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The challenge of HIV/AIDS: Where does agroforestry fit in? - World ...

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Chapter 12: Watershed functions <strong>in</strong> productive agricultural landscapes109Depth (cm)Depth (cm)ForestMultistrata c<strong>of</strong>feema<strong>in</strong> processes are captured <strong>in</strong> simulationmodels that have reached considerablepredictive ability, the dynamics <strong>of</strong> soilstructure <strong>in</strong> terms <strong>of</strong> decay and recoveryare still largely a black box, constra<strong>in</strong><strong>in</strong>gfurther precision <strong>of</strong> models <strong>of</strong> water balancefor example. <strong>The</strong> WaNuLCAS model(van Noordwijk et al. 2004c) uses theempirical reference value for bulk density,BDref , as a ‘fall-back’ value to which soilstructure decay reverts <strong>in</strong> the absence <strong>of</strong>specific macropore creation activities,which create macropores directly (vanNoordwijk et al. 2004d). This model descriptionsuggests that the most importantparts <strong>of</strong> a tree for land rehabilitation are thedead leaves that it sheds and the f<strong>in</strong>e andcoarse root turnover it <strong>in</strong>duces.Simple shade c<strong>of</strong>fee<strong>in</strong> conditions where the soil rema<strong>in</strong>s farfrom saturated. <strong>Where</strong> surface phenomenasuch as crust<strong>in</strong>g rather than soil compactiondom<strong>in</strong>ate <strong>in</strong> the soil physical degradationprocess, recovery may be faster: anytype <strong>of</strong> mulch that protects the soil fromthe direct impact <strong>of</strong> ra<strong>in</strong> and sunsh<strong>in</strong>e andthat stimulates soil biological activity maylead to recovery <strong>in</strong> a timeframe <strong>of</strong> months.Sun c<strong>of</strong>feeFigure 4. Infiltration patterns for a dye that leaves a dark trace <strong>in</strong> all macropores it passesthrough. This simulates what may happen dur<strong>in</strong>g heavy ra<strong>in</strong>fall on four types <strong>of</strong> land use<strong>in</strong> the Sumberjaya benchmark area <strong>in</strong> West Lampung, Indonesia; see Hairiah et al. (2004)and Widianto et al. (2004) for details on the methods and sites.It is thus important to correctly diagnosewhat type <strong>of</strong> degradation dom<strong>in</strong>ates <strong>in</strong> agiven location, as this will <strong>in</strong>fluence thetimeframe for potential recovery. Avoid<strong>in</strong>gcompaction at sites that are still <strong>in</strong> a naturalforest condition is probably more effectivethan try<strong>in</strong>g to rehabilitate degraded sites.<strong>Where</strong> surface processes dom<strong>in</strong>ate, however,rapid ga<strong>in</strong>s by mulch-based restorationactivities can be expected.Standard soil physical textbooks and handbook<strong>of</strong> methods specify how BD can bemeasured – but not how the data can be <strong>in</strong>terpreted.Bulk density is strongly related tosoil texture and soil organic matter content(which <strong>in</strong> itself depends on texture), so fora valid <strong>in</strong>terpretation <strong>in</strong> the context <strong>of</strong> compaction,we need to derive a reference valuefor a soil with the same texture. A simplescheme is available <strong>in</strong> spreadsheet form onwww.ICRAF.org/sea as part <strong>of</strong> the ecologicalmodels that can be freely downloaded.While the water, nutrient and carbon balance<strong>of</strong> soils are well understood, and theA further complication arises when werealize that surface litter, depend<strong>in</strong>g onits size and weight, is prone to be carriedaway by w<strong>in</strong>d or overland flow <strong>of</strong> water,lead<strong>in</strong>g to a differentiation <strong>of</strong> the land <strong>in</strong>tomutually enhanc<strong>in</strong>g zones <strong>of</strong> high <strong>in</strong>filtrationwith deposition <strong>of</strong> surface mulch,and zones <strong>of</strong> crusted soil with high run<strong>of</strong>f.Classification <strong>of</strong> litter sources by their propensityto transport is only just start<strong>in</strong>g.A macro version <strong>of</strong> the transport–depositioneffect is known as the ‘tiger bush’striped pattern <strong>in</strong> semi-arid lands – wherethe degraded zones act as water harvest<strong>in</strong>gsource areas for the vegetated parts.Land rehabilitation can aim at strategicallymodify<strong>in</strong>g the scale <strong>of</strong> this pattern, but notat a fully homogeneous state.For a full understand<strong>in</strong>g <strong>of</strong> the trade<strong>of</strong>fsbetween productivity (or pr<strong>of</strong>itability) <strong>of</strong>land use and the implication for watershedfunctions we thus have a reasonably wellequippedtool kit. <strong>The</strong>re are complications,however, such as the differences <strong>in</strong> time

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