There is a prevailing apprehensiveness all over the universe about the impact of introduced species on the universe ‘s biodiversity due to the capableness of these introduced species impacting native species ( Blanvillain et al. , 2003 ) . Native species are affected by the interactions they are holding with these species, interactions such as competition, predation, herbivory, habitat change, diseases and hybridisation ( Witmer and Fuller, 2011 ) . The magnitude of the impacts of the introduced species can be variable ; some are lay waste toing while others are relatively benevolent.
The impacts of these introduced species can fly alterations in population kineticss and community construction of the native species ( Griffin and Boyce, 2009 ) , besides the ecosystem services can be altered as a consequence. For effectual direction of biodiversity, it is indispensable to understand the impact of these introduced species. Since resources can be a confining factor for direction, prioritization should be given to the introduced species that pose greatest unwanted impact ( Grarock et al. , 2012 ) . Traditionally it was believed that all introduced species have a negative impact on native species ( Grarock et al. , 2012 ) hence this can take to uneconomical allotment of resources. Therefore understanding a species impact facilitates targeted direction to better the impact.
From old surveies, by Grarock et al. , ( 2012 ) it is apparent that it can be really hard to obtain the impact of the introduced species for three cardinal grounds being ; ( 1 ) insufficient informations prior to and so after the invasion. ( 2 ) Changes in the environment happening alongside species debuts, doing it hard to distinguish species impacts from the impacts of environmental alteration, examples being climate alteration and home ground glade. ( 3 ) Poor indulgence of the mechanisms of the impact such as competition versus predation.
Peacock et al. , ( 2007 ) found out that change of biological communities in footings of species profusion, species evenness, guild structuring, biomass and community composing are a consequence of uninterrupted enlargement of human population which causes monolithic land usage alterations. Matching this with the increasing international trade and travel monolithic proliferation of introduced beings has resulted. A major obstruction for the continued endurance of a big proportion of the universe ‘s threatened species peculiarly at local graduated table is the inauspicious environmental effects of introduced species ( Grarock et al. , 2012 ) . Introductions of species outside their natural scope can either be inadvertent or deliberate. Examples of such debuts are for agribusiness, runing, biological control ; habitat Restoration and favored trade being calculated mechanisms while ship assisted draw is said to be inadvertent ( Carr, 1990 ) . As a consequence of homo induced habitat alteration, the geographical scopes of many species are of course increasing. It is non the instance that impairment or atomization of home grounds is appropriate for introduced species establishment but this works interactively with the innate effects that the introduced species themselves pose to the digesting native communities ( Philip, 2007 ) .
In South Africa the association between extremely successful introduced birds, human distribution and modified home grounds has been postulated from the Indian mina or Common mina ( Acridotheres tristis ) ( Peacock et al. , 2007b ) hence human distribution and the rate at which home grounds are modified influences the success and spread of the introduced species. Indian mina is one of the four species out of 48 that have established a feasible population in South Africa ( Carr, 1990 ) . The Indian mina belongs to the Sturnidae ( Starlings ) which is a really adaptable and successful passeriform bird household ( Lovette et al. , 2008 ) . Its distribution is so big to an extent of 1 000 000 to 10 000 000 Km2 globally ( Witmer and Fuller, 2011 ) furthermore it is a species of least concern in IUCN ( Peacock et al. , 2007b ) .
The Indian mina is native to the Indian subcontinent and the next countries, throughout the twentieth century it has expanded its scope up to Malay Peninsula, Thailand, China and Vietnam perchance by debuts ( Philip, 2007 ) .According to Parsons et al. , ( 2006 ) in Melbourne, Australia, minas were intentionally introduced around 1862 for biological control of insect plagues in agricultural Fieldss and market gardens. The birds rapidly established and they became the beginning of other debuts in other parts of Australia ( Parsons et al. , 2006 ) . Around 1900s minas were released in Durban, South Africa ( Peacock et al. , 2007a ) besides for biological control of plagues. Now they have expanded and occur from Kwazulu-Natal up to Northern Free State and Southern Transvaal ( Carr, 1990 ) . These birds were traced to hold originated from populations of the races Acridotheres tristis tristoides, native to Assam and Burma ( Peacock et al. , 2007a ) . Another debut took topographic point in Johannesburg around 1930s and these were from a population of nominate Indian races Acridotheres tristis tristis ( Peacock et al. , 2007a ) . In add-on to consider debuts, minas in South Africa are presently undergoing rapid and extended enlargement, as a consequence of extended natural flora glade for agribusiness and increasing human population densenesss ( Carr, 1990 ) . In Botswana individual birds were observed in Mahalapye in March 1975 and in 1991 March in Gaborone ( Brewster and Major, 2000 ) and besides the birds were observed in Bobirwa, north eastern portion of Botswana in 1996. Refering these birds found in Botswana, it is non apparent whether they were from populations in South Africa or they were from a separate debut.
In the native scope, the Indian mina prefers unfastened farming areas and metropoliss every bit good. The Indian mina is closely associated with worlds since it is frequently found on the outskirts of towns and outlying homesteads ( Griffin, 2009 ) . Seasonal fluctuation in the happening of the birds has non yet been documented. In South Africa, a high rate of happening of the birds in an country that usually does non hold high populations of these birds likely coincides with the genteelness season and besides the usage of unreal constructions for nesting ( Peacock et al. , 2007a ) . Besides in urban countries of South Africa, genteelness can be all twelvemonth about but nesting chiefly occurs in October-March ( Carr, 1990 ) . Indian mina is frequently accused of displacing native bird species and little mammals from gardens and nesting holes. However this competition may be intense for illustration in Durban, South Africa it was reported that Mynas demolished weaver nests ( Peacock et al. , 2007b ) .
Concern has ever been raised around the universe that the mina affects native birds in three ways therefore completion for nutrient, cavity-nesting sites and competition for district ( Grarock et al. , 2012 ) . Despite these allegations, it is frequently hard to obtain empirical grounds of the impact of the Indian mina on the native bird species. But supervising the go oning range addition of this bird species and finding the comparative importance of the influential factors finding its spread and denseness provides valuable chance to ecologists to pull off current and predict hereafter effects of the bird species on native species. In Botswana, a landlocked state bordered by South Africa, Namibia, Zimbabwe and Zambia, of all time since the birds were foremost observed around 1975, there are no surveies that can be singled out to hold tried to find the possibility of the debut of the Indian mina in the state or look into the competition significance of the Indian mina to the native bird species or look into the subsequent urbanisation function in the interactions between the Indian mina and native birds. Botswana has approximately 12 Important Bird Areas, in which some of them coincide with the countries where the Indian mina have been observed. Due to this scenario, how does this bird species impact native bird species in Botswana owing to the fact that in all parts of the universe where the mina have successfully established, there is concern that the mina is hindering the endurance of native bird species through competition?
Therefore this research in Botswana would wish to concentrate on ;
Describing the relationship between the native bird grouping composing and the Indian mina,
Evaluate aggression initiated by the Indian mina to that of the native bird species and
Investigate the frequence at which the mina brushs native birds and the native birds are victims of its aggression.