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EXAMPLAR – OPINION PIECE LEVEL 4 The Value of Wolves << student name >> When Yellowstone National Park was first established in 1872, many grey wolves lived in the park. Starting in the early 1900’s, people began to kill these animals for their furs, and to protect cattle and other farm animals. In 1926, the last wolf was killed in Yellowstone National Park. By 1970, environmentalists began to notice a change in the ecosystem of the park. They then reintroduced 15 grey wolves from Canada to the park. Many of the farmers believe that this was a poor decision because they knew that their livestock was at risk for being killed. On the contrary, many environmentalists think that this was the right choice. It was necessary to reintroduce wolves to Yellowstone National Park because of the animals and plants that were being harmed, and the results on Isle Royale when the same situation occurred there. The wolf is known as a ‘keystone species’. This means that they are a vital animal in the food chain. For example, the leftovers that wolves eat provide a quick meal for scavengers such as ravens, eagles, magpies and bears. In the winter, it is critical for wolves kill their prey and leave leftovers, as this is the main source of food for these animals (Hayes, et. al., 2000). There has been known to have been up to 135 ravens feast off of one wolf kill (Stahler, et. al., 2002). Without the wolf, the number of ravens started to decrease in the park. In addition, the number of weasels and badgers increased dramatically, while the number of fishers, bobcats, lynx, and red foxes dropped (Smith et al., 2003). The animals that were affected the most by the lack of wolves were the ungulates; the primary food source for wolves. The number of these animals, especially elk, increased dramatically when the wolves were gone. As elk consist of 92% of a wolf’s diet (Mech, et. al., 2001), once they were reintroduced, scientists from the university of Wyoming predicted that the elk populations would increase by 15% to 25%. Other predators of elk are cougars, grizzly bears and black bears. Before the reintroduction of the wolf in Yellowstone National Park the number of cougar kills towards elk was twice the amount as it was after (Crabtree and Sheldon, 1999). Also, since the reintroduction of the wolves, 4 beaver colonies have been established in the Yellowstone area (Tyers, et. al., 2000). As stated, many species have benefited from the reintroduction of wolves and therefore, the choice to reintroduce wolves was a positive one for the food chain and ecosystem of Yellowstone National Park. Plants were greatly affected by the absence of the wolf. Ungulates are herbivores, as they feed off of plants. When the wolves were not in Yellowstone National Park, the population elk and other ungulates increase, as the number of willows and other plants decreased (Ives. 2004). Cottonwood trees are food for elk, and they are vital to rebalance stream ecosystems. The reintroduction of wolves tremendously impacted the quality of the streams in a positive fashion, and they prevented the extinction of the Cottonwood tree (Science Daily, 2003). Other plants in the stream ecosystem such as berry-producing shrubs suffered when the wolves were not present. Their population decreased and negatively affected the birds, insects and fish in that area (Science Daily, 2003). Another plant that was affected was the Aspen tree. In some areas, there was up to a 90% decrease of this tree (Ripple, et. al., 2001). Once wolves were present again, these plants could multiply and grow taller, and this created a more balanced environment. The soil became healthier and had more nutrients as many coniferous and deciduous trees had been affected. These plants and trees are important for many species of birds, mammals, beavers and moose. Due to the necessity for plants in to have a balanced ecosystem, wolves play a large and positive role in Yellowstone National Park. Isle Royale is an island that is completely isolated and the animals their have no way of swimming to the shoreline of another land mass. On this island there is an ecosystem of plants and animals, including wolves. At one time wolves were completely wiped out and the island suffered greatly (Smith, et. al., 2003). There are some differences between these two ecosystems. Isle Royal is a closed system (the wildlife is unable to move tom difference areas to live), and it has about one third of the number of animals at Yellowstone National Park. Yellowstone is an open system and they have a wider variety if animals. The affects of no wolves on Isle Royale is much greater and it is a good spot to see the affects with the lack of these animals (Haines, 1997). When there were no more wolves in Isle Royale, the ungulate species greatly increases as well as the plant species. (Allen 1979). In this case, wolves reintroduced themselves by crossing Lake Superior in the 1940’s (Allen, 1979). The wolves helped with keeping the food chain balanced, and they allowed the forest to recover from moose grazing. Although this reintroduction helped, there are still many negative affects from when wolves were not present. Since the many of the trees were not able to escape moose feedings, many of these trees have still not been able to grow back (McLaren and Janke, 1996). Even after a century has past, the forest at Isle Royale is not what it used to be. This would have been similar results to Yellowstone National Park. There are several reasons why the reintroduction of wolves was necessary for Yellowstone National Park. The plant and animals were suffering greatly without their presents. Also, the devastating affects of a similar situation on Isle Royale caused concern, and showed the “cause and effects” for Yellowstone. Clearly, bring these animals back to Yellowstone caused many positive effects. As of 2002, there were 14 packs (132 wolves) in Yellowstone (Boyce, 1993, Mack and Singer 1993). Considering the above reasons, it has been shown that there should be a greater knowledge and appreciation for the value of wolves. Bibliography Allen, D.L. 1979. The wolves of Minong; Their vital role in a wild community. Houghton Mifflin Company, Boston. 499 pp. Boyce, M.S. 1993. Predicting the consequences of wolf recovery to ungulates in Yellowstone National Park. Pages 234-269 (In) Cook, R.S., (ed.) 1993. Ecological issues on reintroducing wolves into Yellowstone National Park. Scientific Monograph NPS/ NRYELL /NRSM-93/22, USDI Nat. Park Serv., Denver, Colo. 328 pp. Crabtree, R.L. and J.W. Sheldon. 1999. Coyotes and canid coexistence. Pages 127-163 (In) Clark, T.W., A.P. Curlee, S.C. Minta, and P. Kareiva, (eds.) Carnivores in Ecosystems: The Yellowstone Experience. Yale University. Press, New Haven Conn. 429 pp. Haines, A.L. 1977. The Yellowstone Story. Colorado Associated University Press, Vol 2, 543 pp. Hayes, R.D, A.M. Baer, U. Wotschikowsky, and A.S. Harestad. 2000. Kill rate by wolves on moose in the Yukon. Canadian Journal of Zoology 78: 49-59. Mack, J.A. and F. J. Singer. 1993. Using Pop-2 models to predict effects of wolf predation and hunter harvests on elk, mule, deer and moose on the northern range. Pages 49-74 in Cook, R.S., ed. 1993. Ecological issues on reintroducing wolves into Yellowstone National Park. Scientific Monograph NPS/NRYELL/NRSM-93/22. USDI Nat. Park Serv., Denver Colo. 328pp. Mech, L.D. 1966. The Wolves of Isle Royale. U.S National Parks Fauna Series 7. McLaren, B.E. and R.A. Janke. 1996. Seedbed and Canopy Cover on Balsam Fir Seedling Establishment in Isle Royale National Park. Canadian Journal of Forest Research. 26:782-793. Ripple, W.J., E.J. Larsen, R.A. Renkin, and D.W. Smith. 2001. Trophic cascades among wolves, elk and aspen on Yellowstone National Park’s northern range. Biological- Conservation 102: 277-234. Smith, D.W., L.D. Mech, M. Meagher, W.E. Clark, R. Jaffe, M. K. Phillips, and J. A. Mack.2000. Wolf- Bison Interactions in Yellowstone National Park. Journal of Mammaglogy 81: 1128-1135. Stahler, D.R., B Heinrich, and D.W. Smith. 2002. Common ravens, Corvus corax. Preferentially associate with grey wolves, Canis lupus, as a foraging strategy. Animal Behaviour 64:283-290. Tyers, D.B., and L.R. Irby. 1995. Shiras moose winter habitat use in the upper Yellowstone River Valley prior to and after the 1988 fires. Alces 31:35-43. U.S. Department of the Interior, National Park Service. 2000. Bison Management plan for the state of Montana and Yellowstone National Park: Final Environment Impact Statement Vol. 1, D-655a. 874 pp.