
| 2000–2001 | 211,416 | 2,089 | 3,522 | 337 | 58,543 | 3,931 | 3,981 | 31,470 | 124,224 | 1,406 | 552 | 17,700 | 546 |
| 2001–2002 | 224,051 | 552 | 1,570 | 398 | 42,913 | 2,768 | 2,280 | 24,979 | 165,839 | 1,229 | 351 | 16,726 | 987 |
| 2002–2003 | 159,891 | 781 | 1,745 | 2,139 | 39,269 | 1,680 | 2,491 | 20,502 | 299,480 | 4,412 | 240 | 18,684 | 1,084 |
| 2003–2004 | 213,581 | 1,564 | 3,215 | 1,098 | 29,555 | 3,525 | 5,143 | 26,958 | 179,694 | 3,132 | 242 | 21,305 | 1,060 |
| 2004–2005 | 143,591 | 2,316 | 2,079 | 1,438 | 22,945 | 2,505 | 10,987 | 16,151 | 136,304 | 1,998 | 202 | 20,331 | 1,192 |
| 2005–2006 | 122,822 | 2,298 | 2,597 | 2,335 | 30,683 | 5,641 | 4,915 | 13,046 | 172,695 | 4,114 | 304 | 15,675 | 1,547 |
| 2006–2007 | 93,476 | 4,481 | 2,162 | 5,377 | 7,427 | 4,929 | 4,143 | 9,750 | 95,542 | 2,279 | 501 | 17,425 | 1,611 |
| 2007–2008 | 51,865 | 3,159 | 2,511 | 1,078 | 3,236 | 3,331 | 1,887 | 6,214 | 37,555 | 3,156 | 112 | 16,071 | 962 |
| 2008–2009 | 43,060 | 2,494 | 1,040 | 123 | 3,273 | 2,666 | 806 | 10,374 | 28,430 | 1,727 | 97 | 11,131 | 414 |
| 2009–2010 | 39,068 | 1,299 | 656 | 149 | 2,043 | 1,263 | 1,812 | 8,541 | 15,199 | 1,297 | 83 | 12,056 | 284 |
| 2010-2011 | 45,350 | 1,000 | 754 | 324 | 4,446 | 1,387 | 1,166 | 5,957 | 18,746 | 1,338 | 172 | 10,679 | 813 |
| 2011-2012 | 88,965 | 1,799 | 1,303 | 132 | 8,440 | 1,239 | 2,352 | 6,537 | 29,518 | 2,557 | 250 | 10,603 | 1,357 |
| 2012-2013 | 143,853 | 2,089 | 1,208 | 203 | 8,529 | 3,175 | 1,264 | 14,799 | 69,798 | 1,746 | 298 | 12,865 | 1,146 |
| 2013-2014 | 131,582 | 2,568 | 1,820 | 575 | 13,997 | 1,763 | 3,593 | 14,073 | 108,045 | 1,280 | 193 | 13,892 | 1,308 |
| 2014-2015 | 131,869 | 3,269 | 3,011 | 1,220 | 19,155 | 2,500 | 18,250 | 25,884 | 65,696 | 4,314 | 148 | 21,295 | 1,404 |
| 2015-2016 | 206,560 | 2,253 | 4,183 | 362 | 32,070 | 4,046 | 18,881 | 13,299 | 82,439 | 2,534 | 201 | 21,031 | 1,737 |
| 2016-2017 | 193,381 | 3,536 | 1,759 | 307 | 31,207 | 4,074 | 4,710 | 13,678 | 72,530 | 3,718 | 205 | 24,387 | 2,294 |
| 2017-2018 | 204,273 | 2,421 | 1,553 | 403 | 21,084 | 2,395 | 3,795 | 25,097 | 106,169 | 2,968 | 76 | 20,799 | 1,490 |
Proportion of replacement landcover (clearing type)
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| Clearing | Pasture | Crop | Settlement | Mining | Infrastructure | Forestry |
|---|---|---|---|---|---|---|
| 1988–1989 | 646,388 | 55,547 | 3,038 | 2,293 | 15,589 | 3,280 |
| 1989–1990 | 646,388 | 55,547 | 3,038 | 2,293 | 15,589 | 3,280 |
| 1990–1991 | 646,388 | 55,547 | 3,038 | 2,293 | 15,589 | 3,280 |
| 1991–1992 | 279,404 | 14,800 | 2,451 | 1,695 | 3,164 | 5,081 |
| 1992–1993 | 279,404 | 14,800 | 2,451 | 1,695 | 3,164 | 5,081 |
| 1993–1994 | 279,404 | 14,800 | 2,451 | 1,695 | 3,164 | 5,081 |
| 1994–1995 | 279,404 | 14,800 | 2,451 | 1,695 | 3,164 | 5,081 |
| 1995–1996 | 296,574 | 30,578 | 2,546 | 2,702 | 8,499 | 4,550 |
| 1996–1997 | 296,574 | 30,578 | 2,546 | 2,702 | 8,499 | 4,550 |
| 1997–1998 | 366,610 | 29,570 | 1,542 | 2,423 | 10,274 | 7,224 |
| 1998–1999 | 366,610 | 29,570 | 1,542 | 2,423 | 10,274 | 7,224 |
| 1999–2000 | 667,964 | 25,403 | 1,927 | 1,314 | 11,858 | 7,005 |
| 2000–2001 | 429,516 | 8,100 | 1,557 | 1,923 | 10,969 | 7,652 |
| 2001–2002 | 467,382 | 889 | 1,762 | 1,712 | 6,803 | 6,095 |
| 2002–2003 | 536,713 | 649 | 3,563 | 1,531 | 4,416 | 5,526 |
| 2003–2004 | 472,071 | 388 | 3,558 | 3,363 | 7,022 | 3,670 |
| 2004–2005 | 341,214 | 1,472 | 1,764 | 3,037 | 5,365 | 9,187 |
| 2005–2006 | 360,745 | 363 | 1,486 | 3,544 | 2,536 | 9,998 |
| 2006–2007 | 233,289 | 181 | 1,523 | 4,269 | 2,860 | 6,981 |
| 2007–2008 | 113,039 | 151 | 2,426 | 3,930 | 2,645 | 8,946 |
| 2008–2009 | 92,826 | 84 | 1,911 | 2,438 | 2,588 | 5,788 |
| 2009–2010 | 70,202 | 160 | 1,403 | 3,125 | 1,817 | 7,043 |
| 2010-2011 | 73,538 | 446 | 1,401 | 2,738 | 7,053 | 6,956 |
| 2011-2012 | 135,325 | 484 | 1,367 | 5,593 | 5,162 | 7,121 |
| 2012-2013 | 236,083 | 2,297 | 1,061 | 6,073 | 7,201 | 8,258 |
| 2013-2014 | 271,205 | 4,040 | 1,128 | 5,064 | 4,130 | 9,122 |
| 2014-2015 | 270,970 | 4,932 | 1,652 | 3,249 | 1,392 | 15,820 |
| 2015-2016 | 363,494 | 4,464 | 1,144 | 2,506 | 1,537 | 16,451 |
| 2016-2017 | 323,458 | 6,379 | 1,403 | 4,583 | 2,306 | 17,657 |
| 2017-2018 | 364,404 | 9,232 | 1,127 | 4,183 | 1,646 | 11,931 |
Historic woody vegetation clearing in Queensland
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| Year | Remnant | Non-remnant |
|---|---|---|
| 1998–1999 | 283,404 | 134,239 |
| 1999–2000 | 423,243 | 292,228 |
| 2000–2001 | 177,356 | 282,361 |
| 2001–2002 | 245,113 | 239,530 |
| 2002–2003 | 349,447 | 202,951 |
| 2003–2004 | 245,477 | 244,595 |
| 2004–2005 | 183,275 | 178,764 |
| 2005–2006 | 212,380 | 166,292 |
| 2006–2007 | 80,508 | 168,595 |
| 2007–2008 | 58,322 | 72,815 |
| 2008–2009 | 41,806 | 63,829 |
| 2009–2010 | 24,000 | 59,750 |
| 2010-2011 | 26,309 | 65,823 |
| 2011-2012 | 34,528 | 120,524 |
| 2012-2013 | 58,026 | 202,947 |
| 2013-2014 | 99,485 | 195,204 |
| 2014-2015 | 113,501 | 184,514 |
| 2015-2016 | 132,276 | 257,320 |
| 2016-2017 | 77,690 | 278,096 |
| 2017-2018 | 74,485 | 318,038 |
Proportion of replacement landcover (clearing type) in Brigalow Belt
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| Type | Pasture | Crop | Settlement | Mining | Infrastructure | Forestry |
|---|---|---|---|---|---|---|
| 1988–1989 | 397,889 | 49,539 | 185 | 1,343 | 4,997 | 0 |
| 1989–1990 | 397,889 | 49,539 | 185 | 1,343 | 4,997 | 0 |
| 1990–1991 | 397,889 | 49,539 | 185 | 1,343 | 4,997 | 0 |
| 1991–1992 | 148,739 | 8,713 | 164 | 959 | 1,529 | 845 |
| 1992–1993 | 148,739 | 8,713 | 164 | 959 | 1,529 | 845 |
| 1993–1994 | 148,739 | 8,713 | 164 | 959 | 1,529 | 845 |
| 1994–1995 | 148,739 | 8,713 | 164 | 959 | 1,529 | 845 |
| 1995–1996 | 173,405 | 20,261 | 247 | 1,475 | 3,494 | 811 |
| 1996–1997 | 173,405 | 20,261 | 247 | 1,475 | 3,494 | 811 |
| 1997–1998 | 215,174 | 23,030 | 108 | 1,430 | 4,385 | 1,369 |
| 1998–1999 | 215,174 | 23,030 | 108 | 1,430 | 4,385 | 1,369 |
| 1999–2000 | 337,892 | 20,848 | 202 | 660 | 4,465 | 826 |
| 2000–2001 | 197,994 | 6,352 | 155 | 1,470 | 4,430 | 1,015 |
| 2001–2002 | 219,603 | 233 | 35 | 1,426 | 2,515 | 239 |
| 2002–2003 | 157,137 | 156 | 54 | 1,233 | 1,295 | 16 |
| 2003–2004 | 207,196 | 196 | 290 | 2,227 | 3,603 | 69 |
| 2004–2005 | 135,731 | 1,355 | 295 | 1,676 | 1,823 | 2,711 |
| 2005–2006 | 117,047 | 291 | 286 | 2,008 | 975 | 2,215 |
| 2006–2007 | 89,499 | 16 | 487 | 1,836 | 919 | 719 |
| 2007–2008 | 46,152 | 41 | 432 | 1,449 | 1,027 | 2,764 |
| 2008–2009 | 39,092 | 46 | 160 | 1,162 | 1,099 | 1,501 |
| 2009–2010 | 35,453 | 81 | 130 | 2,152 | 542 | 710 |
| 2010-2011 | 37,441 | 296 | 157 | 1,995 | 4,292 | 1,169 |
| 2011-2012 | 80,221 | 270 | 252 | 3,865 | 2,727 | 1,630 |
| 2012-2013 | 130,788 | 1,971 | 129 | 4,046 | 5,509 | 1,410 |
| 2013-2014 | 120,180 | 3,352 | 67 | 2,818 | 2,933 | 2,232 |
| 2014-2015 | 122,721 | 3,603 | 89 | 1,846 | 886 | 2,724 |
| 2015-2016 | 197,751 | 3,757 | 42 | 1,221 | 506 | 3,283 |
| 2016-2017 | 182,562 | 5,082 | 110 | 1,544 | 605 | 3,478 |
| 2017-2018 | 192,606 | 7,871 | 75 | 1,951 | 606 | 1,164 |
Historic woody vegetation clearing in Brigalow Belt
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| Type | Non-remnant | Remnant |
|---|---|---|
| 1998–1999 | 83,259 | 162,237 |
| 1999–2000 | 181,772 | 183,121 |
| 2000–2001 | 144,644 | 66,772 |
| 2001–2002 | 137,264 | 86,787 |
| 2002–2003 | 92,601 | 67,290 |
| 2003–2004 | 140,558 | 73,023 |
| 2004–2005 | 99,760 | 43,831 |
| 2005–2006 | 80,930 | 41,892 |
| 2006–2007 | 64,856 | 28,620 |
| 2007–2008 | 32,200 | 19,665 |
| 2008–2009 | 29,516 | 13,544 |
| 2009–2010 | 30,990 | 8,078 |
| 2010-2011 | 35,476 | 9,874 |
| 2011-2012 | 73,382 | 15,583 |
| 2012-2013 | 121,187 | 22,666 |
| 2013-2014 | 106,127 | 25,455 |
| 2014-2015 | 99,063 | 32,806 |
| 2015-2016 | 161,456 | 45,104 |
| 2016-2017 | 156,215 | 37,166 |
| 2017-2018 | 180,994 | 23,279 |
Proportion of replacement landcover (clearing type) in Cape York Peninsula
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| Type | Pasture | Crop | Settlement | Mining | Infrastructure | Forestry |
|---|---|---|---|---|---|---|
| 1988–1989 | 1,041 | 0 | 2 | 434 | 966 | 0 |
| 1989–1990 | 1,041 | 0 | 2 | 434 | 966 | 0 |
| 1990–1991 | 1,041 | 0 | 2 | 434 | 966 | 0 |
| 1991–1992 | 564 | 217 | 3 | 401 | 142 | 0 |
| 1992–1993 | 564 | 217 | 3 | 401 | 142 | 0 |
| 1993–1994 | 564 | 217 | 3 | 401 | 142 | 0 |
| 1994–1995 | 564 | 217 | 3 | 401 | 142 | 0 |
| 1995–1996 | 25 | 597 | 7 | 667 | 934 | 0 |
| 1996–1997 | 25 | 597 | 7 | 667 | 934 | 0 |
| 1997–1998 | 24 | 915 | 7 | 364 | 569 | 0 |
| 1998–1999 | 24 | 915 | 7 | 364 | 569 | 0 |
| 1999–2000 | 482 | 683 | 8 | 53 | 181 | 0 |
| 2000–2001 | 1,507 | 0 | 9 | 0 | 573 | 0 |
| 2001–2002 | 467 | 0 | 2 | 1 | 82 | 0 |
| 2002–2003 | 698 | 0 | 0 | 12 | 71 | 0 |
| 2003–2004 | 534 | 0 | 3 | 643 | 384 | 0 |
| 2004–2005 | 490 | 0 | 12 | 824 | 990 | 0 |
| 2005–2006 | 794 | 0 | 5 | 998 | 501 | 0 |
| 2006–2007 | 2,092 | 0 | 20 | 1,891 | 478 | 0 |
| 2007–2008 | 1,060 | 0 | 5 | 2,002 | 92 | 0 |
| 2008–2009 | 855 | 0 | 2 | 1,072 | 565 | 0 |
| 2009–2010 | 418 | 0 | 9 | 675 | 197 | 0 |
| 2010-2011 | 464 | 0 | 5 | 330 | 201 | 0 |
| 2011-2012 | 391 | 0 | 3 | 1,174 | 231 | 0 |
| 2012-2013 | 357 | 1 | 9 | 1,450 | 272 | 0 |
| 2013-2014 | 456 | 0 | 17 | 1,886 | 209 | 0 |
| 2014-2015 | 2,145 | 2 | 7 | 1,044 | 71 | 0 |
| 2015-2016 | 679 | 1 | 1 | 1,127 | 445 | 0 |
| 2016-2017 | 290 | 0 | 4 | 2,877 | 365 | 0 |
| 2017-2018 | 230 | 0 | 3 | 2,030 | 158 | 0 |
Historic woody vegetation clearing in Cape York Peninsula
- Chart
- Table
| Type | Non-remnant | Remnant |
|---|---|---|
| 1998–1999 | 963 | 916 |
| 1999–2000 | 774 | 633 |
| 2000–2001 | 923 | 1,166 |
| 2001–2002 | 103 | 449 |
| 2002–2003 | 119 | 662 |
| 2003–2004 | 357 | 1,207 |
| 2004–2005 | 231 | 2,085 |
| 2005–2006 | 332 | 1,966 |
| 2006–2007 | 241 | 4,240 |
| 2007–2008 | 409 | 2,750 |
| 2008–2009 | 183 | 2,311 |
| 2009–2010 | 170 | 1,129 |
| 2010-2011 | 51 | 949 |
| 2011-2012 | 212 | 1,587 |
| 2012-2013 | 293 | 1,796 |
| 2013-2014 | 381 | 2,187 |
| 2014-2015 | 511 | 2,758 |
| 2015-2016 | 261 | 1,992 |
| 2016-2017 | 770 | 2,766 |
| 2017-2018 | 1,033 | 1,388 |
Proportion of replacement landcover (clearing type) in Central Queensland Coast
- Chart
- Table
| Type | Pasture | Crop | Settlement | Mining | Infrastructure | Forestry |
|---|---|---|---|---|---|---|
| 1988–1989 | 2,535 | 693 | 32 | 0 | 972 | 144 |
| 1989–1990 | 2,535 | 693 | 32 | 0 | 972 | 144 |
| 1990–1991 | 2,535 | 693 | 32 | 0 | 972 | 144 |
| 1991–1992 | 992 | 571 | 4 | 0 | 70 | 129 |
| 1992–1993 | 992 | 571 | 4 | 0 | 70 | 129 |
| 1993–1994 | 992 | 571 | 4 | 0 | 70 | 129 |
| 1994–1995 | 992 | 571 | 4 | 0 | 70 | 129 |
| 1995–1996 | 1,203 | 3,381 | 1 | 0 | 351 | 118 |
| 1996–1997 | 1,203 | 3,381 | 1 | 0 | 351 | 118 |
| 1997–1998 | 276 | 2,101 | 0 | 2 | 82 | 214 |
| 1998–1999 | 276 | 2,101 | 0 | 2 | 82 | 214 |
| 1999–2000 | 2,681 | 1,898 | 16 | 0 | 419 | 694 |
| 2000–2001 | 2,082 | 1,040 | 2 | 2 | 247 | 149 |
| 2001–2002 | 998 | 219 | 8 | 0 | 58 | 287 |
| 2002–2003 | 1,329 | 145 | 7 | 0 | 22 | 242 |
| 2003–2004 | 3,084 | 25 | 37 | 0 | 46 | 23 |
| 2004–2005 | 1,716 | 37 | 27 | 3 | 20 | 276 |
| 2005–2006 | 2,349 | 15 | 12 | 0 | 9 | 212 |
| 2006–2007 | 1,971 | 31 | 48 | 0 | 91 | 21 |
| 2007–2008 | 1,954 | 27 | 93 | 4 | 32 | 401 |
| 2008–2009 | 705 | 10 | 43 | 3 | 1 | 278 |
| 2009–2010 | 291 | 16 | 8 | 0 | 2 | 339 |
| 2010-2011 | 266 | 6 | 23 | 1 | 9 | 449 |
| 2011-2012 | 896 | 52 | 15 | 10 | 20 | 310 |
| 2012-2013 | 1,038 | 28 | 12 | 13 | 9 | 108 |
| 2013-2014 | 1,559 | 75 | 20 | 3 | 27 | 136 |
| 2014-2015 | 1,904 | 83 | 21 | 17 | 12 | 974 |
| 2015-2016 | 2,151 | 148 | 9 | 21 | 5 | 1,849 |
| 2016-2017 | 1,487 | 41 | 7 | 8 | 16 | 200 |
| 2017-2018 | 1,115 | 89 | 3 | 13 | 8 | 325 |
Historic woody vegetation clearing in Central Queensland Coast
- Chart
- Table
| Type | Non-remnant | Remnant |
|---|---|---|
| 1998–1999 | 1,706 | 969 |
| 1999–2000 | 3,200 | 2,508 |
| 2000–2001 | 2,498 | 1,024 |
| 2001–2002 | 1,037 | 533 |
| 2002–2003 | 1,168 | 577 |
| 2003–2004 | 2,306 | 909 |
| 2004–2005 | 1,519 | 560 |
| 2005–2006 | 1,693 | 904 |
| 2006–2007 | 1,294 | 868 |
| 2007–2008 | 1,632 | 879 |
| 2008–2009 | 705 | 335 |
| 2009–2010 | 462 | 194 |
| 2010-2011 | 579 | 175 |
| 2011-2012 | 1,007 | 296 |
| 2012-2013 | 773 | 435 |
| 2013-2014 | 1,199 | 621 |
| 2014-2015 | 2,088 | 923 |
| 2015-2016 | 2,879 | 1,304 |
| 2016-2017 | 1,086 | 673 |
| 2017-2018 | 1,233 | 320 |
Proportion of replacement landcover (clearing type) in Channel Country
- Chart
- Table
| Type | Pasture | Crop | Settlement | Mining | Infrastructure | Forestry |
|---|---|---|---|---|---|---|
| 1988–1989 | 1,561 | 0 | 0 | 1 | 99 | 0 |
| 1989–1990 | 1,561 | 0 | 0 | 1 | 99 | 0 |
| 1990–1991 | 1,561 | 0 | 0 | 1 | 99 | 0 |
| 1991–1992 | 167 | 0 | 0 | 2 | 34 | 0 |
| 1992–1993 | 167 | 0 | 0 | 2 | 34 | 0 |
| 1993–1994 | 167 | 0 | 0 | 2 | 34 | 0 |
| 1994–1995 | 167 | 0 | 0 | 2 | 34 | 0 |
| 1995–1996 | 2,063 | 0 | 0 | 1 | 133 | 0 |
| 1996–1997 | 2,063 | 0 | 0 | 1 | 133 | 0 |
| 1997–1998 | 334 | 0 | 0 | 11 | 127 | 0 |
| 1998–1999 | 334 | 0 | 0 | 11 | 127 | 0 |
| 1999–2000 | 188 | 0 | 0 | 0 | 169 | 0 |
| 2000–2001 | 59 | 0 | 0 | 0 | 278 | 0 |
| 2001–2002 | 338 | 0 | 0 | 0 | 60 | 0 |
| 2002–2003 | 2,118 | 0 | 0 | 0 | 21 | 0 |
| 2003–2004 | 1,085 | 0 | 0 | 0 | 13 | 0 |
| 2004–2005 | 1,433 | 0 | 0 | 0 | 5 | 0 |
| 2005–2006 | 2,311 | 0 | 0 | 0 | 24 | 0 |
| 2006–2007 | 5,366 | 0 | 0 | 0 | 11 | 0 |
| 2007–2008 | 1,078 | 0 | 0 | 0 | 0 | 0 |
| 2008–2009 | 121 | 0 | 0 | 0 | 2 | 0 |
| 2009–2010 | 148 | 0 | 0 | 1 | 0 | 0 |
| 2010-2011 | 254 | 0 | 0 | 0 | 70 | 0 |
| 2011-2012 | 103 | 0 | 0 | 0 | 29 | 0 |
| 2012-2013 | 180 | 0 | 0 | 2 | 21 | 0 |
| 2013-2014 | 573 | 0 | 0 | 1 | 1 | 0 |
| 2014-2015 | 1,220 | 0 | 0 | 0 | 0 | 0 |
| 2015-2016 | 360 | 0 | 0 | 0 | 2 | 0 |
| 2016-2017 | 302 | 0 | 0 | 0 | 5 | 0 |
| 2017-2018 | 392 | 0 | 0 | 1 | 10 | 0 |
Historic woody vegetation clearing in Channel Country
- Chart
- Table
| Type | Non-remnant | Remnant |
|---|---|---|
| 1998–1999 | 126 | 346 |
| 1999–2000 | 14 | 343 |
| 2000–2001 | 23 | 314 |
| 2001–2002 | 1 | 397 |
| 2002–2003 | 8 | 2,131 |
| 2003–2004 | 200 | 898 |
| 2004–2005 | 909 | 529 |
| 2005–2006 | 36 | 2,299 |
| 2006–2007 | 4,683 | 694 |
| 2007–2008 | 892 | 186 |
| 2008–2009 | 0 | 123 |
| 2009–2010 | 0 | 149 |
| 2010-2011 | 14 | 310 |
| 2011-2012 | 25 | 107 |
| 2012-2013 | 56 | 147 |
| 2013-2014 | 29 | 546 |
| 2014-2015 | 5 | 1,215 |
| 2015-2016 | 170 | 192 |
| 2016-2017 | 119 | 188 |
| 2017-2018 | 18 | 385 |
Proportion of replacement landcover (clearing type) in Desert Uplands
- Chart
- Table
| Type | Pasture | Crop | Settlement | Mining | Infrastructure | Forestry |
|---|---|---|---|---|---|---|
| 1988–1989 | 45,603 | 0 | 0 | 52 | 1,049 | 0 |
| 1989–1990 | 45,603 | 0 | 0 | 52 | 1,049 | 0 |
| 1990–1991 | 45,603 | 0 | 0 | 52 | 1,049 | 0 |
| 1991–1992 | 35,510 | 0 | 0 | 7 | 303 | 0 |
| 1992–1993 | 35,510 | 0 | 0 | 7 | 303 | 0 |
| 1993–1994 | 35,510 | 0 | 0 | 7 | 303 | 0 |
| 1994–1995 | 35,510 | 0 | 0 | 7 | 303 | 0 |
| 1995–1996 | 32,652 | 0 | 3 | 1 | 599 | 0 |
| 1996–1997 | 32,652 | 0 | 3 | 1 | 599 | 0 |
| 1997–1998 | 38,768 | 0 | 0 | 53 | 1,007 | 0 |
| 1998–1999 | 38,768 | 0 | 0 | 53 | 1,007 | 0 |
| 1999–2000 | 64,043 | 0 | 0 | 2 | 1,198 | 0 |
| 2000–2001 | 57,262 | 0 | 2 | 0 | 1,279 | 0 |
| 2001–2002 | 42,514 | 0 | 0 | 0 | 399 | 0 |
| 2002–2003 | 39,055 | 0 | 0 | 0 | 214 | 0 |
| 2003–2004 | 28,719 | 70 | 0 | 0 | 766 | 0 |
| 2004–2005 | 22,771 | 3 | 0 | 0 | 171 | 0 |
| 2005–2006 | 30,661 | 0 | 0 | 0 | 22 | 0 |
| 2006–2007 | 7,398 | 0 | 0 | 0 | 29 | 0 |
| 2007–2008 | 3,064 | 0 | 0 | 14 | 158 | 0 |
| 2008–2009 | 3,199 | 0 | 0 | 5 | 69 | 0 |
| 2009–2010 | 1,976 | 0 | 0 | 24 | 43 | 0 |
| 2010-2011 | 4,299 | 0 | 1 | 53 | 93 | 0 |
| 2011-2012 | 7,979 | 0 | 1 | 65 | 395 | 0 |
| 2012-2013 | 8,368 | 1 | 0 | 59 | 101 | 0 |
| 2013-2014 | 13,932 | 1 | 0 | 16 | 48 | 0 |
| 2014-2015 | 19,136 | 1 | 0 | 1 | 17 | 0 |
| 2015-2016 | 32,026 | 26 | 1 | 0 | 17 | 0 |
| 2016-2017 | 31,135 | 1 | 0 | 4 | 67 | 0 |
| 2017-2018 | 20,951 | 0 | 0 | 0 | 133 | 0 |
Historic woody vegetation clearing in Desert Uplands
- Chart
- Table
| Type | Non-remnant | Remnant |
|---|---|---|
| 1998–1999 | 6,581 | 33,247 |
| 1999–2000 | 11,532 | 53,711 |
| 2000–2001 | 20,592 | 37,951 |
| 2001–2002 | 10,731 | 32,182 |
| 2002–2003 | 3,629 | 35,640 |
| 2003–2004 | 7,166 | 22,389 |
| 2004–2005 | 3,282 | 19,663 |
| 2005–2006 | 3,797 | 26,886 |
| 2006–2007 | 5,286 | 2,141 |
| 2007–2008 | 1,359 | 1,877 |
| 2008–2009 | 1,139 | 2,134 |
| 2009–2010 | 1,278 | 765 |
| 2010-2011 | 2,999 | 1,447 |
| 2011-2012 | 5,989 | 2,451 |
| 2012-2013 | 5,102 | 3,427 |
| 2013-2014 | 9,311 | 4,686 |
| 2014-2015 | 15,502 | 3,653 |
| 2015-2016 | 15,561 | 16,509 |
| 2016-2017 | 23,103 | 8,104 |
| 2017-2018 | 14,856 | 6,228 |
Proportion of replacement landcover (clearing type) in Einasleigh Uplands
- Chart
- Table
| Type | Pasture | Crop | Settlement | Mining | Infrastructure | Forestry |
|---|---|---|---|---|---|---|
| 1988–1989 | 4,968 | 355 | 13 | 229 | 1,505 | 0 |
| 1989–1990 | 4,968 | 355 | 13 | 229 | 1,505 | 0 |
| 1990–1991 | 4,968 | 355 | 13 | 229 | 1,505 | 0 |
| 1991–1992 | 1,047 | 1,234 | 9 | 127 | 217 | 1 |
| 1992–1993 | 1,047 | 1,234 | 9 | 127 | 217 | 1 |
| 1993–1994 | 1,047 | 1,234 | 9 | 127 | 217 | 1 |
| 1994–1995 | 1,047 | 1,234 | 9 | 127 | 217 | 1 |
| 1995–1996 | 1,955 | 1,451 | 24 | 212 | 357 | 2 |
| 1996–1997 | 1,955 | 1,451 | 24 | 212 | 357 | 2 |
| 1997–1998 | 1,526 | 593 | 1 | 78 | 452 | 52 |
| 1998–1999 | 1,526 | 593 | 1 | 78 | 452 | 52 |
| 1999–2000 | 3,618 | 435 | 3 | 16 | 1,361 | 17 |
| 2000–2001 | 2,477 | 198 | 12 | 11 | 1,231 | 2 |
| 2001–2002 | 1,644 | 56 | 9 | 24 | 1,035 | 0 |
| 2002–2003 | 991 | 28 | 1 | 38 | 622 | 0 |
| 2003–2004 | 2,707 | 13 | 45 | 19 | 741 | 0 |
| 2004–2005 | 1,960 | 16 | 2 | 82 | 280 | 165 |
| 2005–2006 | 4,724 | 19 | 14 | 109 | 294 | 481 |
| 2006–2007 | 4,436 | 2 | 1 | 50 | 355 | 85 |
| 2007–2008 | 2,991 | 3 | 6 | 68 | 263 | 0 |
| 2008–2009 | 2,414 | 1 | 16 | 23 | 212 | 0 |
| 2009–2010 | 1,112 | 15 | 1 | 13 | 122 | 0 |
| 2010-2011 | 1,076 | 5 | 2 | 15 | 289 | 0 |
| 2011-2012 | 1,042 | 60 | 0 | 24 | 113 | 0 |
| 2012-2013 | 2,753 | 134 | 4 | 56 | 228 | 0 |
| 2013-2014 | 1,498 | 132 | 2 | 36 | 93 | 2 |
| 2014-2015 | 2,163 | 242 | 1 | 39 | 55 | 0 |
| 2015-2016 | 3,918 | 76 | 0 | 14 | 38 | 0 |
| 2016-2017 | 3,168 | 671 | 1 | 41 | 193 | 0 |
| 2017-2018 | 1,716 | 439 | 3 | 29 | 109 | 99 |
Historic woody vegetation clearing in Einasleigh Uplands
- Chart
- Table
| Type | Non-remnant | Remnant |
|---|---|---|
| 1998–1999 | 561 | 2,141 |
| 1999–2000 | 1,124 | 4,326 |
| 2000–2001 | 1,211 | 2,720 |
| 2001–2002 | 439 | 2,329 |
| 2002–2003 | 165 | 1,515 |
| 2003–2004 | 641 | 2,884 |
| 2004–2005 | 285 | 2,220 |
| 2005–2006 | 630 | 5,011 |
| 2006–2007 | 1,058 | 3,871 |
| 2007–2008 | 624 | 2,707 |
| 2008–2009 | 526 | 2,140 |
| 2009–2010 | 301 | 962 |
| 2010-2011 | 106 | 1,281 |
| 2011-2012 | 164 | 1,075 |
| 2012-2013 | 1,092 | 2,083 |
| 2013-2014 | 563 | 1,200 |
| 2014-2015 | 572 | 1,928 |
| 2015-2016 | 782 | 3,264 |
| 2016-2017 | 1,148 | 2,926 |
| 2017-2018 | 977 | 1,418 |
Proportion of replacement landcover (clearing type) in Gulf Plains
- Chart
- Table
| Type | Pasture | Crop | Settlement | Mining | Infrastructure | Forestry |
|---|---|---|---|---|---|---|
| 1988–1989 | 5,248 | 0 | 0 | 0 | 1,720 | 0 |
| 1989–1990 | 5,248 | 0 | 0 | 0 | 1,720 | 0 |
| 1990–1991 | 5,248 | 0 | 0 | 0 | 1,720 | 0 |
| 1991–1992 | 1,187 | 0 | 1 | 0 | 37 | 0 |
| 1992–1993 | 1,187 | 0 | 1 | 0 | 37 | 0 |
| 1993–1994 | 1,187 | 0 | 1 | 0 | 37 | 0 |
| 1994–1995 | 1,187 | 0 | 1 | 0 | 37 | 0 |
| 1995–1996 | 3,958 | 0 | 15 | 3 | 616 | 0 |
| 1996–1997 | 3,958 | 0 | 15 | 3 | 616 | 0 |
| 1997–1998 | 885 | 0 | 1 | 0 | 861 | 0 |
| 1998–1999 | 885 | 0 | 1 | 0 | 861 | 0 |
| 1999–2000 | 756 | 0 | 0 | 0 | 908 | 0 |
| 2000–2001 | 3,209 | 0 | 0 | 0 | 772 | 0 |
| 2001–2002 | 782 | 0 | 0 | 5 | 1,493 | 0 |
| 2002–2003 | 1,131 | 4 | 0 | 0 | 1,356 | 0 |
| 2003–2004 | 4,304 | 1 | 0 | 0 | 838 | 0 |
| 2004–2005 | 10,220 | 0 | 0 | 0 | 767 | 0 |
| 2005–2006 | 4,695 | 0 | 0 | 2 | 218 | 0 |
| 2006–2007 | 4,062 | 0 | 0 | 0 | 81 | 0 |
| 2007–2008 | 1,872 | 0 | 0 | 0 | 15 | 0 |
| 2008–2009 | 759 | 0 | 0 | 0 | 47 | 0 |
| 2009–2010 | 1,667 | 0 | 1 | 6 | 138 | 0 |
| 2010-2011 | 960 | 0 | 0 | 2 | 204 | 0 |
| 2011-2012 | 2,153 | 0 | 0 | 0 | 199 | 0 |
| 2012-2013 | 1,073 | 0 | 0 | 7 | 184 | 0 |
| 2013-2014 | 3,481 | 0 | 0 | 0 | 112 | 0 |
| 2014-2015 | 18,191 | 0 | 1 | 6 | 52 | 0 |
| 2015-2016 | 18,781 | 0 | 2 | 1 | 87 | 10 |
| 2016-2017 | 4,579 | 0 | 0 | 4 | 127 | 0 |
| 2017-2018 | 3,701 | 0 | 0 | 2 | 92 | 0 |
Historic woody vegetation clearing in Gulf Plains
- Chart
- Table
| Type | Non-remnant | Remnant |
|---|---|---|
| 1998–1999 | 351 | 1,396 |
| 1999–2000 | 76 | 1,588 |
| 2000–2001 | 537 | 3,444 |
| 2001–2002 | 182 | 2,098 |
| 2002–2003 | 89 | 2,402 |
| 2003–2004 | 1,001 | 4,142 |
| 2004–2005 | 743 | 10,244 |
| 2005–2006 | 1,652 | 3,263 |
| 2006–2007 | 1,278 | 2,865 |
| 2007–2008 | 116 | 1,771 |
| 2008–2009 | 94 | 712 |
| 2009–2010 | 837 | 975 |
| 2010-2011 | 145 | 1,021 |
| 2011-2012 | 699 | 1,653 |
| 2012-2013 | 281 | 983 |
| 2013-2014 | 303 | 3,290 |
| 2014-2015 | 168 | 18,082 |
| 2015-2016 | 2,769 | 16,112 |
| 2016-2017 | 1,155 | 3,555 |
| 2017-2018 | 2,115 | 1,680 |
Proportion of replacement landcover (clearing type) in Mitchell Grass Downs
- Chart
- Table
| Type | Pasture | Crop | Settlement | Mining | Infrastructure | Forestry |
|---|---|---|---|---|---|---|
| 1988–1989 | 52,628 | 0 | 0 | 0 | 318 | 0 |
| 1989–1990 | 52,628 | 0 | 0 | 0 | 318 | 0 |
| 1990–1991 | 52,628 | 0 | 0 | 0 | 318 | 0 |
| 1991–1992 | 19,593 | 0 | 0 | 30 | 63 | 0 |
| 1992–1993 | 19,593 | 0 | 0 | 30 | 63 | 0 |
| 1993–1994 | 19,593 | 0 | 0 | 30 | 63 | 0 |
| 1994–1995 | 19,593 | 0 | 0 | 30 | 63 | 0 |
| 1995–1996 | 16,684 | 0 | 4 | 1 | 9 | 0 |
| 1996–1997 | 16,684 | 0 | 4 | 1 | 9 | 0 |
| 1997–1998 | 18,637 | 0 | 0 | 3 | 55 | 0 |
| 1998–1999 | 18,637 | 0 | 0 | 3 | 55 | 0 |
| 1999–2000 | 52,325 | 1 | 0 | 1 | 117 | 0 |
| 2000–2001 | 31,296 | 0 | 0 | 2 | 172 | 0 |
| 2001–2002 | 24,967 | 0 | 0 | 0 | 12 | 0 |
| 2002–2003 | 20,491 | 0 | 0 | 3 | 8 | 0 |
| 2003–2004 | 26,866 | 0 | 0 | 39 | 53 | 0 |
| 2004–2005 | 16,093 | 0 | 1 | 6 | 51 | 0 |
| 2005–2006 | 13,042 | 0 | 0 | 0 | 4 | 0 |
| 2006–2007 | 9,738 | 0 | 0 | 3 | 9 | 0 |
| 2007–2008 | 6,204 | 0 | 0 | 7 | 3 | 0 |
| 2008–2009 | 10,345 | 0 | 0 | 2 | 27 | 0 |
| 2009–2010 | 8,532 | 0 | 0 | 3 | 6 | 0 |
| 2010-2011 | 5,930 | 0 | 0 | 2 | 25 | 0 |
| 2011-2012 | 6,464 | 0 | 0 | 2 | 71 | 0 |
| 2012-2013 | 14,783 | 0 | 0 | 12 | 4 | 0 |
| 2013-2014 | 14,045 | 0 | 0 | 3 | 25 | 0 |
| 2014-2015 | 25,879 | 0 | 0 | 0 | 5 | 0 |
| 2015-2016 | 13,286 | 0 | 0 | 0 | 13 | 0 |
| 2016-2017 | 13,652 | 0 | 0 | 0 | 26 | 0 |
| 2017-2018 | 25,055 | 18 | 0 | 2 | 22 | 0 |
Historic woody vegetation clearing in Mitchell Grass Downs
- Chart
- Table
| Type | Non-remnant | Remnant |
|---|---|---|
| 1998–1999 | 4,368 | 14,327 |
| 1999–2000 | 11,350 | 41,094 |
| 2000–2001 | 22,138 | 9,332 |
| 2001–2002 | 12,350 | 12,629 |
| 2002–2003 | 9,762 | 10,740 |
| 2003–2004 | 12,502 | 14,456 |
| 2004–2005 | 7,444 | 8,707 |
| 2005–2006 | 5,168 | 7,878 |
| 2006–2007 | 7,498 | 2,252 |
| 2007–2008 | 4,745 | 1,469 |
| 2008–2009 | 6,112 | 4,262 |
| 2009–2010 | 4,410 | 4,131 |
| 2010-2011 | 3,421 | 2,536 |
| 2011-2012 | 4,972 | 1,565 |
| 2012-2013 | 9,151 | 5,648 |
| 2013-2014 | 6,398 | 7,675 |
| 2014-2015 | 8,383 | 17,501 |
| 2015-2016 | 7,022 | 6,277 |
| 2016-2017 | 8,944 | 4,734 |
| 2017-2018 | 17,517 | 7,580 |
Proportion of replacement landcover (clearing type) in Mulga Lands
- Chart
- Table
| Type | Pasture | Crop | Settlement | Mining | Infrastructure | Forestry |
|---|---|---|---|---|---|---|
| 1988–1989 | 121,867 | 472 | 0 | 0 | 2,638 | 0 |
| 1989–1990 | 121,867 | 472 | 0 | 0 | 2,638 | 0 |
| 1990–1991 | 121,867 | 472 | 0 | 0 | 2,638 | 0 |
| 1991–1992 | 65,447 | 22 | 0 | 1 | 443 | 0 |
| 1992–1993 | 65,447 | 22 | 0 | 1 | 443 | 0 |
| 1993–1994 | 65,447 | 22 | 0 | 1 | 443 | 0 |
| 1994–1995 | 65,447 | 22 | 0 | 1 | 443 | 0 |
| 1995–1996 | 54,650 | 482 | 0 | 4 | 1,495 | 8 |
| 1996–1997 | 54,650 | 482 | 0 | 4 | 1,495 | 8 |
| 1997–1998 | 81,580 | 704 | 3 | 0 | 1,123 | 25 |
| 1998–1999 | 81,580 | 704 | 3 | 0 | 1,123 | 25 |
| 1999–2000 | 189,331 | 295 | 2 | 0 | 1,816 | 11 |
| 2000–2001 | 122,877 | 10 | 0 | 0 | 1,337 | 0 |
| 2001–2002 | 165,545 | 5 | 0 | 0 | 289 | 0 |
| 2002–2003 | 299,232 | 1 | 0 | 0 | 247 | 0 |
| 2003–2004 | 179,539 | 3 | 0 | 0 | 152 | 0 |
| 2004–2005 | 135,557 | 0 | 0 | 0 | 740 | 7 |
| 2005–2006 | 172,654 | 0 | 0 | 0 | 40 | 1 |
| 2006–2007 | 95,484 | 0 | 17 | 0 | 41 | 0 |
| 2007–2008 | 37,427 | 0 | 0 | 0 | 128 | 0 |
| 2008–2009 | 28,334 | 0 | 11 | 8 | 77 | 0 |
| 2009–2010 | 15,120 | 0 | 2 | 1 | 76 | 0 |
| 2010-2011 | 17,452 | 0 | 8 | 0 | 1,286 | 0 |
| 2011-2012 | 28,897 | 0 | 4 | 0 | 604 | 13 |
| 2012-2013 | 69,513 | 2 | 1 | 2 | 277 | 3 |
| 2013-2014 | 107,956 | 4 | 1 | 1 | 83 | 0 |
| 2014-2015 | 65,464 | 193 | 1 | 0 | 33 | 5 |
| 2015-2016 | 82,293 | 115 | 0 | 0 | 24 | 7 |
| 2016-2017 | 72,334 | 22 | 0 | 0 | 174 | 0 |
| 2017-2018 | 105,839 | 159 | 0 | 0 | 171 | 0 |
Historic woody vegetation clearing in Mulga Lands
- Chart
- Table
| Type | Non-remnant | Remnant |
|---|---|---|
| 1998–1999 | 24,240 | 59,195 |
| 1999–2000 | 64,699 | 126,756 |
| 2000–2001 | 72,969 | 51,255 |
| 2001–2002 | 61,970 | 103,869 |
| 2002–2003 | 76,350 | 223,130 |
| 2003–2004 | 59,979 | 119,715 |
| 2004–2005 | 45,821 | 90,483 |
| 2005–2006 | 55,025 | 117,670 |
| 2006–2007 | 66,441 | 29,101 |
| 2007–2008 | 15,847 | 21,708 |
| 2008–2009 | 15,130 | 13,300 |
| 2009–2010 | 10,301 | 4,898 |
| 2010-2011 | 13,031 | 5,715 |
| 2011-2012 | 22,473 | 7,045 |
| 2012-2013 | 52,026 | 17,772 |
| 2013-2014 | 57,663 | 50,382 |
| 2014-2015 | 34,822 | 30,874 |
| 2015-2016 | 44,714 | 37,725 |
| 2016-2017 | 58,718 | 13,812 |
| 2017-2018 | 77,206 | 28,963 |
Proportion of replacement landcover (clearing type) in New England Tableland
- Chart
- Table
| Type | Pasture | Crop | Settlement | Mining | Infrastructure | Forestry |
|---|---|---|---|---|---|---|
| 1988–1989 | 5,277 | 6 | 1 | 0 | 158 | 0 |
| 1989–1990 | 5,277 | 6 | 1 | 0 | 158 | 0 |
| 1990–1991 | 5,277 | 6 | 1 | 0 | 158 | 0 |
| 1991–1992 | 2,007 | 12 | 4 | 1 | 14 | 71 |
| 1992–1993 | 2,007 | 12 | 4 | 1 | 14 | 71 |
| 1993–1994 | 2,007 | 12 | 4 | 1 | 14 | 71 |
| 1994–1995 | 2,007 | 12 | 4 | 1 | 14 | 71 |
| 1995–1996 | 3,120 | 0 | 0 | 2 | 6 | 123 |
| 1996–1997 | 3,120 | 0 | 0 | 2 | 6 | 123 |
| 1997–1998 | 2,816 | 0 | 0 | 0 | 41 | 165 |
| 1998–1999 | 2,816 | 0 | 0 | 0 | 41 | 165 |
| 1999–2000 | 2,745 | 8 | 0 | 0 | 49 | 102 |
| 2000–2001 | 1,331 | 15 | 1 | 6 | 26 | 27 |
| 2001–2002 | 1,214 | 13 | 0 | 0 | 1 | 1 |
| 2002–2003 | 4,410 | 0 | 0 | 2 | 0 | 0 |
| 2003–2004 | 3,078 | 10 | 4 | 0 | 40 | 0 |
| 2004–2005 | 1,890 | 2 | 1 | 0 | 7 | 98 |
| 2005–2006 | 4,018 | 0 | 1 | 8 | 3 | 84 |
| 2006–2007 | 2,165 | 0 | 3 | 6 | 19 | 86 |
| 2007–2008 | 2,872 | 0 | 13 | 17 | 65 | 189 |
| 2008–2009 | 1,617 | 2 | 3 | 4 | 15 | 86 |
| 2009–2010 | 1,183 | 0 | 0 | 1 | 1 | 112 |
| 2010-2011 | 1,245 | 3 | 2 | 4 | 9 | 75 |
| 2011-2012 | 2,425 | 4 | 3 | 6 | 27 | 92 |
| 2012-2013 | 1,571 | 0 | 0 | 5 | 29 | 141 |
| 2013-2014 | 1,149 | 1 | 4 | 7 | 1 | 118 |
| 2014-2015 | 4,147 | 18 | 2 | 17 | 8 | 122 |
| 2015-2016 | 2,480 | 1 | 0 | 2 | 9 | 42 |
| 2016-2017 | 3,596 | 10 | 2 | 1 | 38 | 71 |
| 2017-2018 | 2,833 | 30 | 0 | 2 | 26 | 77 |
Historic woody vegetation clearing in New England Tableland
- Chart
- Table
| Type | Non-remnant | Remnant |
|---|---|---|
| 1998–1999 | 1,380 | 1,642 |
| 1999–2000 | 1,816 | 1,088 |
| 2000–2001 | 1,240 | 166 |
| 2001–2002 | 962 | 267 |
| 2002–2003 | 3,421 | 991 |
| 2003–2004 | 2,514 | 618 |
| 2004–2005 | 1,733 | 265 |
| 2005–2006 | 3,788 | 326 |
| 2006–2007 | 1,703 | 576 |
| 2007–2008 | 2,046 | 1,110 |
| 2008–2009 | 1,399 | 328 |
| 2009–2010 | 1,019 | 278 |
| 2010-2011 | 938 | 400 |
| 2011-2012 | 1,994 | 563 |
| 2012-2013 | 1,432 | 314 |
| 2013-2014 | 933 | 347 |
| 2014-2015 | 3,358 | 956 |
| 2015-2016 | 2,109 | 425 |
| 2016-2017 | 3,210 | 508 |
| 2017-2018 | 2,501 | 467 |
Proportion of replacement landcover (clearing type) in Northwest Highlands
- Chart
- Table
| Type | Pasture | Crop | Settlement | Mining | Infrastructure | Forestry |
|---|---|---|---|---|---|---|
| 1988–1989 | 29 | 0 | 0 | 3 | 121 | 0 |
| 1989–1990 | 29 | 0 | 0 | 3 | 121 | 0 |
| 1990–1991 | 29 | 0 | 0 | 3 | 121 | 0 |
| 1991–1992 | 41 | 0 | 0 | 0 | 12 | 0 |
| 1992–1993 | 41 | 0 | 0 | 0 | 12 | 0 |
| 1993–1994 | 41 | 0 | 0 | 0 | 12 | 0 |
| 1994–1995 | 41 | 0 | 0 | 0 | 12 | 0 |
| 1995–1996 | 349 | 0 | 0 | 44 | 144 | 0 |
| 1996–1997 | 349 | 0 | 0 | 44 | 144 | 0 |
| 1997–1998 | 158 | 0 | 0 | 252 | 456 | 0 |
| 1998–1999 | 158 | 0 | 0 | 252 | 456 | 0 |
| 1999–2000 | 310 | 0 | 0 | 208 | 73 | 0 |
| 2000–2001 | 293 | 0 | 0 | 189 | 70 | 0 |
| 2001–2002 | 344 | 0 | 0 | 0 | 7 | 0 |
| 2002–2003 | 224 | 0 | 0 | 4 | 12 | 0 |
| 2003–2004 | 131 | 0 | 4 | 50 | 57 | 0 |
| 2004–2005 | 82 | 0 | 1 | 4 | 115 | 0 |
| 2005–2006 | 194 | 0 | 0 | 46 | 64 | 0 |
| 2006–2007 | 304 | 0 | 0 | 187 | 10 | 0 |
| 2007–2008 | 59 | 0 | 6 | 45 | 2 | 0 |
| 2008–2009 | 91 | 0 | 2 | 4 | 0 | 0 |
| 2009–2010 | 49 | 0 | 0 | 34 | 0 | 0 |
| 2010-2011 | 21 | 0 | 3 | 140 | 8 | 0 |
| 2011-2012 | 58 | 0 | 0 | 185 | 7 | 0 |
| 2012-2013 | 96 | 0 | 0 | 181 | 21 | 0 |
| 2013-2014 | 103 | 0 | 0 | 87 | 3 | 0 |
| 2014-2015 | 102 | 0 | 0 | 46 | 0 | 0 |
| 2015-2016 | 185 | 0 | 0 | 15 | 1 | 0 |
| 2016-2017 | 161 | 0 | 0 | 14 | 30 | 0 |
| 2017-2018 | 59 | 0 | 0 | 12 | 4 | 1 |
Historic woody vegetation clearing in Northwest Highlands
- Chart
- Table
| Type | Non-remnant | Remnant |
|---|---|---|
| 1998–1999 | 27 | 839 |
| 1999–2000 | 41 | 550 |
| 2000–2001 | 373 | 179 |
| 2001–2002 | 278 | 73 |
| 2002–2003 | 37 | 203 |
| 2003–2004 | 9 | 233 |
| 2004–2005 | 25 | 177 |
| 2005–2006 | 17 | 287 |
| 2006–2007 | 30 | 471 |
| 2007–2008 | 13 | 99 |
| 2008–2009 | 2 | 95 |
| 2009–2010 | 14 | 69 |
| 2010-2011 | 27 | 145 |
| 2011-2012 | 29 | 221 |
| 2012-2013 | 8 | 290 |
| 2013-2014 | 25 | 168 |
| 2014-2015 | 6 | 142 |
| 2015-2016 | 10 | 191 |
| 2016-2017 | 3 | 202 |
| 2017-2018 | 14 | 62 |
Proportion of replacement landcover (clearing type) in Southeast Queensland
- Chart
- Table
| Type | Pasture | Crop | Settlement | Mining | Infrastructure | Forestry |
|---|---|---|---|---|---|---|
| 1988–1989 | 6,953 | 2,266 | 2,721 | 227 | 849 | 2,813 |
| 1989–1990 | 6,953 | 2,266 | 2,721 | 227 | 849 | 2,813 |
| 1990–1991 | 6,953 | 2,266 | 2,721 | 227 | 849 | 2,813 |
| 1991–1992 | 3,901 | 1,254 | 2,206 | 167 | 274 | 3,787 |
| 1992–1993 | 3,901 | 1,254 | 2,206 | 167 | 274 | 3,787 |
| 1993–1994 | 3,901 | 1,254 | 2,206 | 167 | 274 | 3,787 |
| 1994–1995 | 3,901 | 1,254 | 2,206 | 167 | 274 | 3,787 |
| 1995–1996 | 6,154 | 2,757 | 2,155 | 291 | 328 | 3,416 |
| 1996–1997 | 6,154 | 2,757 | 2,155 | 291 | 328 | 3,416 |
| 1997–1998 | 5,858 | 1,755 | 1,395 | 230 | 1,032 | 5,355 |
| 1998–1999 | 5,858 | 1,755 | 1,395 | 230 | 1,032 | 5,355 |
| 1999–2000 | 12,512 | 1,107 | 1,657 | 374 | 947 | 5,272 |
| 2000–2001 | 8,754 | 439 | 1,353 | 243 | 510 | 6,401 |
| 2001–2002 | 8,312 | 147 | 1,687 | 256 | 828 | 5,496 |
| 2002–2003 | 9,218 | 159 | 3,481 | 239 | 504 | 5,083 |
| 2003–2004 | 14,218 | 58 | 3,117 | 384 | 309 | 3,219 |
| 2004–2005 | 12,714 | 57 | 1,353 | 416 | 373 | 5,418 |
| 2005–2006 | 7,513 | 28 | 1,090 | 366 | 235 | 6,443 |
| 2006–2007 | 9,819 | 72 | 891 | 294 | 795 | 5,554 |
| 2007–2008 | 7,838 | 77 | 1,784 | 297 | 852 | 5,223 |
| 2008–2009 | 4,998 | 24 | 1,653 | 154 | 464 | 3,838 |
| 2009–2010 | 4,114 | 29 | 1,246 | 215 | 660 | 5,792 |
| 2010-2011 | 3,887 | 122 | 1,180 | 196 | 519 | 4,775 |
| 2011-2012 | 4,442 | 76 | 1,083 | 237 | 719 | 4,046 |
| 2012-2013 | 5,287 | 119 | 888 | 228 | 520 | 5,823 |
| 2013-2014 | 5,816 | 434 | 991 | 201 | 581 | 5,869 |
| 2014-2015 | 7,520 | 635 | 1,494 | 229 | 232 | 11,185 |
| 2015-2016 | 9,249 | 305 | 1,080 | 105 | 349 | 9,943 |
| 2016-2017 | 9,810 | 489 | 1,248 | 74 | 638 | 12,128 |
| 2017-2018 | 9,603 | 549 | 1,026 | 127 | 294 | 9,200 |
Historic woody vegetation clearing in Southeast Queensland
- Chart
- Table
| Type | Non-remnant | Remnant |
|---|---|---|
| 1998–1999 | 10,103 | 5,522 |
| 1999–2000 | 15,066 | 6,803 |
| 2000–2001 | 14,857 | 2,843 |
| 2001–2002 | 13,485 | 3,241 |
| 2002–2003 | 14,876 | 3,808 |
| 2003–2004 | 16,633 | 4,672 |
| 2004–2005 | 16,089 | 4,242 |
| 2005–2006 | 12,278 | 3,397 |
| 2006–2007 | 13,057 | 4,368 |
| 2007–2008 | 12,270 | 3,801 |
| 2008–2009 | 8,745 | 2,386 |
| 2009–2010 | 9,811 | 2,245 |
| 2010-2011 | 8,459 | 2,220 |
| 2011-2012 | 8,500 | 2,103 |
| 2012-2013 | 10,652 | 2,213 |
| 2013-2014 | 11,290 | 2,602 |
| 2014-2015 | 18,900 | 2,395 |
| 2015-2016 | 18,088 | 2,943 |
| 2016-2017 | 21,681 | 2,706 |
| 2017-2018 | 18,315 | 2,484 |
Proportion of replacement landcover (clearing type) in Wet Tropics
- Chart
- Table
| Type | Pasture | Crop | Settlement | Mining | Infrastructure | Forestry |
|---|---|---|---|---|---|---|
| 1988–1989 | 789 | 2,216 | 84 | 4 | 197 | 323 |
| 1989–1990 | 789 | 2,216 | 84 | 4 | 197 | 323 |
| 1990–1991 | 789 | 2,216 | 84 | 4 | 197 | 323 |
| 1991–1992 | 209 | 2,777 | 60 | 0 | 26 | 248 |
| 1992–1993 | 209 | 2,777 | 60 | 0 | 26 | 248 |
| 1993–1994 | 209 | 2,777 | 60 | 0 | 26 | 248 |
| 1994–1995 | 209 | 2,777 | 60 | 0 | 26 | 248 |
| 1995–1996 | 356 | 1,649 | 90 | 1 | 33 | 72 |
| 1996–1997 | 356 | 1,649 | 90 | 1 | 33 | 72 |
| 1997–1998 | 574 | 472 | 27 | 0 | 84 | 44 |
| 1998–1999 | 574 | 472 | 27 | 0 | 84 | 44 |
| 1999–2000 | 1,081 | 128 | 39 | 0 | 155 | 83 |
| 2000–2001 | 375 | 46 | 23 | 0 | 44 | 58 |
| 2001–2002 | 654 | 216 | 21 | 0 | 24 | 72 |
| 2002–2003 | 679 | 156 | 20 | 0 | 44 | 185 |
| 2003–2004 | 610 | 12 | 58 | 1 | 20 | 359 |
| 2004–2005 | 557 | 2 | 72 | 26 | 23 | 512 |
| 2005–2006 | 743 | 10 | 78 | 7 | 147 | 562 |
| 2006–2007 | 955 | 60 | 56 | 2 | 22 | 516 |
| 2007–2008 | 468 | 3 | 87 | 27 | 8 | 369 |
| 2008–2009 | 296 | 1 | 21 | 1 | 10 | 85 |
| 2009–2010 | 139 | 19 | 6 | 0 | 30 | 90 |
| 2010-2011 | 243 | 14 | 20 | 0 | 48 | 488 |
| 2011-2012 | 254 | 22 | 6 | 25 | 20 | 1,030 |
| 2012-2013 | 276 | 41 | 18 | 12 | 26 | 773 |
| 2013-2014 | 457 | 41 | 26 | 5 | 14 | 765 |
| 2014-2015 | 378 | 155 | 36 | 4 | 21 | 810 |
| 2015-2016 | 335 | 35 | 9 | 0 | 41 | 1,317 |
| 2016-2017 | 382 | 63 | 31 | 16 | 22 | 1,780 |
| 2017-2018 | 304 | 77 | 17 | 14 | 13 | 1,065 |
Historic woody vegetation clearing in Wet Tropics
- Chart
- Table
| Type | Non-remnant | Remnant |
|---|---|---|
| 1998–1999 | 574 | 627 |
| 1999–2000 | 764 | 722 |
| 2000–2001 | 356 | 190 |
| 2001–2002 | 728 | 259 |
| 2002–2003 | 726 | 358 |
| 2003–2004 | 729 | 331 |
| 2004–2005 | 923 | 269 |
| 2005–2006 | 946 | 601 |
| 2006–2007 | 1,170 | 441 |
| 2007–2008 | 662 | 300 |
| 2008–2009 | 278 | 136 |
| 2009–2010 | 157 | 127 |
| 2010-2011 | 577 | 236 |
| 2011-2012 | 1,078 | 279 |
| 2012-2013 | 894 | 252 |
| 2013-2014 | 982 | 326 |
| 2014-2015 | 1,136 | 268 |
| 2015-2016 | 1,499 | 238 |
| 2016-2017 | 1,944 | 350 |
| 2017-2018 | 1,259 | 231 |
Download data from Queensland Government Open Data Portal
Metadata
Reporting on native vegetation clearing types, using information from the Statewide Landcover and Trees Study (SLATS). SLATS monitors Queensland's forests and woodlands to assess vegetation extent and clearing activities reported. SLATS data between the first mapping period of 1988–91 and up to the most recent 2017–18 mapping period.