


Publications
Andreas Glanznig
June 1995
Since European settlement native vegetation cover in Tasmania has decreased by some 1,768,600 ha from 4,878,000 ha to 3,109,400 ha (AUSLIG 1990). Changes in vegetation cover for particular vegetation types compiled from information supplied by the Tasmanian Department of Parks, Wildlife and Heritage are summarised in Table 8 below.
Table 8 Change in vegetation cover in Tasmania since European settlement(12)
| Vegetation type | Pre-European (ha) | Present (ha) | Change (ha) |
|---|---|---|---|
| Native vegetation | 4,878 000(1) | 3,109,400(1) | 1,768,600 |
| Rainforest | >1,000,000 | 754,268(2) | >245,732 |
| Wet Eucalypt forest | 1,272,750(3) | 1,018,200(3) | 254,550 |
| Dry Eucalypt forest | 2,853,250(4) | 1,439,900(4) | 1,413,350 |
| Blackwood swamp forest | 17,040(5) | 1,040(6) | 16,000 |
| Grassland | 59,369(7) | No data | |
| Coastal heathland | 425,754(8) | 225,754(7) | 200,000 |
| Alpine | 115,000(9) | 113,500(10) | 1,500 |
| Saltmarsh | 4,000(7) | 3,300(11) | 700 |
Significant clearance of native vegetation, mainly for agricultural purposes, has occurred in the last two decades. Analysis of Landsat imagery from 1972 to 1980 has shown that at least 74 000 ha of native vegetation were converted to pasture. Of this total at least 69 500 ha were previously covered by dry eucalypt forest, the remaining being heath country. In addition, losses to pine plantations amounted to about 24 000 ha and hydroelectric impoundments covered 51 800 ha. These losses equate to a total of 2.3 per cent of the area of mainland Tasmania, a total area of about 150 000 ha at an average of about 19 000 ha per year (Kirkpatrick and Dickinson 1982, p.187).

Most of the conversion of forest to pasture occurred along the margins of already cleared land, or in remnant patches of native vegetation within already cleared land. Clearing was concentrated in areas readily accessible to the major woodchip export ports and was undertaken almost totally in dry eucalypt forests with grass, bracken or sclerophyll scrub understorey. The recent loss of habitat due to vegetation clearance or inundation has occurred mostly in east and northwest Tasmania (Kirkpatrick and Dickinson 1982).
In the period 1980 to 1988, 48 000 ha of vegetation were cleared or 6 000 ha per year. A breakdown into vegetation types is provided in Table 9 below.
The rate of clearance decreased by about 40 per cent between the periods 1972-80 and 1980-88. This decline could possibly reflect the reduced availability of natural vegetation and deep soils on relatively flat private land (Kirkpatrick 1991 p.11).
Table 9 Land clearance in Tasmania by vegetation type, 1980-88
| Vegetation type | per cent cleared per year (1980 base) | area 1988 ('000 ha) |
|---|---|---|
| Sclerophyll forest | 0.77 | 186 |
| Grassy woodland | 0.74 | 50 |
| Inland E. tenuiramis dry forest | 0.66 | 60 |
| Inland grassy forest | 0.65 | 175 |
| Coastal grassy forest | 0.42 | 192 |
| Swamp forest | 0.26 | 9 |
| Grassland | 0.20 | 59 |
| E. sieberi dry forest | 0.09 | 48 |
| E. obliqua wet forest | 0.08 | 154 |
| Rainforest | 0.08 | 539 |
| Scrub | 0.04 | 116 |
| E.delegatenis forest | 0.03 | 308 |
| E.obliqua tall forest | 0.03 | 479 |
| Buttongrass moor | 0.03 | 1145 |
| Heath | 0.03 | 200 |
