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Grain Legumes and Green Manures for Soil Fertility in ... - cimmyt

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with the natural fallow, which did not lose its aggregate<br />

stability. The decrease <strong>in</strong> aggregate stability<br />

was more pronounced under sesbania <strong>and</strong> maize<br />

without fertilizer as compared ~ith cajanus <strong>and</strong><br />

maize with fertilizer. Under a sesbania fallow system,<br />

the improvement <strong>in</strong> soil structure is more evident<br />

<strong>and</strong> this is reflected by results from our time to<br />

runoff studies. Time to runoff after fallow clear<strong>in</strong>g<br />

was <strong>in</strong> the order of: natural fallow> S. sesban > fertilized<br />

maize. After one season of cropp<strong>in</strong>g, time to<br />

runoff decreased <strong>in</strong> all treatments except that the<br />

natural fallow ma<strong>in</strong>ta<strong>in</strong>ed the longer time to runoff,<br />

reflect<strong>in</strong>g good ma<strong>in</strong>tenance of aggregate stability.<br />

Through ra<strong>in</strong>fall simulation studies we evaluated<br />

effects of improved fallows on runoff <strong>in</strong>filtration<br />

soil <strong>and</strong> nutrient losses under improved fallows.<br />

Tree fallows of sesbania, gliricidia mixed with archer<br />

dolichos <strong>in</strong>creased <strong>in</strong>filtration rates significantly<br />

compared with cont<strong>in</strong>uously fertilized maize plots<br />

(Figure 7). Fallows compared to no tree plots also<br />

significantly reduced soil loss (Table 5).<br />

Improved fallows improve soil physical properties<br />

as evidenced by <strong>in</strong>crease <strong>in</strong> <strong>in</strong>filtration rates, <strong>in</strong>creased<br />

<strong>in</strong>filtration decay coefficients, reduced runoff<br />

<strong>and</strong> soil losses. However these benefits are short<br />

lived <strong>and</strong> they decl<strong>in</strong>e rapidly dur<strong>in</strong>g the first year<br />

of cropp<strong>in</strong>g. This was supported by <strong>in</strong>crease <strong>in</strong> soil<br />

loss <strong>in</strong> the second year (TableS) <strong>and</strong> decrease <strong>in</strong> <strong>in</strong>­<br />

40<br />

35<br />

i )0<br />

! 2S<br />

~ 20 <br />

c <br />

.g 15<br />

g<br />

~ 10<br />

S. sesban T. vogelii N. rallow fl:t1ilizal. maize G. sepium+ A.<br />

dolichos<br />

Treatmenls<br />

I-October 2000 [JOclober2001 I<br />

Figure 7. Infiltration rate under different fallows measured at<br />

Msekera (source; Nyamadzowo et a/2002)<br />

Table 5. <strong>Soil</strong> loss (g/m2) measured under various fallow species<br />

<strong>and</strong> maize at Kalunga Farmers Tra<strong>in</strong><strong>in</strong>g Center <strong>in</strong> eastern Zambia<br />

Treatment October 2000 October 2001<br />

Sesbania sesban 0.0 5.0<br />

Tephrosia voge/ii 4.5 15.8<br />

Natural fallow 0.0 19.5<br />

Fully fertilized maize 63.8 ..0.5<br />

~iratro (Macroptilium atropurpureum) 0.0 0.7<br />

ILSO 15.3 .<br />

Source: Nyamadzowo et al2002<br />

filtration rates as well (Figure 7). However, mix<strong>in</strong>g<br />

a coppic<strong>in</strong>g species like gliricidia <strong>and</strong> a herbaceous<br />

legume like archer dolichos ma<strong>in</strong>ta<strong>in</strong>ed high <strong>in</strong>filtration<br />

rates <strong>and</strong> reduced soil loss over two years of<br />

cropp<strong>in</strong>g.<br />

Susta<strong>in</strong>ability of Improved Fallows<br />

Improved fallows with sesbania or tephrosia have<br />

been shown to give maize gra<strong>in</strong> yields of 3 to 4 t/ha<br />

without any <strong>in</strong>organic fertilizer addition. Palm<br />

(1995) showed that organic <strong>in</strong>puts of various tree<br />

legumes applied at 4 t/ha can supply enough nitrogen<br />

<strong>for</strong> maize gra<strong>in</strong> yields of 4 t/ha. However,<br />

most of these organic <strong>in</strong>puts could not supply<br />

enough phosphorus <strong>and</strong> potassium to support such<br />

maize yields.<br />

The question ferr susta<strong>in</strong>ability is: Can improved fallows<br />

potentially m<strong>in</strong>e P <strong>and</strong> K over time while<br />

ma<strong>in</strong>ta<strong>in</strong><strong>in</strong>g a positive N balance? To answer that<br />

question we conducted nutrient balances on improved<br />

fallow trials at Msekera Research Station.<br />

These plots were under fallow-crop rotations <strong>for</strong> 8<br />

years. The objectives of these studies on nutrient<br />

balances addressed the follow<strong>in</strong>g questions:<br />

• Can nutrient balances be used as l<strong>and</strong> quality <strong>in</strong>dicators?<br />

• Can they be used to assess soil fertility status,<br />

productivity <strong>and</strong> susta<strong>in</strong>ability?<br />

• Can they be used as a policy <strong>in</strong>strument <strong>for</strong> the<br />

types of fertilizers to be imported or distributed<br />

to farmers?<br />

The nutrient balances considered nutrients added<br />

through leaves <strong>and</strong> litter fall, which were <strong>in</strong>corporated<br />

after fallows as <strong>in</strong>puts. The nutrients <strong>in</strong> maize<br />

gra<strong>in</strong> harvested, maize stover removed <strong>and</strong> fuelwood<br />

taken away at end of the fallow were considered<br />

as nutrient exports.<br />

For all the l<strong>and</strong> use systems, there was a positive N<br />

balance two years of cropp<strong>in</strong>g after the fallows<br />

(Table 6). Fertilized maize had the highest N balance<br />

due to the annual application of 112 kg N/ha<br />

<strong>for</strong> the past 10 years. However, unfertilized maize<br />

had lower balances due to low maize gra<strong>in</strong> <strong>and</strong><br />

stover yields over time. The tree-based fallows had<br />

a positive N balance due to BNF <strong>and</strong> deep capture<br />

of N from depth. These results are consistent with<br />

those of Palm (1995) that showed that organic <strong>in</strong>puts<br />

could supply enough N to support maize gra<strong>in</strong><br />

yields of 3 to 4 t/ha.<br />

However <strong>in</strong> the second year of cropp<strong>in</strong>g (1999) the<br />

N balance was very small. This is consistent with<br />

our earlier results, which showed a decl<strong>in</strong>e of maize<br />

148<br />

<strong>Gra<strong>in</strong></strong> legumes <strong>and</strong> <strong>Green</strong> <strong>Manures</strong> <strong>for</strong> <strong>Soil</strong> <strong>Fertility</strong> <strong>in</strong> Southern Africa

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