Vegetation influence on soil quality in a highly degraded tropical ...
Vegetation influence on soil quality in a highly degraded tropical ...
Vegetation influence on soil quality in a highly degraded tropical ...
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16 SOTOMAYOR-RAMÍREZ ET AL./TROPICAL SOILS<br />
Soil microbial respirati<strong>on</strong> was quantified by <strong>in</strong>cubat<strong>in</strong>g <strong>soil</strong> (10 g<br />
fresh wt) <strong>in</strong> a sealed 125-ml flask c<strong>on</strong>ta<strong>in</strong><strong>in</strong>g 6 ml of 0.1N NaOH. After<br />
a 7-d <strong>in</strong>cubati<strong>on</strong> the NaOH was titrated with standardized HCl by us<strong>in</strong>g<br />
an automatic titrator (Ori<strong>on</strong> EA 960, Thermo Electr<strong>on</strong> Company,<br />
USA). Values of <strong>soil</strong> respirati<strong>on</strong> were expressed as mg C/kg (dry wt)/wk.<br />
The data were subjected to analysis of variance us<strong>in</strong>g GLM procedure<br />
(SAS Institute, 1996). Data were analyzed as a randomized<br />
complete block <strong>in</strong> split-plot design. Whole plots corresp<strong>on</strong>ded to the six<br />
plant species and the c<strong>on</strong>trol; the sub-plots corresp<strong>on</strong>ded to the date of<br />
sampl<strong>in</strong>g; and the split-split plots corresp<strong>on</strong>ded to the sampl<strong>in</strong>g depth.<br />
The class variable for time was not <strong>in</strong>cluded <strong>in</strong> the analysis for extractable<br />
bases, pH, acidity, extractable Al, ECEC, or PMN s<strong>in</strong>ce these were<br />
analyzed <strong>on</strong>ce. Assumpti<strong>on</strong>s of normality and variance homogeneity<br />
were corroborated by us<strong>in</strong>g Shapiro-Wilks and Brown-Forsythe tests,<br />
respectively. Multiple comparis<strong>on</strong>s were performed with a protected<br />
Fisher’s LSD with a significance level of 0.05 for volumetric water c<strong>on</strong>tent.<br />
S<strong>in</strong>gle degree of freedom c<strong>on</strong>trasts were used to make<br />
comparis<strong>on</strong>s am<strong>on</strong>g means of groups of plants (legume trees, legume<br />
shrubs, and grasses) and bare <strong>soil</strong> (c<strong>on</strong>trol). Correlati<strong>on</strong> analysis was<br />
performed by us<strong>in</strong>g the CORR procedure of SAS.<br />
RESULTS AND DISCUSSION<br />
Interacti<strong>on</strong>s were not significant for <strong>soil</strong> physical (bulk density) and<br />
chemical properties (SOM, exchangeable bases, exchangeable acidity,<br />
and ECEC) evaluated, except for <strong>soil</strong> volumetric water c<strong>on</strong>tent. Soil water<br />
c<strong>on</strong>tent was generally higher at the 5- to 15-cm depth than at the 0to<br />
5-cm depth <strong>in</strong>tervals for all species and the c<strong>on</strong>trol (P < 0.05) except<br />
for that of the two forage species. In those two species, <strong>soil</strong> water c<strong>on</strong>tent<br />
was similar at the two depths (data not shown). There was a<br />
general trend for exchangeable bases to decrease and for exchangeable<br />
Al to <strong>in</strong>crease with depth from 0- to 5- to 5- to 15-cm depth (data not<br />
shown). Extractable <strong>soil</strong> phosphorus (P) was undetectable (detecti<strong>on</strong><br />
limit 0.05 mg P/kg) at the beg<strong>in</strong>n<strong>in</strong>g and at the end of the experiment<br />
for all plots evaluated. C<strong>on</strong>trast comparis<strong>on</strong>s of groups showed that<br />
bare <strong>soil</strong> had significantly (P < 0.05) higher acidity and exchangeable Al<br />
than <strong>soil</strong>s with legumes and grasses, both al<strong>on</strong>e and comb<strong>in</strong>ed (Table 1).<br />
In the study by Ramos-Santana et al. (2001), the plants that best<br />
adapted to the <strong>soil</strong> c<strong>on</strong>diti<strong>on</strong>s <strong>in</strong> terms of aerial coverage and biomass<br />
producti<strong>on</strong> were the grasses (H. altissima and B. humidicola), followed<br />
by A. procera. Intermediate growth was observed for A. glabrata,<br />
whereas very poor growth and coverage were observed for C. acutifolium<br />
and for A. <strong>in</strong>ermes. The <strong>soil</strong> protecti<strong>on</strong> provided by the grasses