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close this bookSustaining the Future. Economic, Social, and Environmental Change in Sub-Saharan Africa (UNU, 1996, 365 p.)
close this folderPart 2: Environmental issues and futures
close this folderTropical deforestation and its impact on soil, environment, and agricultural productivity
View the document(introduction...)
View the documentIntroduction
View the documentTRF and its conversion
View the documentSoils of the TRF ecosystem
View the documentForest conversion and soil productivity
View the documentDeforestation and the emission of radiatively active gases
View the documentDeforestation and hydrological balance
View the documentSustainable use of the TRF ecosystem
View the documentResearch needs
View the documentReferences

Deforestation and hydrological balance

Deforestation of TRF can drastically alter the components of the hydrological cycle:

P = I + R + DS + D + > Edt,

where P is precipitation, I is infiltration, R is surface runoff, DS is soilwater storage, D is deep drainage, E is evapotranspiration, and t is time. Deforestation decreases I and DS and increases R and D components. In general, deforestation may also increase E. The change in E, however, may also depend on the land use.

Several experiments have demonstrated the effects of clear-cutting on the increase in total water yield. The impact of deforestation on the hydrological balance of a 44 ha watershed was studied at the International Institute of Tropical Agriculture (IITA), Ibadan, Nigeria. Prior to partial deforestation in 1978 and complete defor estation in 1979, measurements of surface and subsurface flow were made under the forest cover from 1974 to 1977. Under the forest cover, the interflow was 0.4 per cent to 1.4 per cent and total flow 0.8 per cent to 2.7 per cent of the total rainfall. Partial clearing in 1978 increased interflow to 1.2 per cent and increased total flow to 6.6 per cent of the total rainfall (table 9.13).

Table 9.13 Effects of partial clearing in 1978 on total water discharge from Watershed 1

Parameters  
Rainfall (mm) 785.8
Surface flow (mm) 42.7
Surface flow (% of rain) 5.4
Subsurface flow (mm) 9.4
Subsurface flow (% of rain) 1.2
Total yield (mm) 52.1
Total yield (% of rain) 6.6

Note: The partial clearing was of 3.1 ha out of 44.3 ha.

Table 9.14 Hydrological components on an annual basis for Watershed 1, 1979-1986

Year Annual rainfall (mm) Subsurface flowb (mm) Surface flow (mm)

Total water yield

Apparent evapo transpirationa

        mm % of rainfall mm % of rainfall
1979 1,435.5 28.0 73.4 101.4 7.1 1,334.1 92.9
1980 1,449.7 73.1 90.0 163.1 11.3 1,286.6 88.8
1981 1,074.5 58.9 28.9 87.8 8.2 986.7 91.8
1982 851.5 50.9 25.9 76.8 9.0 774.7 91.0
1983 897.6 45.8 21.3 67.1 7.5 830.5 92.5
1984 1,162.2 58.9 27.1 86.0 7.4 1,076.2 92.6
1985 1,675.7 18.5 93.2 111.7 6.7 1,563.9 93.3
1986 1,164.1 1.9 51.7 53.8 4.6 1,110.3 95.3

a. Evapotranspiration includes soil water storage and groundwater recharge.
b. Subsurface flow is underestimated during wet years because it is computed as a part of surface flow during the storm runoff.

The entire watershed was cleared in 1979 and cultivated to food crops. The data in table 9.14 show that the total water yield ranged from 4.6% to 11.3% of the rainfall received. Because of the bimodal distribution of the rainfall, the hydrologic balance was computed separately for each growing season. The hydrologic balance showed that total water yield ranged from 1.4% to 11.8% for the first season (table 9.15) and from 0.8% to 18.1% for the second season (table 9.16). The intermittent stream, with a trace of flow after heavy rain and no flow during the dry season, became a perennial stream that recorded a measurable flow throughout the dry season (table 9.17).

Table 9.15 Hydrological components for the first growing season (March-July), 1979-1987

Year Annual rainfall (mm) Subsurface flowb (mm) Surface flow (mm)

Total water yield

Apparent evapo transpirationa

        mm % of rainfall mm % of rainfall
1979 846.1 7.0 89.8 96.8 11.4 749.3 88.6
1980 604.3 1.2 7.0 8.2 1.4 596.1 98.6
1981 636.8 20.2 17.3 37.5 5.9 599.3 94.1
1982 615.2 28.4 17.6 46.0 7.5 569.2 92.5
1983 580.9 22.3 15.2 37.5 6.5 543.4 93.5
1984 681.6 23.6 13.9 37.5 5.5 644.1 94.5
1985 935.7 10.8 52.1 62.9 6.7 872.8 93.3
1986 714.2 1.8 36.9 38.7 5.4 677.3 94.8
1987 723.5 36.4 49.2 85.6 11.8 637.9 88.2

a. See notes to table 9.14.
b. See notes to table 9.14.

Table 9.16 Hydrological components for the second growing season (AugustNovember), 1979-1986

Year Annual rainfall (mm) Subsurface flowb (mm) Surface flow (mm)

Total water yield

Apparent evapo transpirationa

        mm % of rainfall mm % of rainfall
1979 585.8 0.03 4.6 4.6 0.8 581.2 99.2
1980 845.4 71.90 81.1 153.0 18.1 692.4 81.9
1981 432.4 33.50 11.6 45.1 10.4 387.3 89.6
1982 223.6 19.20 8.1 27.3 12.2 196.3 87.8
1983 230.6 19.20 6.1 25.3 11.0 205.3 89.0
1984 480.6 30.50 13.2 43.7 9.1 436.9 90.9
1985 735.5 6.90 41.1 48.0 6.5 687.5 93.5
1986 379.2 0.10 13.9 14.0 3.7 365.2 96.3

a. See notes to table 9.14.
b. See notes to table 9.14.

Table 9.17 Hydrological components for the dry season (December-February) for Watershed 1, 1979-1987

Year Seasonal rainfall (mm) Subsurface flow (mm) Surface flow (mm) Total water yield (mm)
1979 3.6 0.0 0.0 0.0
1980 23.6 0.0 0.0 0.0
1981 5.3 2.0 0.08 2.1
1982 12.7 5.0 0.10 5.1
1983 0.0 3.6 0.03 3.6
1984 86.1 4.1 1.1 5.2
1985 0.0 3.6 0.0 3.6
1986 7.6 0.0 0.0 0.0
1987 18.8 3.9 0.0 3.9

Note: The data for December are taken from the previous year.

An increase in the magnitude of interflow and its continuous discharge throughout the dry season may be attributed to the replacement of deep-rooted perennials with high water requirements with shallow-rooted annuals with relatively fewer water requirements. Further, annuals were not grown during the dry season.