Effects of Land Use on the Riparian Vegetation along the Njoro and Kamweti Rivers, Kenya

Riparian zones are valuable ecosystems. They act as the ecological engineers that improve river health by delivering a range of ecosystem functions. They play a significant role in river health and provide various ecosystem goods and services for human well-being. Currently, riparian areas are under threat due to intensive human activities such as agriculture and urbanization, which alter riparian ecosystem structure and composition. The main objective of this study was to determine the effect of adjacent land use on the structure and diversity of the riparian vegetation in the Njoro and Kamweti Rivers. Along each river, three sampling sites were selected within the major land use categories which were; forest, agricultural and built-up areas. At each site, three 70 m long transects were established perpendicular to the river. The three plots were systematically established, separated by a 5 m distance along each transect. Forest canopy cover was estimated in percentage. Njoro River riparian vegetation recorded a total of 145 plant species from 40 families where trees and shrubs were dominant in the forest area, and herbs dominated the agricultural and built- up areas. In Kamweti River riparian area, a total of 110 species from 45 families were encountered, in which trees dominated the forest area. A similar trend to the Njoro River was observed, in which herbs were dominant in the agricultural and built-up areas. In Njoro River, the Shannon diversity (H’) values ranged between 2.73 and 3.08 scenarios of the changes in riparian vegetation observed, there is a pressing need for an integrated approach for the management of riparian zones based on various components such as riparian condition assessment, policy frame-work, stakeholder’s participation, management practices, legislation, and awareness.


Introduction
Globally, rivers are considered as the pillars of human civilization. The dependence of humans on riverine vegetation has been demonstrated by the presence of irrigated agriculture, towns, cities, and industrial sites along river banks. [1] reported that humans use more than half of the geographically accessible river runoff worldwide, therefore their significant impact particularly of an adverse kind on the structure and functioning of riparian areas would be predictable. The riverine ecosystems are considered as some of the most sensitive to human influence and potentially threatened ecosystems [2]. It has been observed that human-centered disturbances have a negative impact on the ecological security of watersheds by degrading the integrity of riverine ecosystems processes at both temporal and spatial scales. In comparison with many terrestrial and marine ecosystems, the biodiversity of river ecosystems is highly threatened or has already been diminished due to the growing need for water resources, and the impacts of climatic warming and land-use changes. The sustainability of river ecosystems stands to be further affected by increasing human threats [3].
The word "riparian" is derived from the Latin word "riparius" meaning land adjacent to the water body [4] [5]. Riparian vegetations are plant communities, occurring along the banks of water bodies and are a transition between terrestrial and aquatic systems [4] [6]. Riparian vegetations exhibit unique characteristics such as hydric soils, floral and faunal composition, and community structural relationships and provide an ideal habitat for floral and faunal communities [5] [7] [8]. A healthy riparian ecosystem is essential to the maintenance of water quality and biological integrity in surface water systems, and their destruction often leads to the degradation of adjoining aquatic ecosystems [4]. Despite their importance, anthropogenic impact on this vegetation type is still poorly understood more so in developing countries.
The natural factors that determine the composition, structure, and diversity of riparian vegetation include natural disturbances (e.g., periodic flooding or tree fall), altitudinal climate shifts geographically unique channel processes, and influences of upland on the fluvial corridor [9]. Studies demonstrate how increased human activities accompanied by the changes in land use and land cover within fluvial corridors and surrounding uplands have persistently stressed ripa-rian ecosystems [10] [11] [12]. Riparian degradation occurs as a result of disturbances from anthropogenic activities that occur at different levels, frequencies, and intensities exerting pressure on the riparian vegetation and biodiversity.
Healthy riparian forests are essential to the maintenance of water quality and biological integrity in surface water systems, and their destruction often leads to subsequent degradation of adjoining aquatic ecosystems [4] [13]. The establishment of agricultural fields and urban zones have been studied to cause fragmentation of the riparian vegetation thereby exposing the existing organisms to conditions of a different surrounding ecosystem [14] [15]. Between the new matrix and the remnant vegetation, alterations occur for instance, in the flow of radiation, wind, water, and nutrients what are referred to as the edge effects. These alterations bring about changes in species composition and abundance, vegetation structure and the ecological processes provided by the ecosystem [14] [16].
When significant differences exist between the surrounding matrix and the original vegetation, loss of local species of plants and animals can occur [17]. Some of the disturbances that occur as a result of land-use change that affects riparian communities include livestock grazing [18] [19], cultivation [13], hydrological modification [20]. Cultivation of crops along riparian areas causes excessive siltation and sedimentation [21] affecting the complexity and diversity of the plant species. Unregulated livestock grazing increases erosion and reduces plant vigor and alters the plant age structure and species diversity [7] [18]. However, livestock can also lead to an increase in the diversities of plant species through the transportation of seeds from distant areas and/or from the immediate riparian vegetation [22].
Njoro River is the main source of water for Lake Nakuru, a Ramsar site and an economic hub for the country since the Lake is within a National Park. Activities along with the riparian areas of this river, such as the increased rate of human and livestock population growth, unplanned settlements, increase in agricultural practices, selective cutting of riparian vegetation for charcoal, firewood, and construction is thought to have a negative impact on riparian vegetation species abundance and diversity and thus on the water quality of the river. The pressure for arable land has been on the rise within the catchment since 1994, causing a recession of forest cover and affecting the forest ecosystem integrity. Efforts have been made by various institutions and Community-Based Organizations (CBOs) to improve the overall water quality of the Njoro River since the year 2012 through the rehabilitation of the riparian areas. The extent of success of these efforts has not been well established or documented. It is against this background that this study was conceived to establish the link between adjacent land-use practices, and the riparian vegetation species composition, abundance and diversities. Kamweti River is located on the slopes of Mt. Kenya, which is a protected area by the National Park. Similar anthropogenic activities and challenges faced in the Njoro River riparian area characterize the downstream sections of Kamweti River riparian vegetation but on different levels. Therefore it will be used as a yardstick for evaluating the success of rehabilitation efforts in  [23]. Therefore, the main objective of this study was to determine the effect of adjacent land use (forestry, agriculture, built-up areas) on the structure and diversity of the riparian vegetation in the Njoro (frequently disturbed) and Kamweti (less disturbed) Rivers.
The hypothesis of the study was that anthropogenic disturbances along the Njoro River the riparian vegetation resulting from the intensive land use [18] [24] [25], will present changes in vegetation structure and diversity manifested as a lower abundance of vegetation types and fewer species.
The study of the two rivers offers an excellent study model for understanding vegetation changes associated with adjacent land uses. The extension of the geographic coverage of this type of study is also important since the structure and diversity of riparian communities are dependent upon a complex set of ecological factors (e.g., latitude and altitude) that are particular to each location and directly responsible for the diversity present in each area [4].

Study Sites Description
Njoro River (Figure 1 Kms discharging into Lake Nakuru (at 1750 m Above Sea Level), an internationally recognized Ramsar site. The river traverses agricultural areas, settlements, and urban areas [26]. The catchment has its rainfall peaks falling in April and August. The river is structured in a typical riffle-pool sequence [ Kamweti River (Figure 1(b)), the reference site, is located approximately latitude 0˚20'S to 0˚22'S and longitude 30˚25'E to 37˚30'E. The catchment is located on the southern slopes of Mount Kenya National Park in a well-preserved landscape consisting of rocky Afro-montane forests at higher elevations and highly diverse riverine forests in the valleys. Kamweti River is a tributary of the Thiba River [28]. The area has a cool, moist climate. The mean temperatures Open Journal of Ecology

Vegetation Data Collection and Analysis
A reconnaissance survey was first conducted to identify the various plant communities at various land uses in the Njoro and Kamweti Rivers. This plant survey was conducted after the wet season when most herbaceous species were apparent following [7]. Along each river, three sampling sites in the forest, agri- The size of these plots was the standardized maximum for data collection in riparian vegetation communities considering that the riparian vegetation exists as a thin plant community margin along with a river system that can intermittently expand through floodplains. The plants contained within these areas were then listed and their numbers estimated (abundance). The plants were also identified to the species level, and for those that were not easily identifiable in the field, specimens were identified using a plant specimen collection (herbarium) at Egerton University. Stream and forest canopy cover was estimated as a percentage.

Data Analysis
Data obtained from the Njoro and Kamweti River riparian areas were analyzed for plant species abundance and diversity. The plant species diversity was determined according to Shannon-Wiener Index [30]. This index considers both the where p i is the portion of ith taxon and Σ = the summation of all the values from the first to the ith taxon encountered. The Shannon diversity index ranges typically from 1.5 to 3.5 and rarely reaches 4.5 [31]. Species richness was determined by counting the number of species present. The plant species abundance and diversity between the Njoro and Kamweti riparian areas were compared by using a two-sample t-test at a 5% significant level based on the SPSS Statistics for Windows version 26 [32].
Sorenson's Index of Similarity was measured to express the similarity between communities in the different land uses categories [33] using the formula: where X is the number of species in one community, Y is the number of species in another community, and Z is the species common to both. The Sorenson's Index of Similarity, gives a value between 0 and 1. The closer the value is to 1, the more similar the communities are. Complete community overlap is equal to 1, and 0 represents complete community dissimilarity.

Riparian Vegetation Composition and Structure across Land Use
Three major land-use types identified in both study areas were forests, agricultural and built-up areas. A total of 145 plant species from 40 families were identified along the riparian zone of the Njoro River whereas Kamweti River riparian area, 110 plant species from 45 families were identified across the land uses. Vegetation structure and composition significantly differed across land use, particularly in the following vegetation abundance and diversity. The forest landscape of the Njoro River majorly consisted of shrub and tree species as shown in Figure 2. Tree and shrub species dominated the landscape from the Fabaceae family such as Tipuana tipu and Crotalaria agatiflora, Oleacea family such as Olea europaea subsp. Africana, and Euphorbiaceae families such as Podocarpus latifolius which had an open canopy, and shrubs species such as Rubus steudneri and Rumex orthoneurus were also noted to be dominant. Herbs such Ipomoea spp. and Cyclosorus parasiticus and a few grass and vine species were present.
In the agricultural area, herbs such as Bidens pilosa, Galinsoga parviflora, Vernonia newii, and Ageratum conyzoides from the Asteracea family dominated the site. Herbs also from the Solanaceae family such as Solanum incanum were noted. In the area, a belt of shrubs such as Lantana trifolia, and Hypericum revolutum also existed, and grass species from the Poaceae family such as Pennisetum clandestinum and Cynodon dactylon. A few species of trees were identified which included, Syzigium cordatum, Syzigium guineense, and Dombeya torrida. The area had a percent canopy cover of 0%.  Similar to the agricultural area, the built-up areas were dominated by herb species the common being from the Asteraceae family such as G. parviflora followed by tree species from the Fabacea and Myrtaceae Families were identified.
A few species of shrubs formed dense vegetation. Also, grass and vine species which were also identified.
The Kamweti River riparian vegetation structure is shown in Figure 3. The forested landscape had a 75% canopy cover. The area was dominated by herbs followed by trees. The common herbs were from the Balsaminaceae family such as Impatiens tinctoria, Cyperaceae families such as Cyperus immensus, and Asteraceae family such as the Senecio montuosun. The common tree species included Neoboutonia macrocalyx, Cyperus denudatus, and Pennisetum purpureum which are mostly present habitats with moist conditions. Also noted in these sites were few grass species from the Poaceae family and some vines.
Similar to the forested area, the agricultural areas were dominated by herbs from the Asteracea family followed by tree species. Most of the tree species identified in this site were from the Euphorbiaceae family e.g. Croton species, Macaranga capensis, and Neoboutonia macrocalyx. Herbs in this site were mostly from the Asteraceae family. Shrubs were also present with few types of grass represented from the Poaceae family. The agricultural area had the least canopy cover of 45%.
The built-up area had 60% canopy cover. Some of the tree species present were indigenous and some exotic. Similar to the agricultural area, the site was   (Table 1) showed that the highest Sorenson's Index of Similarity, in Kamweti River, was found between the forest area and built-up area (0.37) and the lowest was between the forest and agricultural area (0.26). In the Njoro River, Sorenson's Index of Similarity was in the range of 0.28 and 0.34. The highest similarity was found between the vegetation communities in the forest and the built-up areas (0.34) whereas the lowest was found between the forest and built-up area (0.28). Plant community similarities between the Njoro and Kamweti Riparian areas were highest between the built-up areas (0.29) while the forest areas and the agricultural areas recorded a similarity index of 0.24.

Riparian Plant Species Distribution
The dominant vegetation species in Njoro and Kamweti Rivers riparian zones across the different land use categories identified were from the Asteraceae family. The herbs dominant from this family in the Njoro River include Ageratum conyzoides, Bidens pilosa, and Conyza floribunda. From the same family, herbs such as Bidens pilosa and Senecio vulgaris and Shrubs such as Vernonia lasiopus, Tarchonanthus camphoratus, and Gutenbergia cordifolia were identified to be common in the Kamweti River.
The Fabacea family was well present along the Njoro and Kamweti rivers. In Njoro River, the vegetation type common from the Fabacea family were mostly tree species such as Acacia abyssinica, Acacia xanthophloea, Acacia mearnsii, and Acrocarpus sp. In the Kamweti River, shrubs such as Crotalaria agatiflora and trees such as Tipuana tipu were common. Poacea family (grasses) was represented was common in both the study area in which Cynodon dactylon and Pennisetum Clandestinum were common in Njoro river and Pennisetum clandestinum and Leersia hexandra identified in the Kamweti river. Euphorbiaceae was represented by tree species such as Croton megalocarpus and Ricinus communis in the Njoro River and Neoboutonia macrocalyx and Macaranga capensis in the Kamweti River which were common. Shrub species such as Plectranthus spp and herbs species such as Leonotis nepetifolia, Leucas martinicensis, were common in the Njoro River from the Lamiacea family whereas in Kamweti River, shrubs species such as Clerodendron johnstonii and Plectranthus species and herbs such as Leonotis mollissima were common.
Vegetation types that were uniquely identified in the Njoro River were from the families of Acanthaceae, Rubiaceae, Oleaceae, Hypericaceae, Verbenaceae, Rutaceae, Anacardiaceae, and Basellaceae whereas vegetation types unique to the Kamweti River were from the Balsaminaceae, Meliaceae, Apiaceae, Rosaceae, Commelinaceae, Thelypteridaceae, and Apocynaceae families.

Riparian Vegetation Composition and Structure across Land Use
Plant species distribution along the rivers studied is presented in Table 2. The variation in plant species composition and distribution along the two rivers studied were a result of the differences in land uses identified. Disturbance, whether natural or anthropogenic is an important agent as it contributes to the structure and composition of plant communities in an ecosystem [7]. For both river systems, the common types of land use activities noted were forests, built up areas, and agriculture. In this study, no quantitative assessment of the disturbances   [22]. In the Kamweti River riparian area, herbs were commonly followed by the trees. Tree and shrub species which were common in both study areas were from the Fabaceae, Malvaceae Open Journal of Ecology and Euphorbiacea families. Fabaceae has been found to be the most species rich family in most forest formations [34]. The species richness of these families identified in the study areas can be attributed to their good seed dispersal mechanisms which make them to be capable of colonizing different forest fragments, coupled with their ability to produce numerous seeds which eventually establish at suitable sites.
The diversity values for the forest areas of Njoro and Kamweti Rivers riparian zone, were 3.08, and 3.40, respectively. The higher species diversity in the Kamweti River riparian zone could be attributed to the protection status of the Mt.
Kenya National park from human disturbances such as logging, livestock grazing and wood fuel harvesting. The undisturbed plant community structure in these sites may reflect the influence of the natural, physical and chemical environment of the plant communities present as described by [35]. Tropical forests such as the Mt. Kenya forest, are usually characterized by high species richness and diversities [36] [37]. The high species diversities in these sites are an indication that the forest has ideal habitat for floral growth and reproduction due to the weather conditions which were witnessed during the sampling periods.
[38] and [39], on the riparian structure and functions pointed out that riparian vegetation buffers sediments and nutrients from agricultural runoff, stabilizes stream banks and provides shade that minimizes evaporation and moderates stream temperatures. This was observed at forested areas of the Njoro and Kamweti riparian zones which were less disturbed anthropogenically. Also noted was that the banks at these sites were stable and favorable moist habitats were available that supported diverse plant species such as N. macrocalyx, C. Denatus and P. Purpereum which were present in these sites.
Herb species dominated the agricultural areas of Njoro Rivers riparian zones followed by the shrub species whereas in the Kamweti Rivers riparian zone, herbs and vines were dominant with few tree species. The dominance of herbs over the other growth habits in the sites could be attributed to their short life cycle that enables them to resist the instability of the ecosystem [40]. The riparian vegetation in the sites were found to be altered, with some areas having small patches of tree cover or none, which has led to severe loss of original habitat. Due to intensive cultivation to the banks of the river, the sites appeared to be more disturbed as the process entails the clearance of the original vegetation and siltation. These impact the habitat negatively and eventually lead to a decrease in plant species diversity [7].
Along with cultivation, the agricultural areas were heavily disturbed by unre- the Njoro River where rare species were also found and the introduction of different climbers and herbs due to disturbance. The regular and frequent disturbances by livestock as observed in the Njoro River may have led to the establishment of the abnormally small tree sizes which were observed along the agricultural zone.
The built up areas along the Njoro River riparian zone were dominated by herbs and trees whereas the built-up areas of the Kamweti River riparian zone were dominated by invasive species of herbs such as Lantana camara, and followed by tree species. Some of the tree species identified in the built-up areas of the Kamweti River riparian zone were indigenous species such as Vangueria madagascariensis, and Cordia abbysinica, and some of the exotic tree species identified were Eucalyptus globulus and Grevillea robusta.
Built-up areas are associated with many anthropogenic activities within and close to the riparian vegetation which has resulted in the loss of biological integrity and edge effect which can be considered an ecological factor which affects riparian vegetation [9]. The effect that arises from the transition of the built-up area and riparian vegetation is that the microclimate of the continuous habitat is affected in terms of air temperature, soil moisture and light intensity. These changes can place organisms beyond their physiological tolerance limits, affecting their ecological performance (i.e., survival, growth, or reproduction) and permanence within the ecosystem [44].

Riparian Vegetation Distribution
In the study areas, plant species from the Asteracea family were present across the three categories of land use in the two river systems. Bidens pilosa, fastgrowing herb from the Asteracea family had a widespread distribution across the land use categories in the study areas. It behaves as a common weed of cultivated lands and pastures, but also of natural and semi-natural sites. B. pilosa, is a prolific seed producer and seeds can be easily dispersed attached to animals, birds, human clothes or by wind and water. It has also been reported as a contaminant in crop seeds and agricultural products [46]. It is regarded as a major weed in cultivated lands, forest margins, and secondary forests at elevations from sea level to 3600 m [46]. Ageratum conyzoides which was also common from the Asteracea family is known to be invasive in parts of Kenya, Tanzania and Uganda [47]. A. conyzoides is known to thrive in agricultural soils and is also very common in disturbed sites and degraded areas.
The Poacea family was also present in the three categories of land use in the study areas represented by species such as Cynodon dactylon, a stoloniferous grass widely naturalized in tropical and subtropical regions of the world. According to [48], the species is listed as one of the most "serious" agricultural and environmental weeds in the world. The presence of the grass species in the study areas was attributed to its ability to grow fast and that it spreads by seeds and stolons and rapidly colonizes new areas and grows forming dense mats. Studies by [49], highlighted that C. dactylon has the potential to alter ecosystem functions by altering fire regimes, hydrological cycles, biophysical dynamics, nutrients cycles, and community composition. The grass species is also very drought tolerant by virtue of rhizome survival through drought-induced dormancy over pe-  [50]. [51] also pointed out that roots of the C. dactylon community effectively enhanced the stability of riparian shallow soil and riverbank.
Pennisetum clandestinum was a common species of grass encountered in the study areas. It is known to be native to the highlands of Eastern Africa but it has been widely introduced elsewhere for forage and for soil conservation [48]. In well managed situations it does not generally spread very far but it is highly tolerant of grazing and mowing and can steadily invade poorly managed plantations resulting to loss of biodiversity. L. hexandra, a semi aquatic species found in a variety of moist, usually freshwater habitats [52] was common in the Kam- Ricinus communis from the Euphobiacea family is a fast-growing shrub or small tree common in the reaches of the Njoro River. It is a highly prolific and producer of toxic seeds, very adaptable to different environments and has been widely distributed by man. It is reported invasive in many countries particularly in the tropics and since dense thickets shade out native flora it is able to have negative impacts on biodiversity. Studies by [54] [55], in the Weed risk assessments, pointed out that due to its high invasive nature, its use as the bioenergy crop has been rejected in the USA and Caribbean. Macaranga capensis and Neoboutonia macrocalyx, a sub-canopy constituent in evergreen forest, usually in wet areas and along stream banks, was common in Kamweti River riparian zone. From the Lamiacea family, the Plectranthus species which occurs in a range of habitats were present in the study areas across the different land uses. [56] reported that Plectranthus species occurs mostly in disturbed areas.
Some of the vegetation families were uniquely identified in the Njoro River such as Acanthaceae, Rubiaceae, Oleaceae, Hypericaceae, Verbenaceae, Rutaceae, Anacardiaceae, and Basellaceae whereas vegetation types unique to the Kamweti River were from the Balsaminaceae, Meliaceae, Apiaceae, Rosaceae, Commelinaceae, Thelypteridaceae, and Apocynaceae families. The species from these families occurred as a single community or in few communities. Some of the species from the families are habitat-specific and encountered in the habitat conditioned by a certain level of few ecological factors, which enabled them to grow and reproduce within a definite range of environmental conditions [57].
In the study areas, it was observed that riparian zones found next to forest areas were in better conditions, and showed higher percentage values of canopy coverage. They were also characterized by higher quantities of leaf litter and or-ganic matter as well as several seedlings. Such variables, according to [13], indicate a more natural condition and low anthropogenic pressure. On the contrary, it was also observed in this study that in the riparian zones adjacent to areas of agriculture, the conditions observed were bad to moderate, which were attributed to soil compaction caused by grazing and agricultural activities, this was also affirmed by [58]. [7] also pointed out that the hoof action and trampling of soils in the river bank and nearby hill slopes by livestock causes siltation and sedimentation to descend to the low plains in the channel, leaving behind a degraded habitat unsuitable for the establishment of riparian plants and aquatic macrophytes affecting species richness and diversity.
It was also observed that the zones which were adjacent to built-up areas were heavily impacted. This affirmed the previous studies which showed that urbanization is among the land uses that have more severe consequences for riparian corridors [59] [60] [61]. In this study, it was noted that, soil compaction was the main impact associated with the built-up areas in both study areas. This has been known to affect the water quality of streams [62] and the ecological functioning of riparian zones by altering their flood capacity and habitat availability [61]. Studies by [63] [64], highlighted that paving and compaction increase the proportion of impervious surfaces, which are excellent indicators of the urbanization process intensity because they may enhance the degradation of fluvial ecosystems.

Conclusions
The study confirms the variations in plant abundance, composition, and diversities along both rivers studied which are attributed to the pressures caused by the different land use categories; forests, agriculture, and built-up areas. The similarity index was low due to the shrinkage of indigenous species in the agricultural and built-up areas.
The poor riparian ecological conditions along the studied rivers in the proximity of agricultural and built areas were the case, confirming the hypothesis that intensive land uses negatively affect riparian habitat conditions. Moreover, it was clear that, as the quality of the riparian habitat increases, a greater diversity of species and structural complexity in the community was found. The forested lands showed the highest potential for preserving plant species, structure, and function complexity in riparian habitats.