1 ECOSYSTEM PAPER Lake Michigan is recognised as a vibrantdeep water oligotrophic ecosystem that underpins a variety amalgamation of native as well as non-native species. Species assortment along with their profusion and distribution of other subjected by a mixture of biotic as well as abiotic factors that signifies varied nature of Open Water Habitat types. Fundamental abiotic factors are regarded as depth temperature current and substrate. Furthermore, abiotic activities for example the increase level of water lucidity and quality related to the Zebra Mussel filtering activity also regarded as significant components of the ecosystem in USA (Bakker et al., 2013). However, the environmental purposes are further been established in order to concentrate on various environmental as well as habitat issues that are hindering the development towards accomplishment of the fish community objectives. Significant pollutants are further being addressed through the Lake Michigan lakeside controllingstrategy along with a remedial action plan that is exercised in order to address the sole area of attention in the Illinois waters of Lake Michigan (Gage & Axel, 2014). However, the Open Water division of Lake Michigan in Illinois further conserves critical records of wintering regular Goldeneye as well as long- tailed ducks, birds, loons, Grebes as well as other ducks in the season of spring as well as fall migration. It is significant to recognise that over the past three decades, Lake Michigan food web has been undergoing an enduring state of transition and has stated possibilities that this developing system has not yet attained a considerable position (Madigan et al., 2017). The proliferation of invasive species situated at trophic levels such as zooplanktons, mussels and fish have reportedly been united with the achievement of a nutrient abatement program that has further provided with continuingdiminutions in the
2 ECOSYSTEM PAPER nutrient import levels and have been contributing to a range of systemic transformations to the ecosystem process of Lake Michigan. Several investigation stated to be required in various areas of ecology in order to comprehend the food web response associated with Lake Michigan and further to anticipate its course to the range of stresses such as the nutrient stocking procedure, new invasive species, fishery management as well as change in the climatic conditions (Gilbert et al., 2014). Positive mutualism among exotic vertebrate as well as invertebrate predators results to a considerable and rapid change in the composition of the community for the consequential to a trophic cascade which has further developed to principal producers and to unknown aquatic species the Bald Eagle. It is important to note that the opossum shrimp, Mysisdiluviana further occupied the flathead lake Montana, which is regarded as the largest freshwater lake located in the Western region of the United States (Gallardo et al., 2016). Furthermore, atrophic cascade has its occurrence during the impact of reciprocal predators on their prey that transforms the profuse biomass or efficiency level of the population neighbourhood or further to the trophic level across more than single network in the food network However the theory of cascading dropping mutualism for the anticipates that the establishment of piscivores associated to the planktivore centric water body that would decrease the abundance of planktivore and further enhance the biomass level of zooplankton and also encourage largest zooplankton species and decrease the algal biomass (Jacobs et al., 2013). It is recognise that Mysids transformed into a well-established interactive and functionally substituted kokanee as the prevailing open water plant Erode however within several years mysids have been facilitating to be influenced by Lake Trout.
3 ECOSYSTEM PAPER Exotic species invasion is regarded as a significant motivator of worldwide ecological system especially in a lake ecosystem. It has been noted that the Exotic species have transformed the ecosystem by causing severe to disruptions in the food web dynamics biogeochemical cycles along with changing habitats and the decreasing rate of native biodiversity (Walsh,et al., 2016). Furthermore invasive species are considered to cause threatening health risks and further influence the socio-economic factors of the society by further causing damages to agricultural facilities commercial as well as recreational fisheries. The invasions by dreissenid mussels involving Zebra and quagga mussels have been reportedly purposes in the North American region. However, dreissenid has been causing impact on the increased trophic levels that includes benthic invertebrates and several fishes were considered to be combined. Furthermore, dreissenid effects the fish varied by the process of ecosystem (Sass et al., 2014). Though several observations reveal that dreissenid mussels have been influencing the aquatic ecosystem of USA it has been further noted that there may be trends in the responsive nature of the ecosystem. For instance the impact of dreissenid invasion possess certain variance with the ecosystem morphology, size of the ecosystem, and for the restricting factors related to the primary production as well as a traffic gradient.
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4 ECOSYSTEM PAPER References Bakker, E. S., Sarneel, J. M., Gulati, R. D., Liu, Z., & van Donk, E. (2013). Restoring macrophyte diversity in shallow temperate lakes: biotic versus abiotic constraints.Hydrobiologia,710(1), 23-37. Gage, S. H., & Axel, A. C. (2014). Visualization of temporal change in soundscape power of a Michigan lake habitat over a 4-year period.Ecological Informatics,21, 100-109. Gallardo, B., Clavero, M., Sánchez, M. I., &Vilà, M. (2016). Global ecological impacts of invasive species in aquatic ecosystems.Global change biology,22(1), 151- 163. Gilbert, B., Tunney, T. D., McCann, K. S., DeLong, J. P., Vasseur, D. A., Savage, V., ... &Kharouba, H. M. (2014). A bioenergetic framework for the temperature dependence of trophic interactions.Ecology Letters,17(8), 902-914. Jacobs, G. R., Madenjian, C. P., Bunnell, D. B., Warner, D. M., &Claramunt, R. M. (2013). Chinook salmon foraging patterns in a changing Lake Michigan.Transactions of the American Fisheries Society,142(2), 362-372. Madigan, M. T., Martinko, J. M., & Parker, J. (2017).Brock biology of microorganisms(Vol. 13). Pearson. Sass, G. G., Hinz, C., Erickson, A. C., McClelland, N. N., McClelland, M. A., &Epifanio, J. M. (2014). Invasive bighead and silver carp effects on zooplankton
5 ECOSYSTEM PAPER communities in the Illinois River, Illinois, USA.Journal of Great Lakes Research,40(4), 911-921. Walsh, J. R., Carpenter, S. R., & Vander Zanden, M. J. (2016). Invasive species triggers a massive loss of ecosystem services through a trophic cascade.Proceedings of the National Academy of Sciences,113(15), 4081-4085.