Extensive or nomadic livestock production system contributes a significant proportion
of national revenues and food security in Tanzania, with over 90% of livestock
contribution to National GDP. However, rangelands are increasingly over-exploited
leading to physical degradation of landscape and loss of diversity and richness
of herbaceous plant species, which could also be the case in the Ngorongoro
Conservation Area (NCA).
In the past 20 years, rangelands in NCA experienced dramatic change of livestock
population, with preference towards small stock (sheep and goat) among pastoralists.
In the 1960’s, the ratio of cattle to small stock was 2:1, but by 2018 the ratio had
shifted to 1:3 respectively. The shift in composition of livestock has been driven
by the effect of climate change mainly due to prolonged drought and associated
diseases. Small stock are relatively resistant to severe drought because of small
body size and also have fewer diseases, hence, high survival rate during bad years.
The current study was conducted to assess and establish on the impact of small
stock on NCA rangelands quality to enable the Ngorongoro Conservation Area
Authority (NCAA) manage the ecosystem sustainably based on quantification of
several indicators of rangeland quality. The study involved some interface areas
including the Loliondo Game Controlled Area (LGCA), areas bordering the Serengeti
National Park (SENAPA), Maswa Game Reserve (MGR) and Makao Wildlife
Management Area (WMA). In addition to vegetation survey and soil analysis, the
study was complemented by administering questionnaires to pastoral communities
to understand their knowledge, attitude and practices related to domestication of
small stock and their impacts to rangelands quality. The survey was conducted
on eleven geo-referenced transects which were selected based on habitat and
vegetation structure of each study zone. During data collection, each transect line
was tracked by using hand held GPS equipment.
Vegetation and soil samples were analysed in the laboratory by following standard
protocols and the results were reported in international standards and units of
measurements. Data analysis employed various statistical tests and models to answer
research questions. For example, Descriptive statistics was used to summarize the
questionnaire response data and chi-square analysis was performed to determine
the differences in the independent variables that explain knowledge about impacts
of small stocks to the environment. All calculations were done in Statistical Package
for Social Sciences (SPSS version 24, NY, USA).
Results of vegetation attributes indicated high variance in terms of plant types and
their desirability. Seemingly, forb species dominated the rangelands in NCA while
sedge species were of low frequency. Generally, the distribution of desirable and
undesirable plant species are nearly the same within rangelands. However, very
small proportion of grass species was highly undesirable while the opposite was
true for forb species. Among plant species encountered, 40% were grass, 54%
were forb, 2% were sedges, shrubs and tree saplings respectively. Proportionally,
about 10% were highly desirable plant species, 34% were desirable, 23% were
less desirable and 33% were undesirable plant species. Among grass species
encountered, 9% were highly desirable, 19% desirable, 11% less desirable and 1%
undesirable. Considering forb species, 1% was highly desirable forb species, 12%
were desirable, 10% were less desirable and 31% were undesirable.
Moreover, herbaceous plant species indicated highest diversity in NCA and lowest
in Maswa Game Reserve (MGR). The same was observed in Loliondo Game
Controlled Area (LGCA), southern Crater rim, SENAPA, Nainokanoka and Olbalbal
Higher grass richness was observed in Ngorongoro crater, Nainokanoka, southern
Crater rim and Olbalbal. However, most grass species in Nainokanoka and around
Ngorongoro crater rim were dominated by unpalatable buffalo grass (Eleusine
jaegeri);
Ecologically, rangelands experience serious decline of palatable grass species in
favour of unpalatable ones, thus diminishes its ecological limits of acceptable use
for herbivores. Indeed, the proportion of grass and herb within the study site was
highly heterogeneous which suggest high spatial variability of plant biomass. In
terms of grass biomass, Ngorongoro crater, Nainokanoka and Olbalbal had the
highest proportion of 33%, 17% and 13% respectively. For herbs biomass, Loliondo,
Nainokanoka, Ngorongoro crater and near crater rim had the highest herbs biomass
of 32%, 16%, 12% and 10% respectively.
Similarly, soil properties like soil pH, temperature, salinity, moisture content and
compaction indicated high variation across different landscapes. This is attributed
to dynamics of grazing pressure, annual rainfall, vegetation cover and topography.
Increasing pressure of small stock grazing in the NCA could have caused severe
soil degradation and loss of high quality vegetation cover in the natural rangelands.
This calls for multi-disciplinary approaches for attaining sustainable rangeland
management. Importantly, it should explore wide range of empirical scientific
knowledge that is backed up by local experiences of indigenous community.
Therefore, to address the observed challenges we recommend that: (i). Re-seeding
and establishment of high quality rangeland plants to improve the vegetation cover
in the heavily grazed area e.g. livestock dominated grazing in Nainokanoka and
Olbalbal areas concurrent with grazing ban; (ii). Rest-rotational grazing system
and defoliation management schemes based on sound scientific principles need
to be developed in the area; (iii). Uprooting of all unpalatable herbaceous and alien
invasive herbaceous plants such as Eleusine jaegeri and Guternbergia cordifolia
from all invaded areas should be applied; and (iv). Controlled grazing will be an
important means of rehabilitating the Ngorongoro Conservation Area rangelands.