Biodiversity
Theme commentary
Steven Cork, Land & Water Australia and CSIRO
Paul Sattler, Paul Sattler Eco-consulting Pty Ltd
Jason Alexandra, Alexandra and Associates Pty Ltd
prepared for the 2006 Australian State of the Environment Committee, 2006
Utilisation and value of biodiversity
Biodiversity is enormously valuable in its own right, in economic and cultural terms, and in the provision of market and non-market ecosystem goods and services (see Williams et al 2001; PMSEIC 2002; Millennium Ecosystem Assessment 2003; CSIRO 2005; BDAC 2005). Biodiversity underpins the life support systems that we depend upon. When it is lost, ecosystems break down and essential ecosystem services falter, causing economical and cultural impoverishment of societies. This can be seen today in some of the worn-out pastoral areas or salinity-affected agricultural regions of Australia.
Biodiversity supplies a pool of biological and genetic resources that contribute to resilience in ecological, social and economic systems. In ecological systems, biodiversity provides ‘insurance’ against change by maintaining a range of species that perform the same or similar functions but that could adapt differently to changing conditions (Folke et al 2002). Biodiversity’s contribution to social and economic resilience is exemplified by disease resistant crops and new crop plants, such as wattle seeds for protein, plantation eucalypts, new medicines, insecticides and other products (Folke et al 2002; Elmqvist 2003; Simpson and Chudleigh 2003; Resilience Alliance 2006).
The SoE 2001 biodiversity theme report mentioned efforts to estimate the economic value of biodiversity and ecosystem services (Williams et al 2001). Such approaches are rarely integrated into decision-making processes. This is a major deficiency in current investment in biodiversity management, especially because the size of this investment is partly determined by the balance between poorly defined (and typically longer-term) benefits from conservation and well-defined (but typically shorter-term) benefits from land conversion.
The indicators of utilisation and value of biodiversity for which data have been collected capture only a small part of the value and utility of biodiversity to Australians. Native species are the basis of the wild-catch fisheries , some aquaculture , native timber harvesting and many traditional food, fibre, art and craft material and medicines used by Indigenous peoples, particularly in more remote parts of Australia. The latter have considerable cultural and economic value that is rarely quantified or considered in decision-making (see Whitehead 2002). Similarly, there is little information on the economic value of biodiversity for medicine and other biological compounds , although there is increasing investment in the bioprospecting of Australia’s biological resources (see Bioprospect Limited 2006). The ongoing commercial harvesting of species like kangaroos (Table 3) and some marine fisheries such as the Western Australian Rock Lobster (Genus species) demonstrate the essential role of biological research and population monitoring in the management of species harvested commercially.
| Year | Macropus rufus (Red Kangaroo) |
M. giganteus (Eastern Grey) |
M. fuliginosus (Western Grey) |
M. robustus (Euro / Wallaroo) |
M. parryi (Whiptail Wallaby) |
Macropus rufogriseus (Bennetts Wallaby) |
Thylogale billardierii (Tasmanian Pademelon |
Total |
|---|---|---|---|---|---|---|---|---|
| 1991 | 1 365 716 | 1 270 877 | 158 213 | 113 791 | 4 226 | 2 912 823 | ||
| 1992 | 1 308 140 | 1 183 681 | 182 814 | 139 943 | 2 071 | 2 816 649 | ||
| 1993 | 1 319 693 | 1 273 922 | 207 397 | 172 449 | 2 737 | 2 976 198 | ||
| 1994 | 1 425 553 | 1 328 561 | 311 504 | 225 644 | 1 965 | 3 293 227 | ||
| 1995 | 1 435 614 | 1 306 747 | 301 405 | 214 916 | 1 766 | 3 260 448 | ||
| 1996 | 1 447 698 | 1 066 364 | 353 650 | 232 502 | 909 | 3 101 123 | ||
| 1997 | 1 171 300 | 704 137 | 264 656 | 148 803 | 791 | 2 289 687 | ||
| 1998 | 1 344 214 | 800 707 | 242 630 | 204 789 | 217 | 149 | 70 | 2 592 776 |
| 1999 | 1 278 469 | 925 946 | 240 727 | 152 782 | 1 279 | 421 | 515 | 2 600 139 |
| 2000 | 1 173 242 | 1 106 208 | 227 552 | 238 439 | 357 | 584 | 20 | 2 746 402 |
| 2001 | 1 364 682 | 1 438 280 | 283 332 | 296 805 | 256 | 6 884 | 2 020 | 3 392 259 |
| 2002 | 1 500 588 | 1 810 426 | 330 372 | 257 140 | 190 | 4 392 | 2 169 | 3 905 277 |
| 2003 | 1 121 724 | 1 758 173 | 246 672 | 347 914 | 0 | 0 | 0 | 3 474 483 |
| 2005 Commercial kangaroo harvest quotas | ||||||||
| NSW | 445 300 | 550 820 | 143 963 | 35 616 | 0 | 0 | 0 | 1 175 699 |
| Qld | 472 332 | 1 081 340 | 0 | 338 279 | 0 | 0 | 0 | 1 891 951 |
| SA | 237 600 | 0 | 97 900 | 76 400 | 0 | 0 | 0 | 411 900 |
| WA | 250 000 | 0 | 180 000 | 0 | 0 | 0 | 0 | 430 000 |
| Total | 1 405 232 | 1 632 160 | 421 863 | 450 295 | 0 | 0 | 0 | 3 909 550 |
Source: DEH (2004a)
Nature-based tourism provides great benefit to Australia’s economy. It is recognised internationally that it is difficult for the tourism industry, which is dispersed and consists mainly of small to medium enterprises, to invest sufficiently to protect the natural resources that support this tourism industry (Keller 2005). Although few data are available, the same is probably true in Australia. Wider monitoring of pressure from tourism and the effectiveness of management responses, particularly in ecological terms on protected areas, is needed.
