Diversity, Abundance, Richness, and Birds of Conservation Interest in Nyando Sugar Belt, Muhoroni Sub-County, Lake Victoria Basin, Western Kenya

Thus far, no expedition has comprehensively surveyed the composition of bird species in the dilapidated habitats of Nyando sugar belt, Western Kenya. This has made it difficult unearthing equilibrium between agricultural growth and bird species conservation. In response, we conducted bird assessment by stratifying the expedition area into farmlands and shrub-land. We then sam-pled birds by the standard point count method and opportunistic counts within a 30 m radius parcel of land. We exhaustively observed 1450 birds of 122 species. The farmland recorded a density of 2.065 ± 1.11 birds per hectare whereas the shrub-land had a density of 1.644 ± 0.70 birds per hectare. Nyando sugar belt was a diverse community with a Shannon diversity index value (H’) of 3.225 regardless of the birds being constrained in certain habitats. The magnitude of the disparity in true diversity indicated that the farmland was 4 times more diverse than the shrub-land. The facts promoted by this research validate the incorporation of bird conservation in the farmland and formulation of avian conservation strategies.


Introduction
In Nyando sugar belt, more land is being converted from natural habitats into sugarcane plantations and human habitats. The remnant indigenous vegetation is unsustainably being overexploited for charcoal, firewood and construction Open Journal of Animal Sciences area is the unsustainable exploitation of natural resources, particularly indigenous vegetation for charcoal, firewood and construction materials. Surprisingly no indigenous forest is left in Nyando sugar belt.

Data Collection Methods
For this bird survey, we preferred the standard point count method and opportunistic counts as the most applicable survey methods since they have proved effective for most researchers all over the world. Bibby et al. (1998) suggest fifty point count stations in each study area. In Nyando sugar belt, we randomly picked a total of five two kilometers long of line transects since they would collectively accommodate fifty 30 m radius point count plots, set at standard intervals of 200 m. We used GPS (Global Positioning System) to set and spot the sampling stations. The observers stood at the center of the point count plots and recorded all birds seen or heard for a period of 10 minutes. Bird observations were conducted at 6.30 a.m. to 10.30 a.m. and 3.30 p.m. to 6.30 p.m. on good weather days. The birds were then identified with Zimmerman bird identification key [6]. We consistently organized random walks to exhaustively search for new bird sightings.  (Spermestes cucculatus), the Little Swift (Apus affinis), the Common Bulbul (Pycnonotus barbatus) and the Fan-tailed Widowbird (Euplectes axillaris) were the most abundant bird species respectively ( Figure 2).

Bird Species Abundance
Bird species abundance in the farmland had a mean of 2.065 ± 1.11 birds per hectare whereas the shrubland had a mean of 1.644 ± 0.70 birds per hectare.

Bird Species Diversity
Species diversity index was determined by use of Shannon Weiner diversity index (H'). This was purposed to show the number of different categories of bird species in a data set. It also accounted for how the individual bird species were distributed among the other bird species. The statistic that birds species diversity index (H') value was 3.225 suggests that the study area was a diverse habitation in spite of birds being limited to specific habitats. The true diversity (Table 1) indicated that the magnitude of the difference in true diversity (effective number of species) revealed that the farmland was four times more diverse than the shrubland ( Figure 3). We provided a checklist of all the bird species in Nyando sugar belt (Appendix 1).

Bird Species Richness
The farmlands had 86 species as contrasted to the indigenous shrub with 60 bird species (Table 2 and Figure 4). Shannon equitability index indicated that the     individual bird species were more evenly distributed in the farmlands than in the shrubland.
Species predictive curve modeled revealed that a complete bird community may not have been captured during the study. However, with more effort, species expected in Nyando sugar belt are at least 180 species ( Figure 5). In the farmlands 86 bird species were cumulatively recorded while 60 bird species were observed in the shrubland ( Figure 6).

IUCN Red Listed Species in Nyando Sugar Belt
A total of three species considered to be red-listed by IUCN were recorded: The Grey Crowned Crane (Balearica regulorum), endangered; the Fischer's Lovebird (Agapornis fischeri) near threatened; and the Steppe Eagle (Aquila nepalensis), endangered (Table 3).

Bird Migrants in Nyando Sugar Belt
Twenty-one (21) of the 122 species of birds observed in the study area were biome-characteristic species. In the entire landscape, there were 6 Afrotropical migrants (am) comprising of 5%, 12 Palearctic migrants (pm) comprising of 10% and 3 both Afrotropical and Palearctic migrants (am, pm) comprising of 2%. The rest of the birds (101) were residents comprising 83% ( Figure 9).

Bird Composition
Bird abundance expressed in birds per hectare was different between the two habitats and largely high in areas with extensive human agricultural activities and low towards degraded natural habitats. This result agrees with the findings of Chace and Walsh (2006) and [7] who resolved that human-disturbed habitats offer heterogeneous conditions that draw human tolerant species [8]. The higher bird abundance in the farmlands could be attributed to a small number of avian species that can cohabit with human beings such as the Bronze Mannikin (Spermestes cucullatus), Common Bulbul (Pycnonotus barbatus), House Sparrow (Passer domesticus) and the Grey-headed Sparrow (Passer griseus) [8]. According to Gloria, 2002 [8], Pennington and Brail (2011) correspondingly found comparable results and deduced that higher bird abundance in the farmlands with settlement was prompted by landscape heterogeneity [9]. The low abundance in the shrubland is in agreement with Doggart (2005), who ascribes this to habitat degradation through human invasive activities like cattle grazing, fuel wood collection, pasture burning and charcoal processing [10]. Gloria, 2002 attributes this observation to the decline in vegetation cover for concealing from predators, shelter, food resources and breeding materials leading to competitive exclusion [8]. Rodriguez attributes this lower abundance in the shrubs to the migrations of bird species in response to particular species requirement such as nesting materials and procreation sites [11].
The highest species diversity in the farmland indicates a complex community in which a high degree of species interaction is possibly contrary to a higher dominance observed in the shrubland. This implies that few bird species pre-dominate the habitats. Though shrubs showed less bird diversity, higher dominance was due to persistence of native and generalist species [9].
Based on the point count method, bird species richness was high in the farmland. This was most likely the case attributable to diversity of vegetation types that supply essential bird resources for their survival. According to Scheiner (2003), species richness is high when bird species are drawn from diverse communities [12]. As stated by Laube (2003), the structure of bird community is most likely modeled by the composition and organization of its ecological niche [13]. The decrease in bird species richness due to human hindrance has been exhibited in bird habitats of the tropical regions [14], and indisputably in the natural shrubs of Nyando sugar belt. Human shrub destruction appears to lessen the vital resources needed by various avian species.

Bird Species of Conservation Interest
During the expedition, we recorded a number of species of birds of international conservation concern. Bennun and Njoroge (1996) noted that some bird species have intrinsic conservation interest for the reason that they are either endangered, threatened, vulnerable, rare, or endemic [15]. In Nyando sugar belt, the Open Journal of Animal Sciences Fischer's Lovebird (Agapornis fischeri) was recorded as near threatened, Grey-crowned cranes (Balearica regulorum) as vulnerable, Steppe Eagle (Aquila nepalensis) as endangered and the Speckled Mousebird (Colius striatus) as endemic. This could be due to bird habitat loss which concurs with IUCN (2008) that habitat loss due to the growth of human activities such as urbanization, settlement and agricultural activities is the main threat facing 85% of all bird species described in the IUCN Red List.
Twenty-one (21) of the 122 species observed in Muhoroni Sub-County were biome-characteristic species. There were 12 Palearctic migrants (10%), 6 Afrotropical migrants (5%), 3 both Afrotropical and Palearctic migrants (2%). The presence of these migratory birds in Nyando sugar belt could be attributed to this expedition coinciding with the

Forest Dependency
In Muhoroni Sub-County 6 birds (5%) were forest generalists (F), 40 birds (33%) forest visitors (f) while 76 birds (62%) were non-forest birds. As the forest habitat becomes increasingly threatened, the birds they host are attracting enormous attention. According to Bennun (1996), studies on forest birds are worthwhile for at least two whys and wherefores [15]. First of all, the composition and richness of forest birds can signify its overall value for the conservation of biodiversity [16]. Secondly, habitat modification and its impacts and more hardly restoration can be gauged by censoring bird communities [17].
Conservationists need supplementary guidelines as to the worth of particular species of birds in pointing out forest condition. The 0% of 'forest specialists' (FF) is a signal that forests in Nyando have been altered to the magnitude that they cannot sustain forest specialists. As per Bennun and Njoroge (1999), forest generalists (F), occur in undisturbed forest and in forest edges, strips, gaps or in modified and fragmented forests [18]. However, forest generalists persistently continue to rely on forests for some resources [18]. The presence of these species in the Nyando sugar belt is attributed to the live fences composed of woody plants and scattered trees that provide breeding sites. Forest visitors (f species) comprised 33% of all the birds observed. Bennun (1999) defines them as those birds which are often observed in the forest but are not fully dependent upon it [18]. They can certainly survive in habitats where the forest has completely become extinct [15]. The presence of these species in Muhoroni is an indication of forest deterioration.

Conclusion
There was clear variation in the diversity, abundance, and richness of bird species in the farmland and shrubland in Nyando sugar belt. This authenticates that dilapidation of bird habitations is steering birds to areas inhabited by humans. This relocation could be due to a potential deterioration of avian resources in the natural shrubs and an upwelling of these resources in the agricultural farms. Any pursuit that changes the original structure of habitat diversity influences the composition of the habitat. In a nutshell, anthropogenic activities that restore the complexity of the habitat incline to draw more bird species as juxtaposed to deteriorated indigenous habitats, and for that reason, surveys concerning the management of avian species within the farmland need to be spotlighted and allotted additional resources. To aid in the conservation of bird species in Nyando sugar belt, further research is necessary to keep an eye on the birds of conservation concern especially the IUCN red-listed species. Open Journal of Animal Sciences