POPULATION GROWTH
Name
Walden
NASC 1001 - Environmental Science
2022
POPULATION GROWTH
Rapidly increasing human population and changing socio-economic lifestyles of different
communities has led to greater natural resource exploitation which has been identified as the
greatest threats to wildlife conservation within rangelands the world over (WRI 1997; Ellis et al.
1999; Foran and Howden 1999). Kenya population is increasing at the rate of 1.8% per annum
(Republic of Kenya, 2009) as a typical developing country. Then human basic needs including
shelter and food demands have to be satisfied, especially in focusing on land for settlement and
agricultural production. Within Kenya, changes in land policies, high human population growth
rates, and rapid changes in people’s expectations over the past few decades have resulted in the
expansion of cultivation, growth in the number of permanent settlements, urbanization and
diversification of land-use activities near conservation areas. All of these factors have contributed to
unprecedented human–wildlife conflicts (Western 1982; Ellis et al. 1999). The changes in land
ownership and policies from communal to freehold holdings has facilitated a market-oriented
economy, which tends to promote expansion of crop agriculture and commercialization of livestock
production systems around wildlife conservation areas (Galaty 1994). Consequences of these
changes on land-use patterns include declining ecological, economic and social integrity of
rangelands due to fragmentation of landscapes, declining rangeland productivity, diminishing
wildlife migratory corridors, wildlife populations and diversity, and cultural and economic
diversification due to immigration (Gichohi et al. 1996).
In Kenya and many parts of the world, protected areas have proved to be too small to sustainably
maintain long-term, viable wildlife populations and diversity (Newmark, 1993). More than 70% of
wildlife is found outside national parks and game reserves in Kenya (Western and Pearl 1989).
Private and communally owned lands within pastoral areas/rangelands provide wildlife the needed
movement and dispersal areas.
Reduction in land sizes and connectivity, pastoral mobility and livestock grazing areas have been
reduced/curtailed due to fragmentation, fencing and cultivation. Therefore the role of wildlife
dispersal areas and migratory corridors outside the protected areas is critical to wildlife conservation
in Kenya. Given the observed phenomena of land sales and fragmentation within the
communal/rangelands which is too high, viable wildlife corridors need to be established before it is
too late.
However, creation of protected wildlife areas has triggered off an over concentration of human
population outside and a diminution of land per capita. Some communities have planted their crops
in arid lands, usually encroaching areas of wildlife. As a result, human and wildlife share natural
resources in these areas (Chiemelu, 2004), creating a spatial competition since some of the
resources like freshwater are unevenly distributed in space and time. The cultivated crops are
infringing on the migratory corridors of wildlife. On the other hand, local population considers
wildlife as an obstacle for development since it damages crops, buildings or kills cattle or even
people. In response, human kill wildlife, which only contributes to further increase the human
wildlife conflicts.
According to the 2009 population census, Rimoi's population was estimated to be 18,544 people
and was estimated to be 12,269 people in 1997 population census with an annual growth rate of
2.2%. A decline in infant mortality rate has been largely credited for the rapid increase in the
Rimoi’s population over the years although the effect of the Acquired Immune Deficiency
Syndrome (AIDS) pandemic on population growth still remains to be seen in the area. The 1997
male to female population ratio was 1:1.05 with 47% of the people being under 15 years of age.
Such a growing population structure poses great challenges to the Rimoi national reserve
biodiversity conservation as the demand for land and other natural resources will continue to
increase. This is worsened by the fact that about 86% of the local population depend on both
individual and communal lands for their daily subsistence and also because of poverty, people tend
to rely on' natural resources for their survival. As is the case in other ASAL areas in Kenya, Rimoi
region has very high poverty level. For example, the 2005 poverty assessment study showed that
61% of the local Rimoi households were poor with 45% of them living in absolute poverty as they
can hardly afford basic food requirements. Furthermore, the majority of such poor households are
headed by women. This has led to greater exploitation of natural resources through intensive
cultivation and patches of land irrigation has been on an increase. There is also an increased
demand on forest goods and services within the region.
Population density and natural resource exploitation in Rimoi eco-system in the selected
villagesa
Sub-
Location
Population
Density
(people/km2)
%of area under
Cultivation Pastoralis
m
Woodland
Kabulwa 65 47.
5
13.
5
39.
0
Kessup 65 41.
8
33.
6
26.
9
Kamoigon 59 44.
9
17.
1
38.
0
Rimoi 30 37.
3
27.
7
35.
0
Annin 15 25.
7
10.
3
64.
0
Setek 11 11.
4
24.
6
65.
0
Siroch 11 16.
8
24.
2
59.
0
Source: Shumba et. al.; (2011)
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