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Journal of Environment and Earth Science www.iiste.org 
ISSN 2224-3216 (Paper) ISSN 2225-0948 (Online) 
Vol.4, No.15, 2014 
Effect of Human Settlement and Altitude on Rangeland Browse 
Woody Species Biodiversity and Productivity in Kafta-Humera 
Woreda, Tigray, Ethiopia 
Teame G/Hiwot1* Tessema Zewdu2 Emiru Birhane3 
1.Adigrat University, College of Agriculture and Environmental Science, Ethiopia 
2.Haramaya University, College of Agriculture and Environmental Science, Ethiopia 
3.Mekele University, College of Agriculture and Environmental Science 
*Corresponding Author: Teame2004@gmail.com 
Abstract 
A research was conducted in Kafta-Humera districts of the Northern Ethiopia with the objective to determine the 
effect of human settlement on rangeland wood species productivity and biodiversity under three altitudinal 
ranges (600-1000, >1000-1400 and >1400-1800 m.a.s.l.) and along three distance intervals near (0-2 km), 
middle (2-4 km) and far (4-6 km) from settlement. The Statistical Package for Social Sciences (SPSS, version 
16.0, 2013) was used to analyze the soil and vegetation data. In the study districts, a total of 46 woody species 
were identified. Browse biomass of woody species in the low, middle and upper altitude categories were, 180.47, 
225.97 and 243.72 kg ha-1, respectively. Browse biomass of woody species near, middle and far distance from 
settlement were, 145.30, 228.03 and 276.824 kg ha-1 respectively. Woody species diversity was increased with 
increasing altitude, and was significantly lower near to settlement than middle and far distance. Far distance 
from settlement had significantly higher in organic carbon, available phosphorus and available potassium than 
middle and near distance from settlement. The upper altitude had significantly higher organic carbon, organic 
matter, available phosphorus and available potassium than the lower and middle altitude. In conclusion, the 
study area was highly dominated by the thorny shrubs woody species. This implies that there is undergoing 
reduction biodiversity and productivity degradation. Therefore, appropriate plan of biodiversity conservation 
such as establishing, designing and implementations of watershed management for physical and biological 
conservation should be planned to minimize loss of biodiversity. 
Keywords: Settlement, plant Species composition, plant species abundance, plant Species diversity, biomass 
production 
1. Introduction 
Plant species are highly damage due to high animal grazing pressure and human activities around human 
settlement areas (Brinkmann, 2009). Settlement influence the composition and abundance of woody plant 
species, patterns of soil nutrient redistribution and finally, these patterns influence the productivity and diversity 
of pastoral systems (Jefferey, 2007). 
In Kafta - Humera satellite imagery in 2000 (before resettlement) and 2007 (after resettlement) was taken 
to know the degree of change in land use and cover related to settlement. The results of the spatio-temporal 
analysis showed decreased in woodland by 25.8% and an increased in arable land by 21.8%, and in 2011 after 
ten years arable land increased almost by 100%, woody vegetation cover reduced by 42% (Moti et al., 2011). 
Settlements in Ethiopia have been studied widely. Though, most the studies have been focused more on 
the social and economic outcomes, planning and implementation (Pankhurst, 2005; Hammond, 2008). There has 
been rather not enough research undertaking at present time, to address some of the fundamental problems with 
the effect of human settlement on rangeland woody diversity, productivity and soil characteristics (Gebrehaweria, 
2011; Moti et al., 2011). 
Therefore this study was conducted with a general objective of determining the effect of human settlement 
on rangeland wood species productivity and biodiversity as well as soil characteristics in Kafta-Humera, in 
northern Ethiopia. And the specific objectives were: 
• To determine the effect of human settlement on woody species composition, plant abundance and 
species diversity under three altitudinal range and distance away from human settlement in Kafta- 
Humera district of northern Ethiopia; and 
• To investigate the effect of human settlement on rangeland woody biomass production and soil 
characteristics under three altitudinal ranges and distance away from human settlement in Kafta- 
Humera district of northern Ethiopia; 
2. Materials and methods 
2.1 Description of the Study Area 
The study was conducted in Kafta-Humera District of Tigray National Regional State in north-western Ethiopia 
38
Journal of Environment and Earth Science www.iiste.org 
ISSN 2224-3216 (Paper) ISSN 2225-0948 (Online) 
Vol.4, No.15, 2014 
39 
(Figure 1). 
Figure 1: Location of Kafta-Humera, the study area 
The District is located between 13040’and 14027’N, and 36027’and 37032’E. It covers an area of 160650 ha and 
its altitude ranges from 560 to 1849 m.a.s.l. The mean maximum temperature varied from 41.70C - 330C while 
the mean minimum temperature varied from 22.20C - 17.50C. The rainfall ranges from 448.8 -1102.5 mm 
(Hailesilassie, 1998; EARO, 2002). 
2.2 Methods of Data Collection 
Vegetation data were collected in a random sample area of 50 m x 50 m at each distance from settlements with in 
each altitude. Twelve quadrats were random taken at each distances, totaling 108 = (3 attitudes x 3 distances x 12 
quadrats). Three composite soil samples in each distance from settlements under each altitudinal ranges were 
pooled and yielding a total of 27 soil samples. 
2.3 Statistical Analysis 
Ordination of sampling sites under the three altitude and three distances from settlements was done by 
multivariate techniques, using Conoco (Ter Braak, 1997). Ordination of woody species was done by a Principal 
Component Analysis (PCA). In addition, the correlations of soil parameters with the woody species were done 
using a Redundancy Analysis (RDA). 
Woody species composition similarity among distance from settlements was estimated by the model 
Jaccard coefficient of similarity according to Krebs (1998). Biomass of selected browse woody species was 
estimated using the model of Petmak (1983). The diversity indices for woody species, plant abundance of each 
species and species evenness data were estimated using PAST software (Koleff et al., 2003). 
To test differences in woody species diversity, plant abundance, soil characteristics and biomass production, 
a General Linear Model (GLM) was applied using SPSS software (version.16). Moreover, Jaccard coefficient of 
similarity (Magurran, 2004) was used to test the differences on species compositions similarities along altitudinal 
range and distance from settlement. Tukey multiple comparison was used to test significant differences among 
the means. 
Soil analyses were done in Mekelle, Ethiopia Agricultural Research Center for organic carbon (OC), 
organic matter (OM), total nitrogen percentage (TN %), available potassium (K), available phosphorus (P), pH 
and percentage of soil textures (clay, silt and sand). 
3. Results and discussion 
3.1 Woody species composition 
In the study area a total of 46 woody species have been identified. In the lower altitude of the study area, a total 
of 27 woody species were identified. Acacia mellifera, Adonsonia digitata, Boswellia papyrifera, 
Dichrostachyus cinerea, Grewia bicolor and Termmalia brownii were the most dominant woody species for all 
distance. In the middle altitude, Acacia bussei, A. mellifera, D. cinerea, ziziphus abyssinica and Ziziphus spina-christi 
were the top five dominant encountered woody species for all distance. A. bussei, Carissa edulis, D.
Journal of Environment and Earth Science www.iiste.org 
ISSN 2224-3216 (Paper) ISSN 2225-0948 (Online) 
Vol.4, No.15, 2014 
cinerea, Dovyalis abyssinica, Maytenus senegalensis and Senna singueana were also common to the upper 
altitudes for all distance intervals (Table 1). 
The ordination result showed a clear separation of the 9 sites for the woody species, as the distance 
interval from settlement in each altitudinal ranges are clustered separately (Figure 2a). The first and the second 
ordination axis explained cumulatively 98% of the total variance extracted by the PCA. The result of the 
sampling site x soil parameter using RDA showed higher relationships with woody species on the first and 
second ordination axis with a correlation coefficient of 0.998 and 0.993, respectively. The first and second 
ordination axis explained 95.5% for the total cumulative variance of woody species to soil relation extracted by 
the RDA (Figure 2b). 
(a) (b) 
-1.0 1.5 
AVP 
Figure 2: Ordination diagram of the 9 sample sites for woody species (a) and sampling sites x soil parameters 
for woody species (b) under 3 altitudinal ranges(open circles = low altitude; filled circles = mid altitude and 
filled squares = high altitude) in Kafta-Humera, Northern Ethiopia. 
In the lower and middle altitude, A. mellifera and D. cinerea were the most dominant woody species near to the 
settlements. A. bussei, D. cinerea, D. abyssinica and M. senegalensis were the common woody species to the 
upper altitude near to the settlement (Table 1). Most of the dominant woody species in the study area were 
thorny woody species and comparatively their relative abundance was higher than of the other woody species. 
They can, therefore, be considered as the best indicators of intensively degraded rangelands of the area. This 
finding was in agreement with the study of Moti et al. (2011). 
40 
-0.5 1.5 
-1.0 1.0 
-0.6 1.0 
pH 
C OM 
AVK 
TN 
Sand 
Silt 
Clay
Journal of Environment and Earth Science www.iiste.org 
ISSN 2224-3216 (Paper) ISSN 2225-0948 (Online) 
Vol.4, No.15, 2014 
Table 1: List of woody species with their relative abundance (N0.25 ha-1) under three altitudes (m.a.s.l.) and 
three distances from human settlement (km) in Kafta-Humera, northern Ethiopia 
41 
Woody species 
Altitudinal Ranges 
600-1000 >1000-1400 >1400-1800 
0-2 2-4 4-6 0-2 2-4 4-6 0-2 2-4 4-6 
Acacia abyssinica 0 0 0 5.4 11.3 8.4 7.4 9.3 15 
Acacia bussei 1 0 7.3 13 7.8 14 16 2 12 
Acacia mellifera 15.2 11.2 16.3 14 16.6 8.2 5.7 3 2 
Acacia nubica 0 0 0 0 6 0 0 0 0 
Adonsonia digitata 3 3 1 0 0 0 0 0 0 
Albizia amara 0 0 0 4.5 4.7 7.4 0 0 0 
Anogeissus leiocarpa 5.3 12.4 4.8 10.5 9.2 7.8 5.2 8.6 7.1 
Balanitesa egyptiaca 3.8 6 9.2 13.3 0 8.5 0 9 0 
Bosica angustifolia 4 0 0 0 7 7.5 0 3.5 4 
Boswellia papyrifera 12 8.64 7.6 9.4 9.5 9.5 0 0 0 
Bridelia cathartica 0 0 0 2 0 0 9 12.5 6.8 
Capparis tomentosa 0 0 0 0 0 0 5.5 12 7 
Carissa edulis 0 0 0 0 0 0 7 13 16 
Combretum collinum 9.4 12.1 6.1 0 8.7 8 0 0 0 
Combretum hartmannianum 6.7 6.8 11.8 13.7 18 0 6 6.1 6.3 
Combretum Sp1. 4.5 6.5 18 0 0 0 10 8.3 9.9 
Commiphora africana 1 0 9.6 0 0 0 0 0 0 
Dalbergja melanoxyylon 6.3 14.7 5.9 13.8 10 10 0 0 0 
Dichrostachys cinerea 17.1 18.5 21.1 18.8 17.1 19 12.7 27.5 23 
Dodonea angustifolia 0 0 0 0 0 0 6.5 8.1 13 
Dovyalis abyssinica 0 0 7 8 15.1 9.4 18 9.6 11 
Erica arborea 2 0 0 0 0 0 0 0 0 
Ficus glumosa 0 0 0 0 8 8 0 0 0 
Ficus sycomorus 0 0 0 0 0 0 0 10.5 0 
Gardenia ternifolia 0 0 0 0 0 0 4.5 6.1 6 
Glumosa pittos 0 10.1 4 11 0 0 0 0 0 
Grewia bicolor 0 27.5 11 4 5.7 8.1 0 0 0 
Lannea frutcosa 3.7 6 7 9.5 6 5.7 5 7.8 6 
Lonchocarpus laxiflorus 0 0 0 0 0 0 0 6 0 
Maytenus obscura 0 0 0 0 0 0 4.3 9.5 0 
Maytenus senegalensis 0 0 0 0 0 0 12.7 12.4 23 
Nuxia congesta 0 8 2 0 5 4 0 6.3 1 
Piliostigma thonningii 0 0 0 0 7.5 9 0 0 0 
Pterocarpus lucens 0 0 8 0 0 0 0 0 0 
Pterollobiu stellatum 0 0 0 0 0 0 5.8 6 8 
Rhus nataliensis 0 0 0 0 0 0 5.1 7 7.4 
Senna singueana 0 0 0 0 0 0 12 13.3 8 
Table 1 continued 
Sterculia africana 4 6.5 0 7 0 11 0 0 0 
Sterospermum kunthianum 1 2.5 10 0 8.3 11 4.6 6 10 
Tamarindus indica 0 4 9.2 8 12.3 10 0 0 0 
Termmalia brownii 9 8.8 5.3 0 0 0 0 0 0 
Ximenia americana 6 0 3.5 8.3 0 0 5.3 10 7.3 
Ziziphus abyssinica 0 6 0 7 21.5 10 2.5 5.5 7.3 
Ziziphus spina-christi 7.5 5 10.8 12.3 9 11 3.6 8.8 12 
Ziziphus mucronata 0 0 0 0 0 0 3 0 11 
3.2 Browse species biomass production 
3.2.1 Effect of distance on browse species biomass at different altitudinal ranges 
Leaf browse biomass of woody species in the low altitude, far distance from settlement was significantly higher 
than near distance to settlement. In the middle altitude, leaf browse biomass of woody species near to settlement 
was significantly lower than of the other two distances. Leaf biomass of woody species in the upper altitude was 
significantly increased with distance from settlement increased (Table 2). This might be related with the 
browsing intensity of cattle and goats across to distance from settlement area.
Journal of Environment and Earth Science www.iiste.org 
ISSN 2224-3216 (Paper) ISSN 2225-0948 (Online) 
Vol.4, No.15, 2014 
3.2.2 The effect of altitude on browse woody species biomass 
In all altitude, browse biomass were significantly increased with increased altitude (Table 2; F2,99 = 11.97, P < 
0.000). Browse biomass of woody species in the low, middle and upper altitude were, 180.47, 225.97 and 243.72 
kg ha-1, respectively (Table 2). 
3.2.3 The effect of distance on browse species biomass 
Browse biomass of woody species were significantly increased with distance increased from settlement (Table 2; 
F2,99 = 49.70, P < 0.000). Browse biomass of woody species near, middle and far distance from settlement were, 
145.30, 228.03 and 276.824 kg ha-1, respectively (Table 2). This result could be related to the decreasing of 
browsing intensity animals and human activities with increasing distance from settlement. 
Table 2: Effect of altitude and distances on Shannon diversity index, evenness, total plant abundance (N 0.25ha- 
1), species richness and browse biomass (kg/ha) of woody species in Kafta-Humera rangelands, northern 
Ethiopia 
diversity Evenness Plant abundance Species richness biomass 
42 
Altitudinal ranges 
600-1000 
0-2 1.59b 0.812a 60.50b 6.58b 130.52b 
2-4 1.86a 0.842a 85.67a 7.75b 177.17ba 
4-6 2.01a 0.785a 88.17a 9.67a 233.72a 
>1000-1400 
0-2 1.71b 0.866a 104.25b 7.16b 146.053b 
2-4 2.17a 0.896a 175.42a 10.58a 244.835a 
4-6 2.34a 0.899a 190.17a 11.58a 287.032a 
>1400-1800 
0-2 2.08b 0.837b 130.58c 9.50c 159.342c 
2-4 2.30a 0.896a 187.83b 11.00a 262.094b 
4-6 2.30a 0.918a 209.00a 11.00a 309.721a 
Altitude (A) 
F (df= 2,99 ) 25.73 17.80 93.71 28.32 11.97 
P 0.000 0.000 0.000 0.000 0.000 
Distance (D) 
F (df= 2,99 ) 30.51 4.31 40.11 40.08 49.703 
P 0.000 0.016 0.000 0.000 0.000 
(A) * (D) 
F (df= 4,99 ) 2.24 2.78 3.21 4.30 1.03 
P 0.07 0.031 0.016 0.003 0.393 
Adjusted R2 0.515 0.307 0.718 0.577 0.528 
Df = degree of freedom, F-ratio = F test value, P value = probability value, A = Altitude, D = Distance. Means 
with the same letter in columns are not significantly different at P ≤ 0.05 
3.2.4 Woody species similarity 
In all altitude, species similarity was high between far and middle distance from settlement with in the same 
altitude range. less species similarity was recorded between low and high altitude distance intervals from 
settlement (Table 3).
Journal of Environment and Earth Science www.iiste.org 
ISSN 2224-3216 (Paper) ISSN 2225-0948 (Online) 
Vol.4, No.15, 2014 
Table 3: .Jaccard coefficient of similarity for woody species under three altitudes (m.a.s.l.) and three distance 
from human settlement (km) in Kafta-Humera rangelands, northern Ethiopia 
Altitudinal ranges 
600-1000 >1000-1400 >1400-1800 
0-2 2-4 4-6 0-2 2-4 4-6 0-2 2-4 4-6 
43 
600-1000 
0-2 - 
2-4 0.54 - 
4-6 0.67 0.68 - 
>1000-1400 
0-2 0.43 0.43 0.33 - 
2-4 0.42 0.42 0.43 0.54 - 
4-6 0.45 0.45 0.31 0.42 0.31 - 
>1400-1800 
0-2 0.28 0.29 0.33 0.38 0.31 0.27 - 
2-4 0.29 0.26 0.29 0.37 0.34 0.34 0.80 - 
4-6 0.31 0.32 0.33 0.31 0.34 0.30 0.84 0.85 - 
3.4. Soil Parameters 
3.4.1. The effect of altitudinal and distance on soil Parameters 
3.4.1.1. The effect of distance on soil Parameters at different altitudinal ranges. 
In the low altitude range, far distance interval was significantly higher in percentage of organic carbon and 
organic matter as well as available phosphorus and the percents of sand contents than near distance to settlement. 
In the middle altitude percentage of organic carbon and organic matter of soil were significantly lower in near 
distance than far distance from settlement. In the upper altitude, percentage of organic carbon and organic matter, 
available of phosphorus and available potassium of soil contents were recorded significantly higher in the far 
distance from settlement than near and middle distance from settlement (Table 4). 
3.4.1.2. The effect of altitude on soil Parameters 
Sand soil content had showed significant decreased with altitude increasing (Table 4; F2,18 = 33. 07, P < 0.000). 
Whereas, clay soil content was increased with altitude increasing (Table 4; F2,18 = 52.33, P < 0.000). In the lower 
altitude, pH value was recorded significantly higher than upper and lower altitudes (Table 4; F2,18 = 6.16, P < 
0.009). This is related to the fact that the pH value and sand soil increase with altitude decreases but clay soil 
content increase with altitude increase Abreha et al., (2012). The higher sand content and pH value under lower 
altitude is probably caused by increasing run off and soil erosion, and soil compacted. Nitrogen percentage under 
low altitude was significantly difference from other altitudes. Under the upper altitude, organic carbon, organic 
matter, available phosphorus and available potassium had significant higher as compared to other two altitude 
ranges (Table 4). This is supported by the finding of Getachew et al., (2007) in Borana rangelands, Ethiopia and 
Abreha et al., (2012) in Tsegede Highlands, Northern Ethiopia. This results probably due to the availability of 
organic matter, higher standing biomass, soil moister and rainfall increasing with altitude range increasing. 
3.4.1.3.The effect of distance on soil Parameters 
In near distance to settlement, sand soil content had showed significantly higher than far distance from 
settlement (Table 4; F2,18 = 3.65, P < 0.047). This result may be related to the high degree of soil erosion, high 
grazing pressures and human activities near to settlement than far distance from settlement. Organic matter and 
organic carbon had significant increased with distance increased from settlement. In far distance from settlement, 
available phosphorus and potassium were recorded significantly higher than that of the near and middle distance 
from settlement. Nitrogen Percentage had significantly higher in far distance from settlement than middle 
distances from settlement (Table 4; F2,18 = 4.97, P < 0.019).
Journal of Environment and Earth Science www.iiste.org 
ISSN 2224-3216 (Paper) ISSN 2225-0948 (Online) 
Vol.4, No.15, 2014 
Table 4: Effect of altitudinal ranges and distance interval away from settlements (km) on physical and chemical 
soil Parameters in Kafta-Humera rangelands, northern Ethiopia 
pH OC (%) OM (%) AVP.ppm AVK.ppm TN (%) Sand (%) Silt (%) Clay 
44 
(%) 
Mean 
Altitude (m.a.s.l) 
600-1000 
0-2 7.45a 1.06b 1.83b 0.61b 1.42a 0.09a 53.33a 16.33b 30.33a 
2-4 7.22a 1.50ba 2.58ba 0.99ba 1.43a 0.08a 48.67ba 26.67a 24.67a 
4-6 7.09a 2.10a 3.62a 1.28a 1.96a 0.10a 42.00b 27.00a 31.00a 
>1000-1400 
0-2 6.86a 0.95b 1.64b 0.92a 1.57a 0.163a 45.67a 22.33a 32.00a 
2-4 6.73a 1.34ba 2.32ba 0.95a 1.78a 0.129a 36.33a 16.33a 47.33a 
4-6 6.60a 2.03a 3.51a 1.22a 2.34a 0.269a 28.67a 23.33a 48.00a 
>1400-1800 
0-2 6.87a 1.59b 2.75 b 1.44b 1.87b 0.210a 17.67a 21.33a 61.00a 
2-4 6.71a 1.77b 3.06b 1.09b 2.41b 0.206a 20.67a 18.33a 61.00a 
4-6 6.53a 2.57a 4.44 a 2.10a 3.39a 0.311a 16.33a 23.00a 60.67a 
Altitude (A) 
F (df =2,18) 6.16 10.43 10.52 19.07 25.95 14.32 33.07 1.47 52.33 
p 0.009 0.001 0.001 0.000 0.000 0.000 0.000 0.255 0.000 
Distance (D) 
F (df 
=2,18), 
1.66 35.97 36.21 18.17 25.98 4.97 3.65 4.03 1.50 
p 0.219 0.000 0.000 0.000 0.000 0.019 0.047 0.036 0.25 
(A) * (D) 
F (df 
=4,18), 
0.02 0.22 0.23 3.75 2.44 0.99 0.85 4.35 2.38 
p 0.999 0.922 0.92 0.022 0.084 0.441 0.513 0.012 0.09 
Adjusted R2 0.229 0.767 0.769 0.758 0.802 0.57 0.726 0.44 0.807 
OC = Organic carbon; OM = Organic matter; AVP = Available phosphorus; AVK = Available potassium; TN = 
Total nitrogen. 
Means with the same letters in columns are not significantly different at P ≤ 0.05 
4. CONCLUSION 
In the study districts, a total of 46 species of woody species were identified. A. bussei, A. mellifera, Anogeissus 
leiocarpa, Combretum hartmannianum, D. cinerea, Lannea frutcosa and Z. spina-christi were the common 
dominant species for all altitude and distance. In all altitude, woody species diversity and abundance in far 
distance to settlements were significantly higher than near distance. In the lower altitude, all woody diversity 
parameters had significantly lower. Sand and pH value had also significantly higher but soil clay was 
significantly lower as compared to the middle and upper altitudinal ranges. Far distance from settlement had 
significantly higher in organic carbon, organic matter, available phosphorus and available potassium than to 
middle and near distance. The upper altitude had showed significantly higher in organic carbon, organic matter, 
available phosphorus and available potassium as compared to the lower and middle altitude. Under the present 
soil status, biodiversity and productivity circumstances of the areas near to settlement and middle distance 
intervals from settlement, preservation or return of habitats should be of greater concern because the best way to 
minimize biodiversity loss is to maintain the integrity of ecosystem function. Research related to rehabilitation 
and possible restoration strategies through soil seed bank under various altitudinal ranges and settlement areas 
should be considered. 
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45
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Effect of human settlement and altitude on rangeland browse woody species biodiversity and productivity in kafta humera woreda, tigray, ethiopia

  • 1. Journal of Environment and Earth Science www.iiste.org ISSN 2224-3216 (Paper) ISSN 2225-0948 (Online) Vol.4, No.15, 2014 Effect of Human Settlement and Altitude on Rangeland Browse Woody Species Biodiversity and Productivity in Kafta-Humera Woreda, Tigray, Ethiopia Teame G/Hiwot1* Tessema Zewdu2 Emiru Birhane3 1.Adigrat University, College of Agriculture and Environmental Science, Ethiopia 2.Haramaya University, College of Agriculture and Environmental Science, Ethiopia 3.Mekele University, College of Agriculture and Environmental Science *Corresponding Author: Teame2004@gmail.com Abstract A research was conducted in Kafta-Humera districts of the Northern Ethiopia with the objective to determine the effect of human settlement on rangeland wood species productivity and biodiversity under three altitudinal ranges (600-1000, >1000-1400 and >1400-1800 m.a.s.l.) and along three distance intervals near (0-2 km), middle (2-4 km) and far (4-6 km) from settlement. The Statistical Package for Social Sciences (SPSS, version 16.0, 2013) was used to analyze the soil and vegetation data. In the study districts, a total of 46 woody species were identified. Browse biomass of woody species in the low, middle and upper altitude categories were, 180.47, 225.97 and 243.72 kg ha-1, respectively. Browse biomass of woody species near, middle and far distance from settlement were, 145.30, 228.03 and 276.824 kg ha-1 respectively. Woody species diversity was increased with increasing altitude, and was significantly lower near to settlement than middle and far distance. Far distance from settlement had significantly higher in organic carbon, available phosphorus and available potassium than middle and near distance from settlement. The upper altitude had significantly higher organic carbon, organic matter, available phosphorus and available potassium than the lower and middle altitude. In conclusion, the study area was highly dominated by the thorny shrubs woody species. This implies that there is undergoing reduction biodiversity and productivity degradation. Therefore, appropriate plan of biodiversity conservation such as establishing, designing and implementations of watershed management for physical and biological conservation should be planned to minimize loss of biodiversity. Keywords: Settlement, plant Species composition, plant species abundance, plant Species diversity, biomass production 1. Introduction Plant species are highly damage due to high animal grazing pressure and human activities around human settlement areas (Brinkmann, 2009). Settlement influence the composition and abundance of woody plant species, patterns of soil nutrient redistribution and finally, these patterns influence the productivity and diversity of pastoral systems (Jefferey, 2007). In Kafta - Humera satellite imagery in 2000 (before resettlement) and 2007 (after resettlement) was taken to know the degree of change in land use and cover related to settlement. The results of the spatio-temporal analysis showed decreased in woodland by 25.8% and an increased in arable land by 21.8%, and in 2011 after ten years arable land increased almost by 100%, woody vegetation cover reduced by 42% (Moti et al., 2011). Settlements in Ethiopia have been studied widely. Though, most the studies have been focused more on the social and economic outcomes, planning and implementation (Pankhurst, 2005; Hammond, 2008). There has been rather not enough research undertaking at present time, to address some of the fundamental problems with the effect of human settlement on rangeland woody diversity, productivity and soil characteristics (Gebrehaweria, 2011; Moti et al., 2011). Therefore this study was conducted with a general objective of determining the effect of human settlement on rangeland wood species productivity and biodiversity as well as soil characteristics in Kafta-Humera, in northern Ethiopia. And the specific objectives were: • To determine the effect of human settlement on woody species composition, plant abundance and species diversity under three altitudinal range and distance away from human settlement in Kafta- Humera district of northern Ethiopia; and • To investigate the effect of human settlement on rangeland woody biomass production and soil characteristics under three altitudinal ranges and distance away from human settlement in Kafta- Humera district of northern Ethiopia; 2. Materials and methods 2.1 Description of the Study Area The study was conducted in Kafta-Humera District of Tigray National Regional State in north-western Ethiopia 38
  • 2. Journal of Environment and Earth Science www.iiste.org ISSN 2224-3216 (Paper) ISSN 2225-0948 (Online) Vol.4, No.15, 2014 39 (Figure 1). Figure 1: Location of Kafta-Humera, the study area The District is located between 13040’and 14027’N, and 36027’and 37032’E. It covers an area of 160650 ha and its altitude ranges from 560 to 1849 m.a.s.l. The mean maximum temperature varied from 41.70C - 330C while the mean minimum temperature varied from 22.20C - 17.50C. The rainfall ranges from 448.8 -1102.5 mm (Hailesilassie, 1998; EARO, 2002). 2.2 Methods of Data Collection Vegetation data were collected in a random sample area of 50 m x 50 m at each distance from settlements with in each altitude. Twelve quadrats were random taken at each distances, totaling 108 = (3 attitudes x 3 distances x 12 quadrats). Three composite soil samples in each distance from settlements under each altitudinal ranges were pooled and yielding a total of 27 soil samples. 2.3 Statistical Analysis Ordination of sampling sites under the three altitude and three distances from settlements was done by multivariate techniques, using Conoco (Ter Braak, 1997). Ordination of woody species was done by a Principal Component Analysis (PCA). In addition, the correlations of soil parameters with the woody species were done using a Redundancy Analysis (RDA). Woody species composition similarity among distance from settlements was estimated by the model Jaccard coefficient of similarity according to Krebs (1998). Biomass of selected browse woody species was estimated using the model of Petmak (1983). The diversity indices for woody species, plant abundance of each species and species evenness data were estimated using PAST software (Koleff et al., 2003). To test differences in woody species diversity, plant abundance, soil characteristics and biomass production, a General Linear Model (GLM) was applied using SPSS software (version.16). Moreover, Jaccard coefficient of similarity (Magurran, 2004) was used to test the differences on species compositions similarities along altitudinal range and distance from settlement. Tukey multiple comparison was used to test significant differences among the means. Soil analyses were done in Mekelle, Ethiopia Agricultural Research Center for organic carbon (OC), organic matter (OM), total nitrogen percentage (TN %), available potassium (K), available phosphorus (P), pH and percentage of soil textures (clay, silt and sand). 3. Results and discussion 3.1 Woody species composition In the study area a total of 46 woody species have been identified. In the lower altitude of the study area, a total of 27 woody species were identified. Acacia mellifera, Adonsonia digitata, Boswellia papyrifera, Dichrostachyus cinerea, Grewia bicolor and Termmalia brownii were the most dominant woody species for all distance. In the middle altitude, Acacia bussei, A. mellifera, D. cinerea, ziziphus abyssinica and Ziziphus spina-christi were the top five dominant encountered woody species for all distance. A. bussei, Carissa edulis, D.
  • 3. Journal of Environment and Earth Science www.iiste.org ISSN 2224-3216 (Paper) ISSN 2225-0948 (Online) Vol.4, No.15, 2014 cinerea, Dovyalis abyssinica, Maytenus senegalensis and Senna singueana were also common to the upper altitudes for all distance intervals (Table 1). The ordination result showed a clear separation of the 9 sites for the woody species, as the distance interval from settlement in each altitudinal ranges are clustered separately (Figure 2a). The first and the second ordination axis explained cumulatively 98% of the total variance extracted by the PCA. The result of the sampling site x soil parameter using RDA showed higher relationships with woody species on the first and second ordination axis with a correlation coefficient of 0.998 and 0.993, respectively. The first and second ordination axis explained 95.5% for the total cumulative variance of woody species to soil relation extracted by the RDA (Figure 2b). (a) (b) -1.0 1.5 AVP Figure 2: Ordination diagram of the 9 sample sites for woody species (a) and sampling sites x soil parameters for woody species (b) under 3 altitudinal ranges(open circles = low altitude; filled circles = mid altitude and filled squares = high altitude) in Kafta-Humera, Northern Ethiopia. In the lower and middle altitude, A. mellifera and D. cinerea were the most dominant woody species near to the settlements. A. bussei, D. cinerea, D. abyssinica and M. senegalensis were the common woody species to the upper altitude near to the settlement (Table 1). Most of the dominant woody species in the study area were thorny woody species and comparatively their relative abundance was higher than of the other woody species. They can, therefore, be considered as the best indicators of intensively degraded rangelands of the area. This finding was in agreement with the study of Moti et al. (2011). 40 -0.5 1.5 -1.0 1.0 -0.6 1.0 pH C OM AVK TN Sand Silt Clay
  • 4. Journal of Environment and Earth Science www.iiste.org ISSN 2224-3216 (Paper) ISSN 2225-0948 (Online) Vol.4, No.15, 2014 Table 1: List of woody species with their relative abundance (N0.25 ha-1) under three altitudes (m.a.s.l.) and three distances from human settlement (km) in Kafta-Humera, northern Ethiopia 41 Woody species Altitudinal Ranges 600-1000 >1000-1400 >1400-1800 0-2 2-4 4-6 0-2 2-4 4-6 0-2 2-4 4-6 Acacia abyssinica 0 0 0 5.4 11.3 8.4 7.4 9.3 15 Acacia bussei 1 0 7.3 13 7.8 14 16 2 12 Acacia mellifera 15.2 11.2 16.3 14 16.6 8.2 5.7 3 2 Acacia nubica 0 0 0 0 6 0 0 0 0 Adonsonia digitata 3 3 1 0 0 0 0 0 0 Albizia amara 0 0 0 4.5 4.7 7.4 0 0 0 Anogeissus leiocarpa 5.3 12.4 4.8 10.5 9.2 7.8 5.2 8.6 7.1 Balanitesa egyptiaca 3.8 6 9.2 13.3 0 8.5 0 9 0 Bosica angustifolia 4 0 0 0 7 7.5 0 3.5 4 Boswellia papyrifera 12 8.64 7.6 9.4 9.5 9.5 0 0 0 Bridelia cathartica 0 0 0 2 0 0 9 12.5 6.8 Capparis tomentosa 0 0 0 0 0 0 5.5 12 7 Carissa edulis 0 0 0 0 0 0 7 13 16 Combretum collinum 9.4 12.1 6.1 0 8.7 8 0 0 0 Combretum hartmannianum 6.7 6.8 11.8 13.7 18 0 6 6.1 6.3 Combretum Sp1. 4.5 6.5 18 0 0 0 10 8.3 9.9 Commiphora africana 1 0 9.6 0 0 0 0 0 0 Dalbergja melanoxyylon 6.3 14.7 5.9 13.8 10 10 0 0 0 Dichrostachys cinerea 17.1 18.5 21.1 18.8 17.1 19 12.7 27.5 23 Dodonea angustifolia 0 0 0 0 0 0 6.5 8.1 13 Dovyalis abyssinica 0 0 7 8 15.1 9.4 18 9.6 11 Erica arborea 2 0 0 0 0 0 0 0 0 Ficus glumosa 0 0 0 0 8 8 0 0 0 Ficus sycomorus 0 0 0 0 0 0 0 10.5 0 Gardenia ternifolia 0 0 0 0 0 0 4.5 6.1 6 Glumosa pittos 0 10.1 4 11 0 0 0 0 0 Grewia bicolor 0 27.5 11 4 5.7 8.1 0 0 0 Lannea frutcosa 3.7 6 7 9.5 6 5.7 5 7.8 6 Lonchocarpus laxiflorus 0 0 0 0 0 0 0 6 0 Maytenus obscura 0 0 0 0 0 0 4.3 9.5 0 Maytenus senegalensis 0 0 0 0 0 0 12.7 12.4 23 Nuxia congesta 0 8 2 0 5 4 0 6.3 1 Piliostigma thonningii 0 0 0 0 7.5 9 0 0 0 Pterocarpus lucens 0 0 8 0 0 0 0 0 0 Pterollobiu stellatum 0 0 0 0 0 0 5.8 6 8 Rhus nataliensis 0 0 0 0 0 0 5.1 7 7.4 Senna singueana 0 0 0 0 0 0 12 13.3 8 Table 1 continued Sterculia africana 4 6.5 0 7 0 11 0 0 0 Sterospermum kunthianum 1 2.5 10 0 8.3 11 4.6 6 10 Tamarindus indica 0 4 9.2 8 12.3 10 0 0 0 Termmalia brownii 9 8.8 5.3 0 0 0 0 0 0 Ximenia americana 6 0 3.5 8.3 0 0 5.3 10 7.3 Ziziphus abyssinica 0 6 0 7 21.5 10 2.5 5.5 7.3 Ziziphus spina-christi 7.5 5 10.8 12.3 9 11 3.6 8.8 12 Ziziphus mucronata 0 0 0 0 0 0 3 0 11 3.2 Browse species biomass production 3.2.1 Effect of distance on browse species biomass at different altitudinal ranges Leaf browse biomass of woody species in the low altitude, far distance from settlement was significantly higher than near distance to settlement. In the middle altitude, leaf browse biomass of woody species near to settlement was significantly lower than of the other two distances. Leaf biomass of woody species in the upper altitude was significantly increased with distance from settlement increased (Table 2). This might be related with the browsing intensity of cattle and goats across to distance from settlement area.
  • 5. Journal of Environment and Earth Science www.iiste.org ISSN 2224-3216 (Paper) ISSN 2225-0948 (Online) Vol.4, No.15, 2014 3.2.2 The effect of altitude on browse woody species biomass In all altitude, browse biomass were significantly increased with increased altitude (Table 2; F2,99 = 11.97, P < 0.000). Browse biomass of woody species in the low, middle and upper altitude were, 180.47, 225.97 and 243.72 kg ha-1, respectively (Table 2). 3.2.3 The effect of distance on browse species biomass Browse biomass of woody species were significantly increased with distance increased from settlement (Table 2; F2,99 = 49.70, P < 0.000). Browse biomass of woody species near, middle and far distance from settlement were, 145.30, 228.03 and 276.824 kg ha-1, respectively (Table 2). This result could be related to the decreasing of browsing intensity animals and human activities with increasing distance from settlement. Table 2: Effect of altitude and distances on Shannon diversity index, evenness, total plant abundance (N 0.25ha- 1), species richness and browse biomass (kg/ha) of woody species in Kafta-Humera rangelands, northern Ethiopia diversity Evenness Plant abundance Species richness biomass 42 Altitudinal ranges 600-1000 0-2 1.59b 0.812a 60.50b 6.58b 130.52b 2-4 1.86a 0.842a 85.67a 7.75b 177.17ba 4-6 2.01a 0.785a 88.17a 9.67a 233.72a >1000-1400 0-2 1.71b 0.866a 104.25b 7.16b 146.053b 2-4 2.17a 0.896a 175.42a 10.58a 244.835a 4-6 2.34a 0.899a 190.17a 11.58a 287.032a >1400-1800 0-2 2.08b 0.837b 130.58c 9.50c 159.342c 2-4 2.30a 0.896a 187.83b 11.00a 262.094b 4-6 2.30a 0.918a 209.00a 11.00a 309.721a Altitude (A) F (df= 2,99 ) 25.73 17.80 93.71 28.32 11.97 P 0.000 0.000 0.000 0.000 0.000 Distance (D) F (df= 2,99 ) 30.51 4.31 40.11 40.08 49.703 P 0.000 0.016 0.000 0.000 0.000 (A) * (D) F (df= 4,99 ) 2.24 2.78 3.21 4.30 1.03 P 0.07 0.031 0.016 0.003 0.393 Adjusted R2 0.515 0.307 0.718 0.577 0.528 Df = degree of freedom, F-ratio = F test value, P value = probability value, A = Altitude, D = Distance. Means with the same letter in columns are not significantly different at P ≤ 0.05 3.2.4 Woody species similarity In all altitude, species similarity was high between far and middle distance from settlement with in the same altitude range. less species similarity was recorded between low and high altitude distance intervals from settlement (Table 3).
  • 6. Journal of Environment and Earth Science www.iiste.org ISSN 2224-3216 (Paper) ISSN 2225-0948 (Online) Vol.4, No.15, 2014 Table 3: .Jaccard coefficient of similarity for woody species under three altitudes (m.a.s.l.) and three distance from human settlement (km) in Kafta-Humera rangelands, northern Ethiopia Altitudinal ranges 600-1000 >1000-1400 >1400-1800 0-2 2-4 4-6 0-2 2-4 4-6 0-2 2-4 4-6 43 600-1000 0-2 - 2-4 0.54 - 4-6 0.67 0.68 - >1000-1400 0-2 0.43 0.43 0.33 - 2-4 0.42 0.42 0.43 0.54 - 4-6 0.45 0.45 0.31 0.42 0.31 - >1400-1800 0-2 0.28 0.29 0.33 0.38 0.31 0.27 - 2-4 0.29 0.26 0.29 0.37 0.34 0.34 0.80 - 4-6 0.31 0.32 0.33 0.31 0.34 0.30 0.84 0.85 - 3.4. Soil Parameters 3.4.1. The effect of altitudinal and distance on soil Parameters 3.4.1.1. The effect of distance on soil Parameters at different altitudinal ranges. In the low altitude range, far distance interval was significantly higher in percentage of organic carbon and organic matter as well as available phosphorus and the percents of sand contents than near distance to settlement. In the middle altitude percentage of organic carbon and organic matter of soil were significantly lower in near distance than far distance from settlement. In the upper altitude, percentage of organic carbon and organic matter, available of phosphorus and available potassium of soil contents were recorded significantly higher in the far distance from settlement than near and middle distance from settlement (Table 4). 3.4.1.2. The effect of altitude on soil Parameters Sand soil content had showed significant decreased with altitude increasing (Table 4; F2,18 = 33. 07, P < 0.000). Whereas, clay soil content was increased with altitude increasing (Table 4; F2,18 = 52.33, P < 0.000). In the lower altitude, pH value was recorded significantly higher than upper and lower altitudes (Table 4; F2,18 = 6.16, P < 0.009). This is related to the fact that the pH value and sand soil increase with altitude decreases but clay soil content increase with altitude increase Abreha et al., (2012). The higher sand content and pH value under lower altitude is probably caused by increasing run off and soil erosion, and soil compacted. Nitrogen percentage under low altitude was significantly difference from other altitudes. Under the upper altitude, organic carbon, organic matter, available phosphorus and available potassium had significant higher as compared to other two altitude ranges (Table 4). This is supported by the finding of Getachew et al., (2007) in Borana rangelands, Ethiopia and Abreha et al., (2012) in Tsegede Highlands, Northern Ethiopia. This results probably due to the availability of organic matter, higher standing biomass, soil moister and rainfall increasing with altitude range increasing. 3.4.1.3.The effect of distance on soil Parameters In near distance to settlement, sand soil content had showed significantly higher than far distance from settlement (Table 4; F2,18 = 3.65, P < 0.047). This result may be related to the high degree of soil erosion, high grazing pressures and human activities near to settlement than far distance from settlement. Organic matter and organic carbon had significant increased with distance increased from settlement. In far distance from settlement, available phosphorus and potassium were recorded significantly higher than that of the near and middle distance from settlement. Nitrogen Percentage had significantly higher in far distance from settlement than middle distances from settlement (Table 4; F2,18 = 4.97, P < 0.019).
  • 7. Journal of Environment and Earth Science www.iiste.org ISSN 2224-3216 (Paper) ISSN 2225-0948 (Online) Vol.4, No.15, 2014 Table 4: Effect of altitudinal ranges and distance interval away from settlements (km) on physical and chemical soil Parameters in Kafta-Humera rangelands, northern Ethiopia pH OC (%) OM (%) AVP.ppm AVK.ppm TN (%) Sand (%) Silt (%) Clay 44 (%) Mean Altitude (m.a.s.l) 600-1000 0-2 7.45a 1.06b 1.83b 0.61b 1.42a 0.09a 53.33a 16.33b 30.33a 2-4 7.22a 1.50ba 2.58ba 0.99ba 1.43a 0.08a 48.67ba 26.67a 24.67a 4-6 7.09a 2.10a 3.62a 1.28a 1.96a 0.10a 42.00b 27.00a 31.00a >1000-1400 0-2 6.86a 0.95b 1.64b 0.92a 1.57a 0.163a 45.67a 22.33a 32.00a 2-4 6.73a 1.34ba 2.32ba 0.95a 1.78a 0.129a 36.33a 16.33a 47.33a 4-6 6.60a 2.03a 3.51a 1.22a 2.34a 0.269a 28.67a 23.33a 48.00a >1400-1800 0-2 6.87a 1.59b 2.75 b 1.44b 1.87b 0.210a 17.67a 21.33a 61.00a 2-4 6.71a 1.77b 3.06b 1.09b 2.41b 0.206a 20.67a 18.33a 61.00a 4-6 6.53a 2.57a 4.44 a 2.10a 3.39a 0.311a 16.33a 23.00a 60.67a Altitude (A) F (df =2,18) 6.16 10.43 10.52 19.07 25.95 14.32 33.07 1.47 52.33 p 0.009 0.001 0.001 0.000 0.000 0.000 0.000 0.255 0.000 Distance (D) F (df =2,18), 1.66 35.97 36.21 18.17 25.98 4.97 3.65 4.03 1.50 p 0.219 0.000 0.000 0.000 0.000 0.019 0.047 0.036 0.25 (A) * (D) F (df =4,18), 0.02 0.22 0.23 3.75 2.44 0.99 0.85 4.35 2.38 p 0.999 0.922 0.92 0.022 0.084 0.441 0.513 0.012 0.09 Adjusted R2 0.229 0.767 0.769 0.758 0.802 0.57 0.726 0.44 0.807 OC = Organic carbon; OM = Organic matter; AVP = Available phosphorus; AVK = Available potassium; TN = Total nitrogen. Means with the same letters in columns are not significantly different at P ≤ 0.05 4. CONCLUSION In the study districts, a total of 46 species of woody species were identified. A. bussei, A. mellifera, Anogeissus leiocarpa, Combretum hartmannianum, D. cinerea, Lannea frutcosa and Z. spina-christi were the common dominant species for all altitude and distance. In all altitude, woody species diversity and abundance in far distance to settlements were significantly higher than near distance. In the lower altitude, all woody diversity parameters had significantly lower. Sand and pH value had also significantly higher but soil clay was significantly lower as compared to the middle and upper altitudinal ranges. Far distance from settlement had significantly higher in organic carbon, organic matter, available phosphorus and available potassium than to middle and near distance. The upper altitude had showed significantly higher in organic carbon, organic matter, available phosphorus and available potassium as compared to the lower and middle altitude. Under the present soil status, biodiversity and productivity circumstances of the areas near to settlement and middle distance intervals from settlement, preservation or return of habitats should be of greater concern because the best way to minimize biodiversity loss is to maintain the integrity of ecosystem function. Research related to rehabilitation and possible restoration strategies through soil seed bank under various altitudinal ranges and settlement areas should be considered. REFERENCE Abreha K, Heluf G, Tekalign M and Kibebew K (2012). Impact of altitude and land use type on some physical and chemical properties of acidic soils in Tsegede highlands, Northern Ethiopia. Journal of Earth and Environmental Science, 2 (3): 223-223. Abule E, Snyman H and Smit G (2005). Comparisons of pastoralists perceptions about rangeland resource utilization in the Middle Awash Valley of Ethiopia. Journal of Environmental Management, 75: 21–35. Brinkmann (2009). Vegetation patterns and diversity along an altitude and grazing gradient in the Jabal al Akhdar Mountain range of northern Oman. Journal of Arid Environments, 73: 1035-1045. EARO (Ethiopia Agricultural Research Organization) (2002). Dry land Agriculture Research Strategic Planning Document. Addis Ababa, Ethiopia. 66p. Ecosystem Processes, pp. 1–30. Berlin: Springer. Gebrehaweria K (2011). Pastoralists’ perception, vegetation diversity and condition assessment in rangelands of kafta-humera woreda, tigray regional state, ethiopia M.Sc. Thesis Presented to the School of Graduate Studies of Haramaya University, Ethiopia. 128p. Getashew H, Mohammed A and Abule E (2007). Effects of rangeland management on soil characteristics of Yabello rangelands, Southern Ethiopia. Ethiopian Journal of Natural Resources, 9(1): 19-35. Hailesilassie A (1998). Present Land Use and Land Cover of Kafta- Humera District Western Zone.Mekelle,
  • 8. Journal of Environment and Earth Science www.iiste.org ISSN 2224-3216 (Paper) ISSN 2225-0948 (Online) Vol.4, No.15, 2014 Bureau of Agriculture and Natural Resources Development Land Use Team. Jeffrey S (2007). Fragmentation and settlement patterns in Maasai land. Implications for pastoral mobility, drought vulnerability and wild life conservation in East Africa savanna. In partial fulfillment of the requirements for the degree of doctor of Philosophy Colorado state University, for Collins, Colorad. Krebs (1998). Ecological methodology University of British Colombia.2th ed. Lamporey R.H and Reid, R.S (2004). Expansion of human settlements in Kenya Maasai area: what future for pastoralism and wild life? Journal of Biogeography, 31: 997-1032. Magurran (2004). Measuring Biological Diversity, First published by Blackwell Science Company, USA. MoARD (Ministry of Agriculture and Rural Development) (2007). Livestock Development Master Plan Study. MoARD, Addis Ababa, Ethiopia. Moti J, Mekonnen Y, Adugna T, Mitiku H, Ansha Y, Kindeya G, Kelemework T, Yemane G, Mekonnen T, Nigatu R, Mulugeta T, Abiye A and Kiros M (2011). Impact of Resettlement on the Livelihood, Food Security and Natural Resource Utilization in Ethiopia. Pankhurs A and Pinguet F (2004). “Contextualizing Migration, Resettlement, and Displacement in Ethiopia.” In: Pankhurst, A. and Pinguet, F. (eds.). People, Space, and the State: Migration and Displacement in Ethiopia. Petmak M (1983). Primary productivity, nutrient cycling and OM turnover of tree plantation after agricultural intercropping practices in north east Thailand. PhD thesis, University of Philadelphia, Los Banos Philadelphia. 228p. Ter Braak C (1997). CANOCO a FORTRAN program for canonical community ordination by [Partial] [Detrained] canonical] correspondence analysis, principal component analysis and redundancy analysis (version 4.15). Institute of Applied Computer Science, 95, Wageningen, Netherlands. Tessema Z, de Boer W, Baars R and Prins H (2011). Change in soil nutrients, vegetation cover, structure and herbaceous biomass in response to grazing in semiarid, savanna of Ethiopia. Journal of Arid Environments, 75: 662-670. Van Reeuwijk L (1992). Procedure for Soil Analysis, third ed. International Soil Reference and Information Center, Wageningen, The Netherlands. 45
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