Ecology and Development Series No. 10, 2003 - ZEF
Ecology and Development Series No. 10, 2003 - ZEF Ecology and Development Series No. 10, 2003 - ZEF
Floristic analysis of the undisturbed forestSpecies Axis I Axis II Axis III Axis IV11 Abutilon cecilli 0.2657 -0.1043 0.1525 -0.034912 Bersama abyssinica 0.2474 -0.0499 -0.1143 -0.02213 Anthiaris toxicaria 0.2423 0.2002 0.1636 0.106414 Canthium giordanii 0.2353 0.2649 0.1741 -0.157115 Rhus ruspoli 0.217 -0.2904 -0.0348 0.101216 Dracaena fragrans -0.2108 0.9724 0.0014 0.004317 Ehretia cymosa 0.2029 -0.0543 0.0908 0.204918 Galiniera saxifraga -0.2001 -0.2214 0.3505 -0.031319 Hippocratea africana -0.1998 0.0902 0.3153 0.001120 Tiliachora troupinii -0.1968 0.0564 -0.1687 0.208221 Teclea noblis -0.194 0.1689 0.2315 0.061322 Trilepisium madagascariense -0.1719 0.2066 0.0421 0.096423 Scutia myrtina 0.1659 0.0604 -0.1017 0.188324 Landolphia buchananii 0.157 0.0047 -0.3134 0.918825 Eugenia bukobensis -0.1508 -0.0233 0.3168 0.036726 Maesa lanceolata 0.1448 0.0128 -0.0935 0.096727 Diospyros abyssinica -0.1439 0.0145 0.4667 -0.2228 Urera trinervis 0.1427 -0.0437 0.0324 0.014929 Morus mesosygia 0.1384 0.0117 -0.0544 -0.02830 Albizia grandibracteata -0.1342 0.0662 0.0573 0.100631 Gouania longispicata -0.1302 -0.2112 0.116 0.162132 Croton macrostachyus -0.1134 0.2036 -0.1106 0.050833 Vepris dainelli -0.1113 0.1093 -0.0571 -0.039734 Celtis toka -0.1044 -0.0133 0.2191 -0.111835 Cissus quadrangularis 0.1032 0.0431 -0.0903 0.062936 Clausena anisata 0.1023 -0.1634 -0.1652 -0.127655
Floristic analysis of the undisturbed forest4.3.4 Relationships between environmental variables and community typeThe three groups identified by cluster analysis are distinct and show a clear distributionpattern with respect to the axes in the PCA species-plots biplot (Figure 4.2). Group 1 ismainly positively correlated with the first axis, while some plots in the group are positivelyand others negatively correlated with the second axis. Group 2 is negatively correlated withboth the first and the second axis. On the other hand, Group 3 is mainly positivelycorrelated with second axis, and slightly negatively correlated with first axis (Figure 4.2).The first axis is the strongest gradient, accounting for 40.8% of the variation, while thesecond axis accounts for 23.3% of the variation species distribution (Table 4.3). Thegradients in the PCA axes can be attributed to some environmental variables (Table 4.5).The gradient in first axis increases with decreasing slope, silt and pH, and with increasingdistance from Geba river. On the other hand, the gradient in the second axis increases withaltitude, silt, soil moisture, CEC, distance from Geba river and C-N ratio.Table 4.5. Correlations between environmental variables and PCA axesEnvironmental variable Axis I Axis IIAltitude 0.269 0.696Slope-percent -0.506 -0.084Sand 0.323 -0.314Silt -0.535 0.327Soil moisture -0.351 0.093pH -0.519 -0.208CEC -0.340 0.243Distance from Geba river 0.625 0.458C : N ratio 0.170 0.718The mean difference in these environmental variables was tested using the onewayanalysis of variance and Duncan’s multiple range tests. The three groups differsignificantly from each other with regard to three environmental variables, namely: altitude(F 2,54 = 5.671, P < 0.01), slope (F 2,54 = 3.510, P < 0.05) and distance from the Geba river(F 2,54 = 10.841, P < 0.001). The summary of the mean difference between groups withregard to the significantly varying environmental variables is presented in Table 4.6.56
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Floristic analysis of the undisturbed forest4.3.4 Relationships between environmental variables <strong>and</strong> community typeThe three groups identified by cluster analysis are distinct <strong>and</strong> show a clear distributionpattern with respect to the axes in the PCA species-plots biplot (Figure 4.2). Group 1 ismainly positively correlated with the first axis, while some plots in the group are positively<strong>and</strong> others negatively correlated with the second axis. Group 2 is negatively correlated withboth the first <strong>and</strong> the second axis. On the other h<strong>and</strong>, Group 3 is mainly positivelycorrelated with second axis, <strong>and</strong> slightly negatively correlated with first axis (Figure 4.2).The first axis is the strongest gradient, accounting for 40.8% of the variation, while thesecond axis accounts for 23.3% of the variation species distribution (Table 4.3). Thegradients in the PCA axes can be attributed to some environmental variables (Table 4.5).The gradient in first axis increases with decreasing slope, silt <strong>and</strong> pH, <strong>and</strong> with increasingdistance from Geba river. On the other h<strong>and</strong>, the gradient in the second axis increases withaltitude, silt, soil moisture, CEC, distance from Geba river <strong>and</strong> C-N ratio.Table 4.5. Correlations between environmental variables <strong>and</strong> PCA axesEnvironmental variable Axis I Axis IIAltitude 0.269 0.696Slope-percent -0.506 -0.084S<strong>and</strong> 0.323 -0.314Silt -0.535 0.327Soil moisture -0.351 0.093pH -0.519 -0.208CEC -0.340 0.243Distance from Geba river 0.625 0.458C : N ratio 0.170 0.718The mean difference in these environmental variables was tested using the onewayanalysis of variance <strong>and</strong> Duncan’s multiple range tests. The three groups differsignificantly from each other with regard to three environmental variables, namely: altitude(F 2,54 = 5.671, P < 0.01), slope (F 2,54 = 3.5<strong>10</strong>, P < 0.05) <strong>and</strong> distance from the Geba river(F 2,54 = <strong>10</strong>.841, P < 0.001). The summary of the mean difference between groups withregard to the significantly varying environmental variables is presented in Table 4.6.56