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Flooding Irrigation

Value Chain
Annual Average Rainfall
Soils
Climatic Zone
Water Source
Decision Making
Farming Characteristics
Mechanisation
Labour Intensity
Initial Investment
Maintenance Costs
Access to Finance/Credit
Extension Support Required
Access to Inputs
Access to Markets
Gender/Youth Smart
Description

Flooding irrigation is a practice where water is pumped or allowed to flow into channels passing between crop rows in areas where farmers have level fields. This flooding system is an effective method of managing weeds and pests, preventing the completion of their lifecycles as they are either drowned or isolated from air and sunlight. This practice is applicable in areas where there are favourable climatic conditions with high rainfall amounts; and is not recommended in arid and semi-arid environments. Flooding is controlled using water pumps in order to reduce waterlogging problems, and fields should not be entirely flooded, with surges of periodic flooding used to distribute water and avoid wastage to run-off, evaporation and creation of anaerobic conditions in the soil. Flood waters can be filtered using a fine mesh to control pests and diseases from spreading to neighbouring fields. Sandy soil is not favourable for flood irrigation as it does not evenly distribute water across the field whereas loam and clay soils distribute water efficiently across the field.

It is considered a climate smart practice because it requires less energy, and can promote crop productivity, whilst controlling weeds and pests.

Technical Application

To effectively leverage flooding irrigation:

  • Step 1: prepare the field, digging parallel furrows and raising beds with the excess soil. Crops are planted in beds, and the irrigation water will flow in the furrows.
  • Step 2: Using a pump or gravity fed water storage, allow water to flow into the field, flooding furrows.
  • Step 3: Insert a fine mesh or introduce a hessian sack at the in-flow point to trap weeds and pests.
  • Step 4: Water release should be moderated so as not to flow too fast and erode beds, and too slow such that it remains trapped at the in-flow point.
  • Step 5: Water release can be more effective if released in surges, taking advantage of infiltration rates and capillary action in soil.
  • Step 6: Observe progress. Avoid leaving soil crusts, which will make water rush over.

A sustainable water source must be identified and a pumping/irrigation system should be used.

Return on Investment Realisation Period
Crop Production
Fodder Production
Farm Income
Household Workload
Food Security
Soil Quality/Cover
Biological Diversity
Flooding
Crop/Livestock Water Availability
Wind Protection
Erosion Control
Increase Production
Less energy is required to irrigate crops, potentially reducing greenhouse gas emissions if generators used for pumping water.
Mitigate Greenhouse Gas Emissions
Effective flood irrigation can increase
Additional Information
PDF File
/sites/secondsite/files/tb/CCARDESATechnicalBrief_64_FloodingIrrigation_2019-10-17_0.pdf
Benefits and Drawbacks

Benefits

  • A flood irrigation system reduces weed growth and acts as preventive measure against spread of pests and diseases.
  • Requires less energy, so reduces costs. Gravity does the work, so less need for pumping.
  • Flood irrigation can work with lower-quality water because the water doesn’t contact with crop leaves, which is usually a concern with waste water.

Drawbacks

  • Requires larger amounts of water than other types of irrigation – only suitable in wetter climates.
  • Is considered more labour intensive as land must be closely managed, and prepared.
  • Land must be level, or manually/mechanically levelled.
  • Cannot effectively operate in sandy soils.
  • Very clay-heavy soil can easily become water-logged.
  • If not managed properly, can be very wasteful with respect to water.

Water Spreading Bunds

Value Chain
Annual Average Rainfall
Soils
Climatic Zone
Water Source
Decision Making
Farming Characteristics
Mechanisation
Labour Intensity
Initial Investment
Maintenance Costs
Access to Finance/Credit
Extension Support Required
Access to Inputs
Access to Markets
Gender/Youth Smart
Description

Water spreading bunds are barriers used on gradual slopes to slow down surface water and slow filter runoff, increasing the chance of infiltration, capturing runoff sediment, and decreasing soil erosion. Bunds can be built of different materials including packed earth or stones. Bunds can be spread across fields or used in micro-settings around individual trees or plants and should be applied in semi-arid or arid conditions. Bunds efficiently spread rainwater across the system and prevent streams from developing. Implementing bunds in areas with adequate rainfall or irrigation, may cause waterlogging and adversely affect crop growth.

Different types of bunds include:

  • Contour bunds: ridges of soil that follow slope contours and can be implemented at a large scale. Crops are cultivated between bunds.
  • Semi-circle bunds: ridges of varying size build in a half-moon or semi-circle. They are generally applied to rehabilitate rangelands and/or in the production of fodder.
  • Contour stone bunds: lines of stones laid in a shallow dug out areas that slow down the flow of runoff
Technical Application

To effectively Water Spreading Bunds the following should be carried out:

  • Step 1: Farmers should consider making earth bunds by hand, animal ploughs or mechanised ploughs.
  • Step 2: Contour bunds:
    • Contour lines must be plotted and marked prior to developing the bund.
    • A 40 cm deep infiltration pit is dug directly above where the bund will be plotted.
    • Bunds should be spread 5 m to 10 m apart.
    • Material from the infiltration pit will be piled and compacted to form a 25 cm to 30 cm in height with a base of 75 cm.
    • Soil is piled to form a ridge along the contour. The more significant the slope, the closer the bunds must be plotted.
  • Step 3: Semi-circle bunds:
    • Contour lines must be plotted and marked prior to developing the bund.
    • A centre point is chosen as diameter for the bund is selected (this could be 3 m or 30 m depending on the available space). From the centre point a string is used to stake out an even semi-circle.
    • Excavate a small trench before the bund and pile the excavated material. Pile and compact a bund wall, wetting it often to form the wall.
  • Step 4: Contour stone bunds:
    • Developed on less steep slopes.
    • Must have access to local stones.
    • Dig out a shallow ditch, 10 cm to 15 cm in depth.
    • Lay largest stones at the bottom of the ditch and pile smaller stone upward.
    • Step 5: Regular monitoring of bunds should take place, especially after rain events or after significant periods of time. Repairs should be done if any damage is found.
Return on Investment Realisation Period
Crop Production
Fodder Production
Farm Income
Household Workload
Food Security
Soil Quality/Cover
Biological Diversity
Flooding
Crop/Livestock Water Availability
Wind Protection
Erosion Control
Increase Production
Reduces soil erosion and enables farmers to maintain agricultural productivity.
Increase Resilience
Reduces soil erosion in higher rainfall environments, especially relevant as climates change.
Additional Information
  • The Food and Agriculture Organisation (FAO), 1991. Water Harvesting. Rome, Italy.
PDF File
/sites/secondsite/files/tb/CCARDESATechnicalBrief_28_waterSpreading_2019-10-17_0.pdf
Benefits and Drawbacks

Benefits

  • Water spreading bunds are implemented on slopes of varying degrees to slow the flow of surface water, increasing infiltration and nutrient capture.
  • Bunds capture water and spread it across an area more evenly, preventing streams, erosion channels and gullies from forming at depression points.

Drawbacks

  • Developing bunds can be laborious.
  • Bunds in areas with adequate rainfall or irrigation may cause waterlogging and affect crop growth.

Agroforestry: Alley Cropping

Annual Average Rainfall
Climatic Zone
Water Source
Decision Making
Farming Characteristics
Mechanisation
Labour Intensity
Initial Investment
Maintenance Costs
Access to Finance/Credit
Extension Support Required
Access to Inputs
Access to Markets
Gender/Youth Smart
Description

Agroforestry is a land management practice that combines the planting and management of trees and shrubs with crops and pasture, providing benefits of soil health, crop yields, resilience to climate change, biodiversity and economic opportunities. Agroforestry encompasses numerous practices, including silvo-pasture, agro-silvo cultural, and agro-silvo-pastural. One successful agro-silvo-cultural practice is alley cropping, where the farmer plants rows of trees, shrubs or hedges between crop rows. Usually hedges comprise leguminous plants intended to fix nitrogen in the soil and provide leaf litter and prunable biomass. The hedges are pruned with the pruned material spread on the ground, to reduce shading and competition with the primary crop. Timing of pruning is important to ensure that the pruned biomass releases nutrients to the soil at a time when the primary crop needs them for maximum crop productivity; e.g. when alley-cropping maize, the pruned biomass needs to breakdown with and release beneficial nutrients into soil from two and eight weeks after planting the maize crop. This approach has proven to be highly successful, with examples in Malawi where gliricidia was alley-cropped with maize where the prunings created a three-fold increase in maize production, which was increased a further 29 % when fertilisers were added. This fertilisation could be achieved with green manure, and other climate smart soil amendment approaches. The space and number of hedge rows to primary crop is dependent upon the field size and the regular growth height of the shrub/hedge. The hedge must not be planted so close that it shades the primary crop. In larger fields, larger deep-rooted timber trees can be planted between groups of rows of primary crop, providing soil benefits, reducing wind-speeds/erosion, and providing timber products.

This approach is considered climate smart as it increases productivity, provides a mechanism for more climate resilient farming, whilst increasing soil carbon levels.

Technical Application

While agroforestry practices are deemed highly beneficial and climate smart, it is important to ensure that proposed practices are appropriate for the specific context – the benefits of the agroforestry practice match the needs of the farmer - and are fit for purpose. Obtain advice from an agroforestry expert before embarking on secondary crop/hedge species selection.

To effectively implement alley-cropping the following should be carried out:

  • Step 1: Clearly understand the objectives of the intervention and identify an appropriate species for intercropping. For maize and sorghum in a smaller subsistence farm setting, selection and growth of hedge rows of a legumes such as cowpea or Gliricidia can provide sustainable benefits in terms of soil quality and secondary fodder/food products. In larger fields, timber trees can be planted every five to ten crop rows, depending on the height of the mature tree, and the shade-tolerance of the crop.
  • Step 2: Identify and understand key conditions, such as prevailing wind direction, and sunlight to ensure that the field is planted in an appropriate configuration, with primary crop and secondary (hedge/shrub/tree) crops planted in such a way as to benefit the primary crop and not compete with it. East to west row orientation should maxmise sunlight, topography permitting.
  • Step 3: For beneficial hedgerow growth with legume species such as Leucaena, cliricidia, and Sesbania sesban, the trees should be planted in rows between two and four metres apart, with individual trees planted as close as possible - between 10 to 15 cm apart. If planted closely, the trees will favour leaves over step growth, creating more mulch to prune for cover. Note that if rows are planted too closely, the secondary crop can dominate the available crop land reducing productivity. Furthermore, the closer the hedges, the more shade will present, which can depress crop growth, and also start to compete for soil water and nutrients, which is not beneficial.
  • Step 4: Once reaching sufficient maturity, after approximately six months (one-metre tall for legumes)– hedges should be pruned to generate mulch for working into the soil. Then the primary crop (maize) can be planted. Pruning once per month thereafter provides cover and ensures that light penetration is maintained. Planting legumes approximately six months before planting the primary crop can ensure that sufficient pruned material is available to incorporate into the soil to enhance growth.
  • Step 5: After harvesting the primary crop, hedgerows can be left to grow taller so that shade reduces weed grown, and to develop material to prune and incorporate into the soil again during the following crop cycle. However, hedges should not be allow to grow too high or dense as their roots will dominate the soil and out-compete primary crops for water and nutrients.

Before implementing any of these technologies, further research may be required beyond the guidance provided here. The World Agroforestry Centre (ICRAF) has many resources, toolkits and success stories that can support such research.

Return on Investment Realisation Period
Crop Production
Fodder Production
Farm Income
Household Workload
Food Security
Soil Quality/Cover
Biological Diversity
Flooding
Crop/Livestock Water Availability
Wind Protection
Erosion Control
Increase Production
Alley cropping and pruning of leguminous hedges increases productivity of primary crops such as maize.
Increase Resilience
Helps farmers to be more resilient to climate change, by sustaining productivity and controlling soil health, especially when faced with changing climates.
Mitigate Greenhouse Gas Emissions
The planting of alley hedge rows of legumes and the introduction of pruned material contributes more carbon to the soil.
Additional Information
PDF File
/sites/secondsite/files/tb/CCARDESATechnicalBrief_17_AgroForestry_2019-10-17_0.pdf
Benefits and Drawbacks

Benefits

  • Trees, shrubs, and hedges are incorporated into farming systems and have many different biophysical and socio-economic benefits.
  • Use of leguminous hedges no only provides pruned materials to provide cover, but they also help fix nitrogen in the soil.
  • Hedges planted in alleys can also provide other benefits such as edible seed pods for human or animal consumption.
  • Hedges and trees can reduce soil erosion from run-off or wind erosion.
  • Alley cropping can provide opportunities for diversified income – selling secondary crops and/or timber.
  • Alley cropped timber trees can provide building materials fire wood.

Drawbacks

  • Initial labour requirements will likely be significant; however, this will be primarily at the earlier stages of the intervention.
  • Ongoing maintenance such as pruning and maintenance of hedges will be needed, although relatively minimal.
  • There may be some costs involved in obtaining hedge seedlings.
  • Use of trees rather than hedges and shrubs introduces more labour, but yields more benefits.

Contour Planting

Value Chain
Annual Average Rainfall
Soils
Climatic Zone
Water Source
Decision Making
Farming Characteristics
Mechanisation
Labour Intensity
Initial Investment
Maintenance Costs
Access to Finance/Credit
Extension Support Required
Access to Inputs
Access to Markets
Gender/Youth Smart
Description

Contour Planting is a planting strategy for sloping fields, where crop rows follow slope contours rather than planting in rows up- and down-slope. The primary aim of this strategy is to slow the downhill flow of water and encourage the infiltration of water into the soil. Slowing the flow of runoff water reduces soil erosion and therefore also nutrient loss.

Contour Ridges are created by tilling, ploughing or hoeing soil to establish ridges along contour lines, acting as a barrier to downhill water runoff and other erosive processes - the higher the ridge height, the more effective the barrier is to preventing soil erosion.

Contour Strips involves use of vegetative barriers e.g. planting of strips of grass or hedges and other species to secure soil and further prevent erosion. These practices are labour intense and require extension support, especially as contour lines are not straight but follow slope characteristics, correctly identifying contour lines is important and can be done using the ‘low-technology’ options that are identified in the Technical Application section of this Technical Brief.

Technical Application

To effectively undertake contour planting:

  • Step 1: Construct an A-frame that has a plumb-line with a rock hanging down the centre. The base of the A-frame should be 90 cm.
  • Step 2: Calibrate the A-frame on flat ground. Ensure that both legs are on the ground. Mark where the plumb line meets the cross bar.
  • Step 3: On a slope, working perpendicular to the slope, plant one leg of the A-frame and swing the other leg around until the plumb line meets the mark on the cross bar. Drive a stake into the ground where the first ‘planted’ leg is and continue the process across the slope.
  • Step 4: Once the extent of the contour has been staked, tie a string from post-to-post across the slope; this identifies the contour to be planted.
  • Step 5: Plant selected crops, develop contour ridges or plant contour strips along the contour line.
  • Step 6: Subsequent contours should be spaced 3-5 m up or downhill of the preceding contour line. To determine the length between contour lines, measure off the top of each stake to a stake up or downhill with a tape measure or accurately measured third stick.
  • Step 7: Contour ridges can be implemented like Water Spreading Bunds (Technical Brief 28) to form ridges of soil that are formed by tilling or ploughing and can be left after land preparation to further prevent erosive forces. Crops can be planted between these ridges.
  • Step 8: The planting of contour strips can be implemented by planting grasses or hedges 20 m (shallow slopes) to 10 m (steeper slopes) apart up or downhill, similar to Trash Lines (Technical Brief 14). This intercropping allows for erosion control and can be used as fodder for livestock.
Return on Investment Realisation Period
Crop Production
Fodder Production
Farm Income
Household Workload
Food Security
Soil Quality/Cover
Biological Diversity
Flooding
Crop/Livestock Water Availability
Wind Protection
Erosion Control
Increase Production
Retaining soil structure enables farmers, particularly those planting on sloping fields to maintain productivity.
Increase Resilience
This land management practice aid farmers to maintain soil structure in the face of changing climates and shifting rainfall patterns.
Additional Information
PDF File
/sites/secondsite/files/tb/CCARDESATechnicalBrief_16_ContourPlanting_2019-10-17_0.pdf
Benefits and Drawbacks

Benefits

  • Contour planting prevents erosion on sloped fields and efficiently trap runoff water.
  • Contour planting improved water infiltration and contour ridges improve water retention.
  • Contour planting can be integrated with intercropping contour strips of grass or hedges to help maintain soil structure.

Drawbacks

  • Contour lines are extremely labour intensive and take a significant amount of time to implement.
  • During contour measuring and development, land may be exposed to erosive forces.

Trash Lines

Value Chain
Annual Average Rainfall
Climatic Zone
Decision Making
Farming Characteristics
Mechanisation
Labour Intensity
Initial Investment
Maintenance Costs
Access to Finance/Credit
Extension Support Required
Access to Inputs
Access to Markets
Gender/Youth Smart
Description

Trash lines are the incorporation of lines of organic materials spread across contours of hilly agricultural fields - strips of heaped straw or weed materials that have been collected during primary cultivation of the land. Trash lines have been found to direct runoff in field and act as an erosion control method. Through decomposition, the trash line material acts as a type of compost adding nutrients to the soil, adding more organic material year on year, should the farmer continue to build this line. This is a climate smart approach as it contributes to soil health, capturing more nutrients and carbon in the soil, and in turn promoting sustainable agricultural productivity. In changing climates, implementation of this practice can contribute to adaptation strategies.

Technical Application

To effectively undertake trash lines:

  • Step 1: Collect straw, stalks, picked weed or other organic materials from field or surrounding area.
  • Step 2: Establish contour lines using method identified in contour planting (Technical Brief 16).
  • Step 3: Contour lines for trash lines should be spaced between 5 to 10 m apart.
  • Step 4: Heap straw along contour lines on hilly or sloped fields to be approximately 0.5 m wide and up to 0.3 m in height.
  • Step 5: Trash should be piled on annually or as the field is prepared. Lines can be maintained for a few years and then decomposed materials can be mixed into the soil.
Return on Investment Realisation Period
Crop Production
Fodder Production
Farm Income
Household Workload
Food Security
Soil Quality/Cover
Biological Diversity
Flooding
Crop/Livestock Water Availability
Wind Protection
Erosion Control
Increase Production
Contribute to soil health and therefore agricultural productivity.
Increase Resilience
In changing climates, strategies such as this can contribute to retain and improving soil health.
Mitigate Greenhouse Gas Emissions
Helps retain carbon in soil.
Additional Information
PDF File
/sites/secondsite/files/tb/CCARDESATechnicalBrief_14_Trashlines_2019-10-17_0.pdf
Benefits and Drawbacks

Benefits

  • Low cost option for soil and water conservation on sloped fields.
  • Increase of organic materials in fields.
  • Green manure (Technical Brief 02) production in the field.

Drawbacks

  • Increased workload to implement trash lines but low effort to maintain.

Erosion Control

Value Chain
Topography
Climatic Zone
Water Source
Decision Making
Farming Characteristics
Mechanisation
Labour Intensity
Initial Investment
Maintenance Costs
Access to Finance/Credit
Extension Support Required
Access to Inputs
Access to Markets
Gender/Youth Smart
Description

Erosion control measures are practices designed to reduce runoff water and wind erosion that wash away top soil and nutrients, degrading soil biodiversity and reducing agricultural productivity. Erosion is a natural, biophysical process resulting from rainfall, water flows, wind, or storm runoff. Erosion is integral to the formation of soils, however human and animal activity, including agriculture and clearing of land, can accelerate erosive processes, drastically impacting landscapes, soils (e.g. quality) and watercourses. In addition, erosion control measures can contribute to reducing rainfall runoff, increased water infiltration into the soil, and attenuates flooding. The intensity of rainfall is directly correlated with the severity of soil erosion; hence, this is a significant problem across the Southern African region as much of the rainfall in the region is episodic, and intense. To prevent or reduce erosive processes control measures can be incorporated into farming systems to reduce or reverse degradation and potentially restore or improve soil quality. Erosion control measures aim to mitigate soil erosion and improve soil fertility by reducing flow and speed of run-off to avoid soil being washed away. Erosion control can be initiated through a number of interventions, including, but not limited to, intercropping (e.g. planting cover crops), mulch, conservation tillage and reforestation, as well as terracing, soil bunds, etc.. Example: Stone Bunds. Lessons learned from West Africa show that stone bunds constructed along contour lines in fields and in key run-off locations can significantly reduce run-off, particularly in steeper agricultural fields. The stone lines reinforce the soil structure in the field following the contours of the land, reducing the speed and volume of run-off, thereby reducing the likelihood of erosion. This is an appropriate technology to implement on slopes up to 15 to 20 degrees. This is considered a climate smart practice as it maintains soil structure and nutrients, in turn retaining carbon in soil, enabling farmers to adapt to climate changes and sustain agricultural productivity.

Technical Application

Without a topographic survey, this technology may require trial and error to begin with, to see how rainfall and run-off responds to the contouring. To effectively implement erosion control measures the following should be carried out:

  • Step 1: Perform a thorough local study of the landscape, soils, land use and erosive processes that most impact the area: steep slopes, flood plains, high winds etc.
  • Step 2: Source a large number of stones, preferably five to ten centimetres square blocks (from a quarry) or five to ten-centimetre diameter cobbles (from a river-bed). You will need 30 to 50 tonnes of stone per hectare for contour bunds approximately 300 metres long.
  • Step 3: Mark out contours, as discussed in Technical Brief 16 Contour Planting.
  • Step 4: In larger fields with shallower slopes, place stones in rows of two along contour line, interlocking alternately, burying the lower half. The bunds can be between 25 and 40 metres apart. On steeper slopes, stack and bury stones against or in vertical/near vertical walls of contours much closer together (five to ten metres apart) to reinforce them.
  • Step 5: Make sure that stone bunds follow the contours from one side of the field to the other, ensuring that no ‘pour’ points (larger gaps) exist along the way, lining the drainage channel or weir from one contour to the next with stones to avoid or reduce scouring in these locations.
  • Step 6: Following, and if possible, during rainfall events, check the stability of the slope, adjusting stone bunds where necessary.
  • Step 7: At the end of the rainy season and again following harvest, review the performance of the technology, and prepare for the next growing season.
Return on Investment Realisation Period
Crop Production
Fodder Production
Farm Income
Household Workload
Food Security
Soil Quality/Cover
Biological Diversity
Flooding
Crop/Livestock Water Availability
Wind Protection
Erosion Control
Increase Production
Increased water infiltration can extend growing period and mitigates short dry spells. Can reduce flood risk downstream.
Increase Resilience
Increased production due to improved nutrient availability and higher nutrient use efficiency.
Mitigate Greenhouse Gas Emissions
Depending on practices used, may lock more carbon into the soil.
Additional Information
PDF File
/sites/secondsite/files/tb/CCARDESATechnicalBrief_11_ErosionControl_2019-10-17_0.pdf
Benefits and Drawbacks

Benefits

  • Erosion control measures prevent the loss of top soils and nutrients.
  • Can help farmers adapt to changes in climate that have include increased rainfall amounts and intensity.
  • Can reduce the impact of wind erosion.

Drawbacks

  • Erosion is a natural process that can be increased due to human and animal activity.
  • Requires substantial labour inputs to construct bunds and other erosion control measures
  • Maintenance is also needed.

Green Manure

Value Chain
Climatic Zone
Water Source
Decision Making
Farming Characteristics
Mechanisation
Labour Intensity
Initial Investment
Maintenance Costs
Access to Finance/Credit
Extension Support Required
Access to Inputs
Access to Markets
Gender/Youth Smart
Description

Green manure (otherwise known as cover crops), is a climate smart fertiliser process that involves growing plants (mainly legumes) and distributing uprooted or sown crop-parts to wither and cover soil. It provides soil coverage to enhance biological, physical and chemical properties of soil while mitigating soil erosion, supressing weed growth, adding biomass to soils, improving soil structures, promoting biological soil preparation, and reducing pests, diseases and weed growth. These functions can increase economic return, reduce the need for herbicides and pesticides, while increasing productivity and potentially the quality of crops. It can also increase soil nitrogen, improve soil fertility, conserve soil humidity and reduce fertiliser costs. Green manure also has low management costs, presents good conservation characteristics, and improves biodiversity. Green manure is a feasible and sustainable option for farmers to improve soil quality and productivity, depending on local context and availability of different leguminous plants that best fit for farmers’ cropping systems. Examples of leguminous plants that can be used in southern Africa include: Mucuna (Mucuna pruriens); Sunhemp (Crotalaria juncea), Lab-lab (Lablab purpureus); Pigeon pea (Cajanus cajan); Cowpea (Vigna unguiculata) and Butterfly pea (Clitoria ternatea). Green manure has climate smart benefits as contributes to sustainable maintenance of agricultural production without the use of chemical fertilisers and depending upon the cover crop can contribute to adaptation of agricultural practices to climate change. Furthermore, coverage of soil with additional plant material can assist with carbon sequestration in soil. Not only does growing a secondary green manure crop provide a soil amendment benefit, but the crop can also be used as fodder for livestock. As the most common green manure plants are legumes, the pods and seeds can be fed to livestock while leaving the crop residue to perform the cover crop function in in the fields.

Technical Application

To effectively apply a green manure approach, the following should be considered:

  • Step 1: Select legumes that grow well under local conditions and in local soils. Green manure crops should be resilient and require few crop management practices. A thorough investigation should be made to ensure that green manure crops are appropriate for the local conditions in terms of rainfall, climate, soil pH and texture, and salt tolerance.
  • Step 2: Identify the appropriate time for planting the green manure crop to ensure growth, but not impacting the primary crop. Especially if the secondary crop is a climber/creeper. Main crop may need to be mature before planting the manure crop, as if a creeper, it may outcompete or constraint growth of maize or sorghum plants.
  • Step 3: If seeking to enrich soil properties, the farmer must allow crop residue to remain in the soil longer. This is particularly relevant with multiple uses – e.g. soil amendments and livestock fodder. In these cases, pods can be harvested for fodder, and the remaining plant residue left in the field to cover the soil.
  • Step 4: Crop planting should be alley cropped between the primary crop rows, allowing management of the primary and secondary crops, also reducing the competition between the primary and the secondary crop. If the secondary crop also has pest management properties, it may be beneficial to consider boundary planting.
  • Step 5: When harvesting the secondary crop, the farmer should consider leaving the residue in the ground. If it is uprooted, it should left on the soil surface. A common mistake is to remove it from the field and accumulate it in one location, missing the benefits of cover-crops, and exposing the residue to decay.

Unless local examples are available, small test plots should be used to test different cover crops to determine which is the most appropriate, and if necessary, demonstrate value to farmers and communities. As the secondary (green manure) crop is not a direct cash-crop, you may need to ensure expectations are measured. It may take several years to develop enough green manure crop to contribute to crop production; hence, crop production has to fit around existing cash/subsistence crops. Furthermore, benefits may not be realised within a single planting season., e.g. Nitrogen may only be available in the soil in the subsequent season.

Return on Investment Realisation Period
Crop Production
Fodder Production
Farm Income
Household Workload
Food Security
Soil Quality/Cover
Biological Diversity
Flooding
Crop/Livestock Water Availability
Wind Protection
Erosion Control
Increase Production
Green manure can maintain or increase agricultural productivity through improved soils.
Increase Resilience
Adjustment of practices to include cover crops allows farmers to diversify crop types, and produce their own fertilisers.
Mitigate Greenhouse Gas Emissions
Reduction in carbon released from soil.
Additional Information
PDF File
/sites/secondsite/files/tb/CCARDESATechnicalBrief_02_GreenManure_2019-10-17_0.pdf
Benefits and Drawbacks

Benefits

  • Green Manure is a non-tillage method that promotes soil fertility through enhancement of soil organic content. In doing so, it mitigates erosion, maintains soil humidity, and promotes biological activity.
  • Many green manure plants can be used to feed livestock if there is an excess
  • Green manure cover crops also make organic matter to apply – compost requires work and time to develop, whereas this approach sees it added immediately.
  • Cover crops can reduce weed competition by shading soil.
  • If using legumes, they can thrive in poor quality soils.
  • Cover crops such as Cow pea can also be used for animal and human consumption.

Drawbacks

  • Require access to seedbanks for legumes and other viable cover crops.
  • May require the testing of crops in test plots prior to implementation.
  • If so, community action may be required to test varieties and make decisions.
  • Farmers may require more land to plant the same amount of the main crop, as they need to be intercropped with the cover crop. This can be unattractive to some farmers.

Compost

Value Chain
Climatic Zone
Water Source
Decision Making
Farming Characteristics
Mechanisation
Labour Intensity
Initial Investment
Maintenance Costs
Access to Finance/Credit
Extension Support Required
Access to Inputs
Access to Markets
Gender/Youth Smart
Description

Compost is a biological process where micro-organisms recycle decaying or decomposing organic matter to produce a soil conditioner that can be applied as an additive to improve soil conditions. Composting takes place in the presence of oxygen (aerobic conditions), and with adequate temperature and moisture, transforming organic matter into plant-available nutrients. Compost can comprise organic plant and/or animal matter, and/or residues including leaves, dead roots, manure, urine, bones, and nematodes, amongst other organic materials. As it is generally rich in nutrients, the application of compost can naturally fortify soils, acting as a fertiliser, with soil humus or natural pesticide increasing the resistance of plants to diseases, foreign species and insects. The amount of organic matter in different soils depends on the soil type, vegetation species, and other environmental conditions, such as moisture and temperature. Thus, the application of compost may add important nutrients to soils that can benefit vegetation growth. Rainfall, temperature changes and other biophysical factors may result in a diminishing return of compost benefits to soil health. Therefore, the application of compost to soils should be a continuous practice, in order to increase physical, chemical and biological benefits. There are two main composting systems: Open Systems (compost piles or pits) or Contained Composting – see technical application below. This is a climate smart approach as it recycles readily available organic materials from a farm for use within the farming system, plus it avoids the use of chemical fertilisers. Composting is a climate smart approach as it reduces the need for chemical fertilisers, contributes to soil amendments that support adaptation to climate change, and helps retain soil fertility, which in turn aids agricultural productivity.

Technical Application

To effectively undertake composting:

  • Step 1: gather compostable materials - rests of harvests, animal manure and dung, organic kitchen waste (fruit and vegetable waste), other food waste, edible oils and fats, wood shavings, paper products (not printed), hair cut waste. Avoid non-compostable materials such as chemical residues, glass, metals, plastics, carcasses, cooked leftovers or meat.
  • Step 2: Chop/cut materials to achieve optimum particle size is between 5 – 20 cm – this will assist decomposition. Wire mesh can be used to sift smaller non-organic particles.
  • Step 3: Add water regularly using a watering-can to assist decomposition, ensuring that the materials do not become water logged.
  • Step 4: Using a pitchfork or shovel, turn-over or rotate compost materials regularly as oxygen is a key component to the decomposition process.
  • Step 5: If available, add earthworms (known as vermiculture) to compostable material, which enriches soil, enhances plant growth (hence yields) and suppresses disease.
  • Step 6: Once compost material has been decomposed (three months to two years, depending on climate and composting material) it will be a fine, dark material. Screen the material to remove large particles and mix with soils in gardens or fields prior planting and around plants throughout growing period.
  • Step 7: If compost does not include animal manure/waste it can be applied to crops as an organic fertiliser at any point up to harvest. If it does include animal waste, it can be incorporated into soil not less than 120 days prior to harvest, especially where edible portion of crops has been in contact with the soil surface.

Additional notes:

  • For Open Composting System (Piles): select a level area or dig a pit with a level bottom away from developed areas, chop collected materials into piles, turn over or rotate and add water to material regularly (weekly or bi-monthly). Cover pile if there is heavy rain to prevent materials from washing away and becoming water-logged.
  • For Contained Composting Systems: construct a container unit from mesh, wooden panels, bricks and other suitable building materials, fill the container with chopped material, turn over or rotate, and add water to material regularly (weekly or bi-monthly). Keep compostable material covered.
Return on Investment Realisation Period
Crop Production
Fodder Production
Farm Income
Household Workload
Food Security
Soil Quality/Cover
Biological Diversity
Flooding
Crop/Livestock Water Availability
Wind Protection
Erosion Control
Increase Production
Retaining or improving soil fertility to ensure increased or sustained agricultural productivity.
Increase Resilience
As climate change places increased pressure on land management, compost can contribute to soil amendments to aid adaptation.
Mitigate Greenhouse Gas Emissions
Use of compost to amend soil avoids the use of chemical fertilisers and reduces greenhouse gas emissions.
Additional Information
PDF File
/sites/secondsite/files/tb/CCARDESATechnicalBrief_01_Compost_2019-10-17_0.pdf
Benefits and Drawbacks

Benefits

  • Composting is an effective and low-cost option to recycle organic matter that can improve soil nutrient health.
  • Composting in scalable, based on need and available organic materials.
  • Moisture and oxygen are very important. Ensure that compost materials are moist and regularly rotated to optimise decomposition conditions.
  • Cover during extreme weather events (heavy rain, extreme heat, high wind etc.).
  • Add earthworms to the material to increase decomposition and speed up process.
  • Compost should be regularly added to soils to increase soil organic nutrients.

Drawbacks

  • Developing productive compost material, with beneficial nutrient is not a quick process, and can take up to two years for productivity to reach optimal outputs.
  • Faster methods require more energy and inputs as significant amounts of organic material is needed, material must be shredded/chipped, and compost piles need to be turned every three days.
  • While composting is scalable, the amount of available organic material may be a limiting factor.
  • Composting plant material must include removal of any diseased plant material and weed seeds should be avoided.
  • Earthworms will need to be sourced to improve the productivity of composting operations.

Earthworms can be sourced from a worm farm – if worm farms are not available, you can create your own by purchasing worms from an agricultural supplier. Worm farms can also be purchased as kits.

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