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Land Use and Land Cover for Hobart and Launceston Index of indicators

Indicator description

Why is it indicative

Data

Acknowledgment

Indicator description

Up to 30 land cover classes were identified from Landsat satellite remote sensing data from images captured at September 1999 for the south-east and November 2000 for the north (descriptions of the classes can be downloaded. Classification statistics were prepared for the statistical divisions of greater Hobart and greater Launceston. The 30 classes were grouped into land use classes, natural land cover classes and other classes. Woody vegetation change analysis was undertaken for Landsat data acquired for the previous SoE report (around 1994) to the current SoE report. The results, available as a map of woody vegetation change, are also presented for Hobart and Launceston statistical divisions.

Why is it indicative

The land cover classification assists in providing an indication of the major land-related issues occurring within each statistical division. Comparisons over time will assist in identifying the pattern of land use change and intensification.

Data

Land use in Greater Hobart and Launceston

Land use classification of Greater Hobart

Land use

area (ha)

% total

Airports/aerodromes

634

0.7

Aquaculture

3

0.0

Biodiversity

549

0.6

Commercial services

172

0.2

Cropping

61

0.1

Defence

84

0.1

Defence facilities

0

0.0

Effluent pond

11

0.0

Electricity generation/transmission

106

0.1

Environmental

2

0.0

Estuary/coastal waters

14

0.0

Estuary/coastal waters - conservation

21

0.0

Grazing modified pastures

16,491

18.4

Grazing natural vegetation

10

0.0

Habitat/species management area

3

0.0

Intensive horticulture

37

0.0

Irrigated cropping

455

0.5

Irrigated modified pastures

117

0.1

Irrigated perennial horticulture

331

0.4

Irrigated seasonal horticulture

87

0.1

Irrigated vine fruits

46

0.1

Landfill

125

0.1

Managed resource protection

692

0.8

Manufacturing and industrial

671

0.8

Marsh/wetland

547

0.6

Marsh/wetland - conservation

46

0.1

Mines

271

0.3

Mining

280

0.3

Natural feature protection

226

0.3

Navigation and communication

1

0.0

Other conserved area

12,419

13.9

Plantation forestry

1,404

1.6

Ports and water transport

104

0.1

Poultry

3

0.0

Production forestry

1,121

1.3

Protected landscape

3,088

3.5

Public services

467

0.5

Quarries

36

0.0

Railways

16

0.0

Recreation and culture

1,235

1.4

Remnant native cover

26,738

29.9

Research facilities

20

0.0

Reservoir

147

0.2

River

51

0.1

River - conservation

93

0.1

Roads

216

0.2

Rural residential

10,265

11.5

Services

675

0.8

Sewage

30

0.0

Strict nature reserves

415

0.5

Surface water supply

193

0.2

Transport and communication

4

0.0

Urban residential

8,586

9.6

Utilities

3

0.0

Waste treatment and disposal

18

0.0

Water storage and treatment

16

0.0

Totals

89,457

100.0

Source: Andrew Drennen


Land use classification of Launceston

Land use

area (ha)

% total

Airports/aerodromes

184

0.2

Biodiversity

109

0.1

Commercial services

326

0.4

Effluent pond

10

0.0

Electricity generation/transmission

399

0.5

Estuary/coastal waters - conservation

0

0.0

Estuary/coastal waters - intensive use

0

0.0

Grazing modified pastures

36,131

45.0

Grazing natural vegetation

6,261

7.8

Habitat/species management area

993

1.2

Intensive horticulture

3

0.0

Irrigated cropping

1,190

1.5

Irrigated modified pastures

22

0.0

Irrigated perennial horticulture

549

0.7

Irrigated vegetables and herbs

18

0.0

Irrigated vine fruits

181

0.2

Landfill

166

0.2

Managed resource protection

13

0.0

Manufacturing and industrial

1,303

1.6

Marsh/wetland

254

0.3

Marsh/wetland - conservation

116

0.1

Mining

434

0.5

National park

857

1.1

Native/exotic pasture mosaic

82

0.1

Natural feature protection

434

0.5

Navigation and communication

6

0.0

Other conserved area

1,300

1.6

Plantation forestry

668

0.8

Ports and water transport

94

0.1

Production forestry

2,988

3.7

Protected landscape

283

0.4

Public services

375

0.5

Quarries

4

0.0

Railways

138

0.2

Recreation and culture

1,225

1.5

Remnant native cover

11,676

14.5

Reservoir

230

0.3

Residential

134

0.2

River

177

0.2

River - conservation

43

0.1

Roads

186

0.2

Rural residential

5,780

7.2

Services

197

0.2

Sewage

44

0.1

Surface water supply

1

0.0

Urban residential

4,603

5.7

Utilities

48

0.1

Waste treatment and disposal

64

0.1

Water storage and treatment

5

0.0

Totals

80,303

100.0

Source: Andrew Drennen


Landcover classification of Greater Hobart and Launceston

According to this classification, urban and suburban land cover occupies 7.9% of greater Hobart and 9% of greater Launceston. 'Modified' land cover classes that can be identified from Landsat data represent 33.5% of greater Hobart and 45% of greater Launceston. 'Natural' land cover classes account for 61.9% of greater Hobart and 49.6% of greater Launceston. The difference between Hobart and Launceston is due in part to the greater significance of agriculture, pasture and forestry activity around Launceston. The Mt Wellington Park and the Meehan Range in Greater Hobart also occupy a significant area of the greater Hobart statistical division, contributing to the overall proportion of 'natural' land cover.

Greater Hobart

Greater Launceston

 

total area
(ha)

% Greater
Hobart

total area
(ha)

% Greater
Launceston

Modified land cover classes

Agriculture

3,438.3

2.5

7,219.9

9.0

Forestry Activity

5,917.8

4.4

5,119.8

6.4

Pasture

25,250.6

18.6

16,362.5

20.4

Regrowth

205.1

0.2

167.0

0.2

Suburbs

9,346.0

6.9

5,892.8

7.3

Urban

1,336.1

1.0

1,378.7

1.7

subtotal

45,493.9

33.5

36,140.7

45.0

Natural land cover classes

Alpine

617.9

0.5

7.4

0.0

Alpine scrub

220.9

0.2

-

-

Buttongrass

75.8

0.1

1,121.3

1.4

Coastal scrub

3,286.3

2.4

1,809.4

2.3

Eucalptus coccifera

1,025.5

0.8

1.1

0.0

Eucalptus delegatensis

2,601.3

1.9

781.6

1.0

Dry forest

28,458.6

20.9

14,517.9

18.1

Dry forest (wet)

2,503.1

1.8

911.5

1.1

Grassland

3,294.8

2.4

3,361.2

4.2

Rainforest

926.7

0.7

101.4

0.1

Saltmarsh

2,376.7

1.7

1,088.2

1.4

Scrub/heath

8,221.6

6.0

9,258.4

11.5

Eucalptus tenuiramis

-

-

-

-

Wet forest

5,255.8

3.9

2,190.1

2.7

Wet forest (dry)

2,581.6

1.9

369.7

0.5

Wet scrub

985.1

0.7

793.8

1.0

Wetland

969.4

0.7

1,240.6

1.5

Woodland

20,725.9

15.2

2,299.8

2.9

subtotal

84,126.8

61.9

39,853.2

49.6

Other land cover classes

Cloud

367.0

0.3

790.4

1.0

Shadow

121.5

0.1

13.1

0.0

Water

269.3

0.2

21.7

0.0

Shallow water

96.3

0.1

133.0

0.2

Bare

5,007.6

3.7

3,264.7

4.1

Sand/quartz

427.9

0.3

53.4

0.1

subtotal

6,289.4

4.6

4,276.3

5.3

total

135,910.1

100.0

80,270.1

100.0

Vegetation change

The analysis of woody vegetation change for greater Hobart compares vegetation cover from Landsat satellite images from ~1994 to 1999. The results identify areas that have woody vegetation cover at both dates, areas that have gained woody vegetation cover, and areas that have lost woody vegetation cover. The on-the-ground context in which these changes are occurring is all important: not all vegetation loss may be 'bad' for the environment and not all gains may necessarily be 'good'.

The logging of a plantation such as at Seven Mile Beach, for example, is indicated as vegetation loss even though the environmental consequences of this harvesting on an established plantation are comparatively neutral. Some change may simply be a part of natural cycles, such as regrowth following bushfire. Other limitations of the change detection relate to what it omits. In particular, non-forest vegetation, may have high conservation importance yet the loss of such vegetation can not be identified in change detection from Landsat remote sensing.

Scale and resolution is also important: Landsat data has a resolution of about 25 m2 so changes that are finer than this resolution may not be evident but may be just as critical for priority vegetation communities and habitat. The slope, elevation and visibility of vegetation change are also an important part of the on-the-ground context of change. For example, the vegetation change indicated over this period for Mt Nelson and Tolmans Hill does not adequately portray impacts on landscape quality on hillslopes [link the words landscape quality to the issue report on 'landscape quality'].

With noting these issues and limitations, the change detection indicates the following:

  • An overall perspective of increasing fragmentation of vegetation in greater Hobart.
     
  • Vegetation clearance for housing development at Seven Mile Beach, Tolmans Hill, Mt Nelson, Kingston, Blackmans Bay, and Cremorne.
     
  • Plantation regrowth at Seven Mile Beach.
     
  • Forestry activity near Magra, north of New Norfolk, and on the eastern side of greater Hobart staistical division indicated by land cover patterns of woody vegetation increase and decrease.
     
  • Evidence of the role of parks and reserves in preserving the landscape from land cover change shown by Mt Wellington Park and the Domain.
     
  • Significant land cover activity in a belt extending north of Hobart from Bridgewater to Forcett.
     
  • An unknown percentage of vegetation loss includes the clearance of vegetation of conservation priority. Comparisons with TASVEG data and with conservation priorities for forest and non-forest components identified by CARSAG would assist in understanding the conservation significance of the changes identified.
     

Acknowledgment

Adapted from Key Land Indicator L 2.4 and 2.5 (Hamblin 1998)

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Last Modified: 14 Dec 2006
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