Acacia mearnsii

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Acacia mearnsii
Acacia mearnsii blossoms.jpg
Scientific classification
Kingdom:
Plantae
(unranked):
Angiosperms
(unranked):
Eudicots
(unranked):
Rosids
Order:
Fabales
Family:
Fabaceae
Genus:
Acacia
Species:
A. mearnsii
Binomial name
Acacia mearnsii
Synonyms
  • Acacia decurrens auct. non Willd.
  • Acacia decurrens Willd. var. mollis auct. non Lindl.
  • Acacia decurrens Willd. var. mollis Lindl.
  • Acacia mollissima sensu auct.
  • Albizia mearnsii De Wild.
  • Racosperma mearnsii (De Wild.) Pedley[1]

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Acacia mearnsii is a fast-growing, extremely invasive leguminous tree native to Australia. Common names for it include black wattle, Acácia-negra (Portuguese), Australian acacia, Australische Akazie (German), Swartwattel (Afrikaans), Uwatela (Zulu). This plant is now known as one of the worst invasive species in the world.[2]

Taxonomy

Émile Auguste Joseph De Wildeman described the black wattle in 1925.[3] The species is named after American naturalist Edgar Alexander Mearns, who collected the type from a cultivated specimen in East Africa.[4] Along with other bipinnate wattles, it is classified in the section Botrycephalae within the subgenus Phyllodineae in the genus Acacia. An analysis of genomic and chloroplast DNA along with morphological characters found that the section is polyphyletic, though the close relationships of many species were unable to be resolved. Acacia mearnsii appears to be most closely related to A. dealbata, A. nanodealbata and A. baileyana.[5]

Distribution and habitat

A. mearnsii is native to south-eastern Australia and Tasmania, but has been introduced to North America, South America, Asia, Europe, Pacific and Indian Ocean islands, Africa, and New Zealand.[6][7][8][9][10]

It has been introduced to numerous parts of the world, and in those areas is often used as a commercial source of tannin or a source of firewood for local communities. In areas where it has been introduced, it is often considered a weed, and is seen as threatening native habitats by competing with indigenous vegetation, replacing grass communities, reducing native biodiversity and increasing water loss from riparian zones. Found in tropical rainforests.

In its native range A. mearnsii is a tree of tall woodland and forests in subtropical and warm temperate regions. In Africa the species grows in disturbed areas, range/grasslands, riparian zones, urban areas, water courses, and mesic habitats at an altitude of between 600-1700m. In Africa it grows in a range of climates including warm temperate dry climates and moist tropical climates. A. mearnsii is reported to tolerate an annual precipitation of between 66 to 228 centimetres (26 to 90 in), an annual mean temperature of 14.7 to 27.8 °C (58.5 to 82.0 °F), and a pH of 5.0 – 7.2.[11] A. mearnsii does not grow well on very dry and poor soils.[12]

Ecology

A. mearnsii plays an important role in the ecosystem in its native Australia. As a pioneer plant it quickly binds the erosion-prone soil following the bushfires that are common in its Australian habitats. Like other leguminous plants, it fixes the atmospheric nitrogen in the soil. Other woodland species can rapidly utilise these increased nitrogen levels provided by the nodules of bacteria present in their expansive root systems. Hence they play a critical part in the natural regeneration of Australian bushland after fires.

Acacia mearnsii seed pods
  • Consumption and excretion: The seeds are potentially distributed by rodents or birds.[13]
  • For ornamental purposes (local)
  • By animals: The dispersal of the seeds of A . mearnsii is believed to be aided by cattle and birds.[14]
  • By people: Local people collecting branches and logs for firewood may spread seeds.[15]
    • Transportation of soil: The seeds may also be spread by the movement of seed-contaminated soil.[16]
  • By water: The hard-coated seeds are spread readily down water courses.[16]

Mycorrhizal fungi attach to the roots to produce food for marsupial animals, and these animals in turn disperse the spores in their droppings to perpetuates the symbiotic relationship between wattle's roots and the mycorrhizal fungi.

The cracks and crevices in the wattle's bark are home for many insects and invertebrates. The rare Tasmanian hairstreak butterfly lays her eggs in these cracks, which hatch to produce caterpillar larva attended by ants (Iridomyrmex sp.) that feed off the sweet exudates from the larva.

The tree is home to various grubs, such as wood moths, which provide a food source to the Australian black cockatoos, who strip the bark for access to these borers.

During winter insects, birds and marsupials are hosted by the black wattle with the aid of their supplies of nectar in their leaf axials. These creatures provide an important predatory role to deal with tree die back caused by scarab beetles and pasture pests.

Black wattles, along with gums, native box, native hop form the framework vegetation on so-called "hill-topping" sites. They are often isolated remnant pockets of native vegetation amongst a lower sea of exotic pasture. These "hill topping" sites are critical habitat for male butterflies to attract females for mating, which then lay their eggs under the wattle's bark elsewhere but still within close proximity. It's the only acceptable mating site in the area for these butterflies.

Black wattle flowers provide very nitrogen rich pollen with no nectar. They attract pollen-feeding birds such as wattlebirds, yellow-throated honeyeaters and New Holland honeyeaters. The protein rich nectar in the leaf axials is very sustaining for nurturing the growth of juvenile nestlings and young invertebrates, e.g. ants.

Ants harvest the seed, attracted by the fleshy, oil rich elaiosome (or seed stalk), which they bury and store in widely dispersed locations. These seeds are buried ready for germinating with the next soaking rains. However a "wattle seed-eating insect' which enjoys liquid meals using its proboscis-like injector to pierce the testa and suck out the embryo often reduces the seeds viability.[17]

Reproduction

A. mearnsii produces copious numbers of small seeds that are not dispersed actively. The species may resprout from basal shoots following a fire.[6] It also generates numerous suckers that result in thickets consisting of clones.[6] Seeds may remain viable for up to 50 years.[18]

Chemistry

Leuco-fisetinidin, a flavan-3,4-diol (leucoanthocyanidin) and a monomer of the condensed tannins called profisetinidins, can be extracted from the heartwood of A. mearnsii.[19]

References

  1. ↑ Lua error in package.lua at line 80: module 'strict' not found.
  2. ↑ Global Invasive Species Database: 100 Worst Invasive Species
  3. ↑ Lua error in package.lua at line 80: module 'strict' not found.
  4. ↑ Lua error in package.lua at line 80: module 'strict' not found.
  5. ↑ Lua error in package.lua at line 80: module 'strict' not found.
  6. ↑ 6.0 6.1 6.2 PIER, 2003. Pacific Island Ecosystems at Risk web
  7. ↑ Adair, R. (2002). Black Wattle: South Africa Manages Conflict of Interest. CABI Biocontrol News March 2002, Volume 23 No. 1. web
  8. ↑ Paiva, J. 1999. Acacia. In Talavera, S. Aedo, C, Castroviejo, S, Romero Zarco, C, Sáez, L, Salgueiro, F.J & Velayos, (ed). Flora Iberica – Plantas Vasculares de la Península Ibérica e Islas Baleares. Vol.VII(I). Leguminosae. Real Jardín Botánico, CSIS. Madrid. ISBN 84-00-06221-3. pp. 11- 25.
  9. ↑ Franco, J.A. 1971. Nova Flora de Portugal (Continente e Açores). Vol. 1. Franco, J.A. (Ed.). Lisboa.
  10. ↑ Tutin, T. G., Heywood, V.H., Burges, N.A., Moore, D.M., Valentine, D.H., Walters, S.M. & Webb, D.A. 1992. Flora Europaea. Vol.2 Rosaceae to Umbelliferae. (reprint). Cambridge University Press. Cambridge. ISBN. 0 521 06662 X pp. 84–85
  11. ↑ Duke, J. A. 1983. Acacia mearnsii. Handbook of Energy Crops. Unpublished. web
  12. ↑ Franco, J.A. 1943. Dendrologia Florestal. Lisboa.
  13. ↑ Carr, G. D. Acacia mearnsii University of Hawaii, Botany Department. web
  14. ↑ Milton, S.J., Dean W.R.J. and Richardson, D.M. 2003. Economic Incentives for Restoring Natural Capital in Southern African Rangelands, Front Ecol Environ+C26 1 (5): 247,254.
  15. ↑ Sankaran, K. V. (2002). Black Wattle Problem Emerges in Indian Forests. CABI Biocontrol News March 2002 23(1) web page (archived 2005)
  16. ↑ 16.0 16.1 De Wit, M.P., Crookes, D.J. and Van Wilgen, B.W. 2001. Conflicts of Interest in Environmental Management: Estimating the Costs and Benefits of a Tree Invasion, Biological Invasions: 3 167 – 178.
  17. ↑ Australian Plants Society (Tasmania), June 2000
  18. ↑ Lua error in package.lua at line 80: module 'strict' not found.
  19. ↑ Lua error in package.lua at line 80: module 'strict' not found.

External links

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