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Improving soil organic matter

When plant material and manure are mixed into the soil, they are decomposed and partly transformed into humus. Humus serves many purposes, for example:

  • It acts as a reservoir of nutrients. The nutrients are released to the plants in a balanced way, which contributes to good plant health. Soil organic matter is the main nutrient pool for the plants beside nitrogen from symbiotic fixation.
  • It increases the water holding capacity of the soil as it acts like a sponge with the ability to absorb and hold up to 90 % of its weight in water.
  • It causes the soil to form strong complexes with clay particles, which improve soil structure and thus increase water infiltration, making the soil more resistant to erosion. Better soil structure also enhances root growth.
  • Humus improves the exchange capacity for nutrients and avoids soil acidity.
  • Soil biological activity is enhanced, which improves nutrient mobilisation from organic and mineral sources and the decomposition of toxic substances.
  • Mycorrhizal colonisation is enhanced, which improves phosphorus supply.
  • Compost has the potential to suppress soil borne pathogens, when applied to the soil.

Plant nutrition in organic farming relies on sound humus management. Proper management of soil organic matter requires some basic knowledge of the dynamics of soil organic matter. Aeration of the soil in combination with humidity and high temperature create favourable conditions for soil organisms and result in high biological activity enhancing decomposition of organic matter in the soil. Under dry and cool conditions soil biological activity is strongly reduced resulting in a reduction or even in a standstill of transformation processes. Managing soil organic matter for plant nutrition and soil organic matter level means knowing, when and how to manage temperature, oxygen and moisture conditions of the soil and interfering (or not interfering) to stimulate or calm down decomposition and build-up of soil organic matter. Excessive tillage for example stimulates decomposition of soil organic matter, whereas cooling the soil with a soil cover slows it down.
Building soil organic matter is a long-term process, but investing into it is highly benefi cial to crop or forage production, and contributes to higher and more reliable yields.

There are different ways of maintaining or improving soil organic matter:

  • Growing green manure, mostly legumes, for the amount of biomass they build. Before fl owering they are cut and worked into the soil.
  • Intercropping cover crops such as velvet bean, Tithonia, lablab and others as living mulch. The cover crop is regularly slashed, when it competes too much with the main crop.
  • Mulching with especially hard-to-compost or woody materials, like dry crop residues or green manure crops, which have been grown to maturity, also can ontribute to a slow increase of soil organic matter over time.
  • Trees and shrubs for agroforestry can be grown in the fi elds with crops where they are regularly pruned and the branches are used as mulch. They may also be planted on the edges of a field or on fallow plots.
  • Residues from harvested crops in the form of husks, leaves, roots, peelings, branches and twigs should be returned to the fi elds either as compost, as mulching materials, or for incorporation into the soil.
  • Depending on the fi nancial situation of the farm, additional materials from agro-processing like wood shavings, or coffee or rice husks, or from food industry like seed cakes can be purchased.
  • Integration of livestock helps to quickly improve soil organic matter, when livestock excreta and bedding are properly recycled.

The amount and the quality of organic matter supplied to the soil influence the content of organic matter in the soil. A regular supply of organic matter provides the best conditions for balanced plant nutrition. Estimates say that in humid tropical climates 8.5 tons, in sub-humid climate 4 tons, and in semi-arid 2 tons of biomass are needed per hectare and year to maintain soil carbon levels of 2, 1 and 0.5 % respectively.
Burning organic residues and standing dead biomass (such as crops left on a field) is a crime to the environment! All the benefits that may be derived from incorporating organic matter are lost and, if the plant material is burned, the atmosphere is polluted. The ashes contain nutrients that are directly available to the plants; however, large amounts of carbon, nitrogen and sulphur are released as gas and are lost. The nutrients in the ash are also easily washed out with the first rain. The burning also harms benefi cial insects and soil organisms.

Identifying sources of biomass

The majority of the farmers by far do not exploit the potentials of on-farm production of organic soil inputs. Realizing the potentials of farm-own resources can be essential for long-term sustainability of the farm, as it helps to reduce the cost of buying organic materials like manure or mineral fertilizers. Instead of buying farm inputs the farmers may use part of the savings for buying seeds for green manures and feed plants or for purchasing own livestock.
Due to limited landholdings and lack of livestock, some of the farmers may be unable to produce adequate quantities of green manure and compost. These farmers will depend on outside sources of organic materials to maintain the fertility of their soils.

Proposed Group Exercise: Identifying local sources of biomass

Identify the farm sources of biomass in the local context, which can be used for soil fertility management.

  • Is animal manure available? If yes, how is it used?
  • Are harvest residues recycled on the field? Or are they fed to livestock and recycled as manure? Or are they composted?
  • Do the farmers grow green manures?
  • Are there any other sources of biomass that have remained unused so far, such as prunings of leguminous trees, nutrients from fish ponds or others?
  • Are there any nearby sources of organic by-products or wastes from food processing such as seed cakes, fish meal or bone meal that may be used?Are there any commercial livestock producers in the area to source animal manure?
  • Are there any large scale producers of compost in the area?
  • Is there any source of wastes from crop processing such as coffee pulp?

Discuss with the farmers potentials and constraints of increasing supply of organic materials to the soils using farm-own sources of biomass more efficiently, increasing own production of organic soil fertility inputs, or introducing inputs from
nearby sources. Clarify as to whether the farmers have the ability or interest of purchasing feed-based biomass or commercial organic fertilizer.

Green manuring

Challenges and constraints

Green manuring means growing plants with the primary purpose of incorporating their biomass into the soil to supply “organic food” to the soil to improve its nutrient content and thus its fertility. Cover crops and green manures are near synonyms. While the main purpose of growing cover crops is to cover the soil with a low vegetation cover to protect it from exposure to sun and rain as well as to suppress weeds, green manures are grown with the main purpose to build maximum biomass.
Green manures play a key role in organic farming. They are an invaluable source of food for soil organisms and thus of nutrients for the following crop. They are a farm-grown fertilizer and, therefore, are a cheap alternative to purchased fertilizers. Green manures complement animal manures well and are of high value on farms where animal manure is scarce. Green manures can provide an incentive to abandon harmful traditional practices, such as burning crop residues or allowing animals to graze during the dry season, if their benefi ts are sufficiently largeIn Africa, the potential of green manuring is not nearly as well used as it could be. Farmers in some regions of Africa have practiced green manuring in their traditional farming systems since a long time, for example by undersowing legumes and composites in ripening millet fi elds. In some regions farmers collect tree leaves and incorporate them into the soil of arable land. Though grain legumes, particularly cowpea, occur widely in traditional cropping systems, few farmers use the legumes for soil fertility management. Usually legumes are cultivated in relatively intensive production systems only, where farmers are oriented to markets. Most African farmers, who grow crops for subsistence, grow legumes only if they provide valuable food.
Challenges and constraints related to the adoption of green manuring:

  • The main reason for the lack of broader adoption of green manures in Africa is due to the need of many farmers for an immediate economic product, such as grains, from any crop that is grown. While legumes that are grown for harvesting the grains are grown to maturity of the plant, green manures are ideally harvested when they are still green and have produced maximum biomass.
  • In spite of the advantages of green manures, many farmers cannot afford to give up cropland to grow a soil amendment on an entire or part of a fi eld, due to scarcity of cropland. Legumes are only grown in rotation, if the added benefit from them is very high, for example that it can be used as fodder or marketed. Growing green manures among traditional row crops (intercropping) is more common, as it allows growing green manures without reducing land for other crops. Or green manures are relay intercropped, when crop harvest nears. This avoids competition between the crop and the green manure, as the green manure will primarily grow during the dry season. Or green manures, for example jack bean or velvet bean, are grown in alleys.
  • Water may be considered the limiting factor to growing a green manure crop in arid and semi-arid climates. Fact is though, that growing green manures requires far less water than is needed for producing compost. The plants get the water themselves and take advantage of available rainwater.
  • Green manuring creates extra work.
  • Also, especially in the beginning, seeds may not be easily available.

Proposed Group Exercise: Assessment of alternative approaches to bio-mass production

Discuss alternative approaches to biomass or compost production for soil fertility improvement:

  • Production of large quantities of green manures for sale as livestock feed or compost production by individual farmers.
  • Bulk commercial compost production at strategic sites, as in proximity to irrigation schemes.

Benefits of green manures

  • Recycling of nutrients. Green manures contribute to recycling of nutrients. They help prevent nutrients from being washed out of the soil when they are grown in the rainy season. They take the nutrients up into their biomass and release them when they are ‘harvested’ and decomposed in the soil, making them available to the next crop. Ideal timing of slashing of green manures is required to avoid loss of nutrients.
  • Production of biomass. Green manures supply the soil with great amounts of fresh biomass. This material is easily decomposed by soil organisms – within about two weeks under humid and warm conditions – after having been incorporated into the soil. Most nutrients are then readily available to the plants. A small percentage is transformed into stable soil organic matter contributing to a better soil structure, better aeration, drainage and water and nutrient holding capacity of the soil.
  • Collection of nitrogen. Legumes and other nitrogen fi xing plants can provide considerable amounts of nitrogen to the soil and are particularly benefi cial. But legumes do not signifi cantly contribute to higher soil nitrogen contents when their grains and residues are removed for human and/or animal nutrition. If legume biomass or residue is burnt or fully exported from the fi elds where they are grown, negative nutrient balances arise. It is therefore important to ensure that all or part of the legume residues are retained in the fi elds, if soil organic matter content is to be maintained. In intercrops of legumes and cereal crops, cereals can take up some nitrogen from adjacent legumes. But evaluation of traditional cropping systems in Africa showed that rotation of legumes and cereals is by far more sustainable than intercropping of both.
  • Prevention of soil erosion. Green manures help to stop the soil from being carried away by wind and rain by providing a ground cover during their growth and a root system that holds the soil in place. As they contribute to increasing soil humus, they also contribute to better soil structure thus improving water infi ltration and reducing the susceptibility of the soil to being carried away by run-off water.
  • Suppression of weeds. Most green manure plants are fast growing and build a dense plant cover. This prevents weeds from growing beneath them and saves on time and labour which would otherwise be needed for weed control. Green manures, which leave a thick dry mulch cover at the end of their life cycle, can provide favourable conditions for planting of the following crop without any need for weeding or soil preparation.
  • High quality fodder. Some green manures can provide generous amounts of high protein fodder for livestock. This fodder can be especially valuable, if it is available during the last months of the dry season. Of course the value of the green manure for soil fertility improvement is reduced, if the above soil plant parts are used as fodder. On the other side the livestock will produce manure, which can be of high value, if it is handled properly.
  • No transportation. Green manures are mostly grown in-field and usually do not require transportation, in contrast to compost or other organic fertilizers.

Green manures are probably best suited to supply adequate amounts of biomass and nitrogen to arable land. But, if used as a sole soil fertility management measure, it may not be suffi cient to maintain or even improve soil fertility

Proposed Group Exercise: Assessment of local adoption of green manuring

Collect information among the farmers on the use of green manures:

  • Do they practice green manuring? If not, why not?
  • How do they integrate green manures into their cropping system?

Integration of green manures into the cropping system

Many farmers do not grow green manures because they do not know which species to plant and how to integrate them in their cropping system. It is, therefore, important to plan where, when and how to plant which species in order to obtain good results.
There are several ways of integrating green manures into the farming system:

  1. Food and non-food legumes can be intercropped with cereals and tree crops
  2. Short duration non-food legumes can be grown towards the end of the cereal growing season using residual moisture.
  3. Legumes are grown as short-term rotational fallow.
  4. Long term green manures are grown for more than one season.
  5. Or legume trees are grown in an agroforestry system to provide nutrient rich plant material.

a) Green manures in a crop rotation

Integration of green manures in crop rotations supplies nutrients to the rota tion and balances crops that take many nutrients out of the soil. Rotated green manures can also serve to break pest and disease cycles, when they are grown between closely related crop species.
Green manures can be integrated in a rotation whenever there is no crop in the ground, rather than leaving the land bare and allowing weeds to grow and nutrients to leach out of the soil. To prevent nutrients from the green manure leaching out of the soil before being taken up by the next crop, the time lag between digging-in the green manure and planting the next crop should not be more than two weeks in rainy periods. From a nutritional point of view, integration of green manures is particularly useful when they are grown before crops with high nutrient demand.

b) Intercropping or relay cropping in annual crops

Green manures can be grown underneath row crops such as corn, millet and sorghum. To avoid or reduce competition with the crop, green manures are usually sown toward the middle or the end of the growing season, when the crop is well established or near maturity. In relay cropped green manures major growth of the green manure occurs during the dry season after the harvest of the main crop. This procedure has the advantages that the green manure uses land that normally would not be under cultivation, and extends the period with a soil cover. In relay cropping sowing of the green manure is often combined with weeding of the crop, for example in maize after the second weeding. The green manure seeds are either broadcasted or are planted in bunches on hills.

c) Long term green manures

Green manures can be grown for more than one season in the following ways:

  • They can be planted in a bush-fallow system to restore poor soil. They are broadcast and left to grow uninterrupted for as long as required. The longer the period, the greater the benefit on soil fertility is.
  • They can be grown on new land before it is prepared for use, especially to help control diffi cult perennial weeds like couch grass and spear grass.
  • They can also be grown to produce large amounts of green plant material, which are then cut and carried to other fi elds, fed to livestock or used for composting. An example of such a perennial species is alfalfa (Medicago sativa).

d) Green manures in agroforestry systems

Agroforestry involves growing trees or shrubs together with crops. The trees or shrubs act as long-term green manures, where the leaves are spread on the field and dug into the top soil layer. For example, every sixth row, pigeon pea trees are intercropped with traditional grain crops. At the end of the season the crop residues are gathered under the pigeon pea plants and left for decomposition together with pigeon pea leaves. After six months the mixture is spread on the surface and incorporated into the soil.
Regular pruning of agroforestry trees, before or as soon as they flower, increases the amount of green materials obtained and reduces competition with the main crop.

Proposed Group Exercise: Discussion on advantages and inconveniences of green manures

Ask the farmers about their estimation of green manures. Do they see any other advantages to the ones mentioned? What impact do the legumes have on yields of subsequent crops? Have they contributed to increase of household food security? Have the farmers observed any changes in soil attributes? What constraints do they see to growing green manures? Is it worthwhile growing green manures, even if labour to sow and cut green manures must be hired and no money is earned to replace the money spent?

Selection of appropriate green manure species

Proper selection of green manures is essential to enable them to maximize their potential and minimize possible inconveniences like competition with crops. Green manures must suit the local climate, soil, and pest and disease situation, and fit into the cropping system. Therefore, when choosing green manure plants to use, the following aspects should be considered:

  • Annual green manures must be fast growing, have vigorous growth and be non-woody.
  • Green manures should grow well in the poorest soils and not need any fertilizer.
  • They must be adapted to local climate. In dry climates they should not need extra irrigation.
  • They must have few enough natural enemies and grow vigorously without any pesticides.
  • They should not be closely related to the incoming crop, as they could attract pests and diseases and affect the following crop. They should either be very shade-tolerant for intercropping or drought-resistant, when grown into or through the dry season.
  • They should fi rst cover the ground well to protect the soil and suppress weeds, and then climb stalks, if desired, but should not smother the main crop.
  • Leguminous green manures can collect considerable amounts of nitrogen. However, non-legumes can also be grown, as long as they produce enough biomass and develop a good root system. Non-legumes may also survive better in the local conditions, may grow faster and sometimes tolerate extreme weather conditions or poor soils.
  • Last but not least farmers may request that green manures provide food, if food is in short supply and little land is available.
  • The seeds should be readily available and affordable. For long term sustainability, farmers should be able to produce their own seed for the green manure crops. If the green manure crop is cut down before seeds have ripened, seeds must be produced on a separate small plot.

Some green manures may grow too vigorously and become weedy among the crop or even spread into new areas. This is especially true for plants that are not locally sourced. Normally, green manures with light seeds, which are easily blown away by wind, or creeping stems are problematic, as they may spread uncontrollably. Growing perennial green manures as annuals will prevent them from taking over other crops and growing in areas where they are not wanted. In case of unreliable climate, similar plants with different properties can be com bined with one variety having good drought-resistance.
The green manure should be able to produce enough biomass within the period the land is free (not under main crop production). Therefore, the species must be selected in relation to the period the land is free for the green manure to grow to flowering and decompose after cutting.
If a green manure is to be used for the first time in an area, it should be tried on a small plot fi rst to check how it behaves.
After cutting, the green manure plants can either be left to wilt for some days or incorporated into the soil immediately after cutting. Green manures should be worked into the top soil only.
Wilting saves on labour for incorporation, but results in some nutrient (nitrogen) losses. Incorporating the green manure should happen before the rainy season. In heavy soils, incorporation during the dry season may be diffi cult. If incorporation into the soil is diffi cult, the green manure can be cut down partially only when the rain comes and cut down entirely two weeks later. When grown in a rotation, the period between digging the green manure into the soil and planting the next crop should not exceed two weeks to prevent nutrients from leaching out of the soil.
In the case that green manures grow too old and tough to easily decompose by themselves, they may instead be cut in small bits and composted or used as mulch. Mulching releases nutrients slowly, but has other advantages of hindering weed growth, protecting the soil from erosion and reducing water loss through evaporation.

Proposed Group Exercise: Evaluation of green manure species for integration into the cropping system

Define together with the farmers criteria for the selection of green manure plant species for local use.
The following questions may guide you:

  • Is there enough land to grow green manures as a sole crop; or must they be intercropped in existing crops?
  • If they should be intercropped: in which crop(s) should they be integrated (cereals, a small crop, permanent crop)?
  • Is a short- or rather a long-term green manure more appropriate?
  • Is there need for additional food or a market for leguminous grains?
  • Should it suppress persistent weeds?
  • Should it leave a thick mulch?
  • Should it suppress nematodes?

Management of green manures

To keep farmland productive, green manures must produce at least 10 to 25 tons of fresh organic matter per hectare and year. Under favourable conditions common green manure species may produce up to the double amount of biomass and collect at least 80 kg of nitrogen per hectare and year.
Green manures are ideally allowed to grow up to fl owering stage. At this stage, biomass is highest and the plant material is still easily decomposed, as it is still green and not yet woody. If plants become too old and tough, they will be more difficult to dig under and soil organisms will fi nd it diffi cult to break the biomass down.
Instead of incorporating the legumes into the soil to directly improve fertility and soil moisture or enhancing the effectiveness of the legumes, they may be composted together with other plant residues and manure. When applied to the soil, the compost produced will be more effective in improving soil fertility and physical conditions such as structure and water infi ltration and hence will contribute to greater harvesting of rain water, and higher moisture holding capacity and soil aeration.
Another possibility is to use the material from green manures to cover the soil surface as mulch. Compared to incorporation of the plant material into the soil, mulch releases nutrients slowly, contributes to suppression of weeds, protects the soil from erosion, and keeps it moist during dry weather. In this case green manure plants are best grown through their full life cycle, as this will result in more woody plant material, which is better suited for mulch. Such an approach extends the period with a living plant cover and allows harvesting of large amounts of ripe seeds. The residues can then be allowed to cover the entire soil surface, or are arranged into strips along the contour, if another crop is to be planted.
Leguminous green manure species grow well in nitrogen defi cient soils. But they depend on the availability of sufficient phosphorus, the presence of the right rhizobium and suffi cient soil moisture. High pest and disease pressure can hinder proper development of the crop and production of reasonable grain yields. It furthermore requires use of healthy seeds, sowing at recommended planting distances or seeding rates, and the consideration of other management measures.
The following management measures may be relevant, when growing green manures:

  • If legumes are grown in a fi eld for the fi rst time, inoculation of the seeds with the specific rhizobia may be necessary to profi t from potential nitrogen fixation. Farmers can consult their extension agents for possible sources of and information on how to apply the rhizobium.
  • Continuous cropping of the same legume on the same fi eld may result in increase of pests and diseases and decline of performance of the green manure. Therefore, it is recommended to alternate between different species on the same field.
  • Performance of green manures also depends on seed rates and planting distances. Both can vary from one species to the other and must be tested for each individual situation.
  • Green manures need suffi cient soil humidity for germination and growth.
  • Leguminous green manures normally do not need additional fertilization.
  • Climbing legumes may need regular pruning.
  • The availability of nutrients and the impact on soil quality can be increase with a light top-dressing of compost (even of poor compost) to the green biomass, which is incorporated into the soil.

Proposed Group Exercise: Evaluation of green manure species for farm integration

List the species the farmers are familiar with and evaluate them based on the criteria selected together with the farmers.
Present further green manure species, if any highly valuable species are not mentioned.
Discuss with the farmers possibilities of integrating green manures into their cropping systems:

  • growing them in rotation with annual crops;
  • intercropping or relay cropping them in annual crops;
  • growing them on neglected land or using them for improved fallows;
  • introducing agroforestry trees or introducing green manures in agroforestry systems;
  • growing green manures alongside food crops.

Composting

Benefits of compost

Compost is a common name used for plant and animal material (mainly animal manure) that has been fully decomposed in a targeted process initialized and controlled by man. Compared with uncontrolled decomposition of organic material as it naturally occurs, decomposition in the composting process occurs at a faster rate, reaches higher temperatures and results in a product of higher quality.
Composting is a means of ensuring or improving long-term soil fertility, especially to smallholder farmers with no or little access to manures and fertilizers. Compost is more than a fertilizer. It is not just a nutrient source, but also acts on the structure of the soil and on its capacity to hold and provide nutrients and water. Its main value lies in its long-term effect on soil fertility.
Compost contributes to an increase of the organic matter content of the soil and thus to a better soil structure. It clearly enhances drought resistance of crops.
During the composting process diseases, pests and weed seeds are destroyed. Even viruses are destroyed, if a high temperature is reached. Thus, composting helps solve common problems associated to the management of plant residues. Compost also increases biological activity of the soil and its capacity to positively infl uence biological control of root rot diseases from fungi, bacteria and nematodes.
In the composting process nutrients are adsorbed into the organic matter, microorganisms and humus. The humic substances are relatively resistant to microbial decomposition. Thus, the nutrients are released slowly and are not easily lost. The total nutrient content of compost is similar to that of cow manure with an average nutrient content of 0.5 % N, 0.1 % P and 0.5 to 2 % K. Nevertheless, the values of compost cannot be estimated high enough. Compost has proven to be the best type of organic fertilizer in dry climates. It also increases the effect of even small amounts of manure. Defi ciencies of trace elements are less likely, when compost is applied, as compost contains trace elements as well. Compost also increases the availability of phosphorus to plants in soils rich in iron oxides. Due to its neutral pH, compost improves the availability of nutrients in acid soils. Where soils tend to be water-logged, composting helps avoid nitrogen losses occurring from incorporation of green plant material under such conditions.

Proposed Group Exercise: Discussion on investment into compost production

Discuss with the farmers advantages and constraints of compost production under local circumstances compared to green manuring, mulching and other approaches to improvement of soil fertility. Instead of making compost one-self, it may be purchased from nearby producers. Are there commercial compost producers in the area? Are their products suitable in terms of availability (quantity and distance to the farm), costs and quality (including the risks of heavy metal or other residues)?
Discuss the feasibility of such an approach and the acceptance of such products with the farmers.

Potentials and constraints of composting

From a farmer’s perspective, there are a number of reasons for investing time and effort into making good compost. Compost production is labour intensive, however, and demands regular attention. Collecting the composting materials, setting up the heap, regular watering and repeated turning of the heap make composting a very labour intensive activity. But the work can be done, when the farm’s labour forces are free. It is not restricted to a particular season. Livestock can greatly ease transportation of plant material to the composting area and when adding compost to the fi elds.
If labour requirements for compost production are considered, composting may not be economical when used on grain crops such as corn or millet, whereas compost application to vegetables or other cash crops may be highly worthwhile.
In African context, it is more economical to produce compost than to buy the equivalent amount of nutrients in mineral form. This is especially true if the compost’s effect on soil quality improvement is considered. On a basic level no or little cash is needed for compost production, as it relies on materials that are available on the farm and does not require special equipment for small scale production. This keeps the fi nancial risks very low, whereas expenditures for inputs prior to harvesting always bear a certain risk.
For composting, considerable quantities of water are needed to maintain humid conditions in the heap for development of decomposing bacteria. Scarcity of water or distance of the water source from the fi elds can be critical for compost making. If water is scarce, it should rather be used for composting than for irrigation, as this will result in a more effi cient use of water, because compost will improve fertility and water holding capacity of the soil in the long term. If little or no water is available to moisten composting material, compost heaps can be built during rainfall, heaping the wet materials. For easy watering, the composting area should be placed in proximity of a permanent water source. In general, it is easier to produce good compost during the wet season as the rain saves on labour for watering. Water harvesting can help to make water available for composting during the dry season.
Starting with composting may be diffi cult when organic materials are rare or competition for other uses of organic materials is high. In this case, special efforts would be necessary to produce more organic material in the farm growing hedges, establishing agroforestry systems and growing other plants to provide material for composting.
During the composting process the volume of the organic materials is halved. This means that a farmer needs 2 tons of organic material to produce 1 ton of compost. With biomass yields of green manure species like Mucuna being as high as 35 to 50 tons of fresh matter or 7 to 9 tons of dry matter per hectare, the amount of fresh organic material required to produce 1 ton of compost can easily be achieved from about 0.05 hectare.
Depleted soils in arid climates can be made arable again by applying 10 tons of compost per hectare over several years. Compost application should be limited to 40 tons of moist compost (or 25 tons of dry matter or 90 m3 ) per hectare in three years. Application of large quantities of compost, which is rich in wood parts, can result in temporary unavailability of nitrogen in the soil, and therefore would require additional application of a nitrogen rich source. Although contents in P and K are similar in compost (approx. 1.5 kg per m3 ) annual supply of 30 m3 of compost per hectare covers plant needs in phosphorus, whereas needs in potassium are covered by 20 % only. Total nitrogen content of compost is low (about 1 %) and only 10 % of it is easily available to plants.
Composting is an appropriate measure for soil fertility improvement, especially when soil fertility is low, land is scarce and organic materials, labour and a water source in proximity of the fi elds are available.

Proposed Group Exercise: Practical demonstration on compost making

Obtain the different materials required for compost making and demonstrate to the farmers how compost is made. During the compost making, explain to the farmers the main points to be considered.

The composting process

Properly made compost goes through three phases: the heating phase, the cooling phase and the maturing phase.

The heating phase: During the heating phase, within three days after setting up the compost heap, temperature in the center of the heap rises to about 60 to 70 °C. It usually stays at this level for two to three weeks. The high temperature is a result of the energy that is released during the decomposition of easily digestible materials by the bacteria. The warm temperature is typical and important for the composting process. The heat destroys diseases, pests, weed-roots and seeds and thus prevents their further propagation.
Due to the rapid development of their population, the oxygen demand of the bacteria is very high during this phase of the composting process. High temperatures in the heap indicate that oxygen supply is adequate. If temperature stays low or the compost develops an unpleasant odour, this can be an indication that the heap is compacted and oxygen supply is low.
Bacteria not only depend on oxygen, but also on humidity for their development. Due to the high biological activity and high evaporation, the humidity requirements are highest during the first phase of composting.

The cooling phase: After decomposition of the green plant material by the bacteria, the temperature in the compost heap declines slowly to 25 to 45 °C. When temperature declines, fungi settle and start the decomposition of straw, fibres and wooden material. As this decomposition process is slower, the temperature of the heap does not rise.

The maturing phase: During the maturing phase, red compost worms and other soil organisms start to inhabit the compost heap. Nutrients are mineralised and humic acids and antibiotics are built up. At the end of this phase the compost has lost about half of its original volume, has taken on a dark colour and the smell of fertile soil and is ready to use. Water requirements during this phase are low.
The longer the compost is stored, the more it will lose its quality as a fertilizer. Its capacity to improve soil structure, however, will increase.

Proposed Group Exercise: Practical demonstration on compost making

Obtain the different materials required for compost making and demonstrate to the farmers how compost is made. During the compost making, explain to the farmers the main points to be considered.

How to make compost

a) Selection of a suitable composting site

The composting process should be conducted in a place that is easy to access for easy transport of materials to the composting site and close to the fi elds where the compost is to be used after production, and next to a water source. A well-drained and levelled ground minimizes the risk of sieving out of nutrients by run-off rainwater. Natural shade such as a tree or a built shade reduces evaporation. An adjustable structure may allow its removal during rain.
There should be an appropriate distance from short term crops such as vegetables to avoid the risk of contamination, especially if animal waste is used.

b) Materials and tools for compost production

Ideally composting plant material is a mixture of 50 % different fresh green material and 50 % of dry material. The rate of coarse material should not exceed 10 %. If too much fresh material is used, aeration of the heap will be poor. As a result the heap will start to smell and nitrogen will be lost. If too much dry material is used, bacteria lack food and the composting process will not start. Larger quantities of dry material are thus best left in the fi eld to protect the soil surface from drying out and being washed away.
As most crop residues are low in nitrogen, sources high in nitrogen such as leaves of green legume plants or prunings from leguminous trees or legume stalks may be used to insure suffi cient nitrogen for the composting process. Also materials from shrubs such as tithonia, gliricidia, leucaena, sesbania, crotalaria and lantana leaves are good materials to use.
Whenever possible, plant materials should be composted together with animal manure. Addition of animal manure accelerates the composting process and results in compost with higher fertilizer value. Dung can be dissolved in or mixed with water and poured over the compost heap when preparing the compost. Urine and slurry, both rich in nitrogen, can encourage decomposition of dry material when poured over it.
Ashes can be spread in thin layers between the other materials. Too much ash, however, can result in gaseous nitrogen losses. Some earth or old compost can be used as well. Earth will adsorb escaping nitrogen well.
Where soils have the tendency to fi x phosphate, ground rock phosphate is best added to the compost, as it will be more readily available to the plants than if it is added to the soil directly.
Lime can be added in small quantities, but is in general not necessary for the composting process.
Tools needed for composting include a hand hoe, machete (panga), stick pegs, spade or forked hoe, watering can, wheelbarrow, sharp stick or compost thermometer (to monitor the temperature changes in the compost heap). For watering, a watering can or a sprayer should be used rather than a bucket, as this allows the material to better soak up the water.
Materials that should not be used for composting include materials from diseased or pest infested plants or plants that have been sprayed with pesticides or herbicides, materials with hard prickles or thorns, which may hurt the persons handling the compost. Persistent perennial weeds should not be composted either. Instead they should be destroyed by spreading them out in the sun to dry, or even burning. The dried material or ashes can then be added to the compost heap. Non-organic materials such as metal or plastic, rubber, leather and textile materials cannot be composted.

c) Compost making procedure

There are different methods for making compost based on different approaches and origins. They include the Indore and the Bangalore method, which were developed in India, the heating process/block method, the Chinese high temperature stack, the pit, trench, basket or the Boma composting. Each of these methods has advantages and disadvantages.
In the Bangalore method, the composting materials are mixed with urine, slurry or dung. The heap, once set up, is plastered with a layer of mud and is not turned. Due to the mud layer, the composting process becomes semi-anaerobic after a few weeks. The method is simple to use and needs little labour and water. It has fewer nutrient losses than the Indore-method, but may not destroy all diseases and needs more time to reach maturity.
In the Indore method the heap is turned twice. It is more labour intensive and needs more water than the Bangalore method, but has a shorter composting period. The materials go through an intensive heating phase.
In dry climates composting is mainly practiced in pits to keep the compost humid and save on water and labour for maintaining ideal conditions.
Vermi-composting uses specially introduced earthworms for decomposition.It is a good technique for recycling food waste and crop residues from vegetable gardens in the proximity of the house. The composting period is longer as compared to other methods and varies between six and twelve weeks.
In this manual only the heap/pit method and vermi-composting are described in further details.

How to proceed for making compost:

  1. Collect adequate quantities of the materials needed.
  2. Measure out an area 1.5 meters wide and of any convenient length. The width should enable to work with the compost without having to walk on it.
  3. Dig out a shallow pit of the planned size of the compost heap. The more arid the climate, the deeper the pit is usually dug. Compost pits should, however, not be deeper than 50 cm to ensure aeration. If no pit is dug in a humid climate, loosen the ground where the compost heap will be, as the materials need close contact with the loose soil at the bottom. The topsoil obtained when digging the trench should be carefully put to one side beside the trench so that it can be used in the compost.
  4. Woody materials should be chopped into pieces 5 to 10 cm in length or spread on a road or used as livestock bedding before composting to be bruised and increase its surface for better decomposition. Wet plant material such as sea-weed or fresh grass should be wilted before mixing it with other material. Straw should be pre-soaked in water, if possible. Ideally dry material is thoroughly mixed with urine and animal dung.
  5. Lay down the bottom layer of rough vegetation such as maize stalks or hedge cuttings. This layer should be about 30 cm thick. Such materials allow for air circulation into the heap.
  6. Then add a layer of mixed green material and animal manure (if available) followed by a layer of dry material. Then mix both layers and water well. The better the different materials are mixed, the better the composting process. Plant material infected with viruses should be placed in the center of the compost, and should be covered fast to avoid that the viruses are propagated to healthy plants by sucking insects.
  7. Repeat the process to build a heap to a height of 1 to 1.5 meters. Make sure to water each new layer well to create humid conditions. As for composting, aerated conditions are needed, the compost heap should not be stamped. A well-made heap has almost vertical sides and a fl at top. If you have a lot of materials, it is good to make several heaps of about 2 meters in length.
  8. To complete the pile, ideally cover it with 10 cm of topsoil to prevent gases from escaping from the compost pile. Lastly, cover the whole pile with dryvegetation or banana leaves to prevent loss of moisture through evaporation.
  9. Take a long, sharp, pointed stick and drive it into the pile at an angle. The stick helps to check the condition of the pile from time to time. If the stick is pulled out and is warm after two to three days, this indicates that decomposition has started. If the stick is white, this is an indication that the heap is dry inside. The heap should be turned and watered well.
  10. Do not grow cover plants such as pumpkin on the compost heap itself, as this dries it out. Plant them next to it.

How to maintain the compost heap:

  1. About every third day, depending on the weather conditions and if it has rained or not, the heap must be watered.
  2. If all goes well, the heap should be turned after 3 weeks, after the temperature of the pile has fallen. Compost heaps are usually turned 2 to 3 times in their early stages. When turning the compost heap, make sure the outside material comes inside. Thus, when turning the heap, fi rst take the material from the top and the outside to make the new heap. This procedure ensures that all parts of the compost go through a proper heating phase. Do not add new material during turning.
  3. After 3 to 6 weeks the heap should be turned again. By now the compost should have a fresh earth smell and no grass, leaves or animal droppings should be visible. Some woody branches or stalks may still be present, as they take a longer time to rot.
  4. In 3 to 6 weeks after the second turning, the compost should be ready for use. Mature compost turns blackish-brown in colour and has a pleasant smell. If the planting season is still far off, leave the pile covered where it is. The pile should always be kept moist and covered with dry material. If the heap becomes too wet it should be opened up and mixed with dry organic matter or allowed to dry in the sun before rebuilding.The decomposition process is quickened by adding large amounts of fresh animal manure and by turning the heap more frequently.

d) Applying compost in the field

In an African context, there is no such thing as too much compost. Usually the amount that can be produced by a smallholder farmer is rather small. So it is, therefore, important that compost be applied where the cultivated plants can use it and where it directly contributes to better plant nutrition and water retention. Efficiency of the compost can be improved through targeted application to the root zone of the crop plants through banding or placing into planting holes rather than spreading it over the entire fi eld. Labour requirements may be higher with targeted application, it may however result in higher productivity and help to reduce the size of land required to produce the required quantities of food.
In planted crops, compost is best applied into the planting holes and mixed with topsoil. Compost should be applied first to the crops with high nutrient demands such as tomatoes. In sown crops, compost is best brought out in the sowing rows prior to sowing and worked into the topsoil. In perennial tree crops, compost application is most effi cient when applied along the drip line of the trees (and not at the foot of the trunk). Good quality compost is ideal for seedbeds also. Compost should not be ploughed deeply into the soil. Compost can also be hoed into the topsoil as a top dressing.
Effect of nitrogen from compost is generally little and extends over a long period. Availability of nitrogen and other nutrients from compost can be increased, when the compost is supplemented by nitrogen rich liquid manure or fresh animal manure after its application before crops.
Compost that has not fully decomposed can be used for mulching between crops or around tree crops. It will continue to mature on the ground and organisms in the soil will draw it into the soil where it will decompose further. When using compost as mulch, it should be covered with a thin layer of straw or dry grass or leaves. This will avoid loss of nutrients due to direct exposure to sunlight and heat. Young composts are best applied to the soil together with nitrogen rich plant material like green manures, or they are applied before sowing a green manure crop.
The compost can be used immediately or stored for later use. Ripe compost for storage should be kept in the shade and covered with 10 cm of top soil to keep it humid and prevent loss of nutrients.

Vermicomposting

Vermicomposting is the method where compost is prepared using specially introduced earthworms, Red Wigglers (Lumbricus rubellus or Eisenia foetida), as agents for decomposition. In contrast to ordinary composting, vermicomposting is mainly based on the activity of worms and does not go through a heating phase. Vermicomposting is a good technique for recycling food waste and crop residues from vegetable gardens in the proximity of the house. It creates small volumes of very rich manure. Though vermicompost is very good manure, it requires more investment (a tank and worms), labour and more permanent care compared to ordinary composting. On the other hand, letting worms recycle farm or household waste saves time and labour input because no turning is required to keep the compost aerated.
Red Wigglers reproduce quickly, adapt well to life in a confined environment, and compost food rapidly as they consume their weight in food per day. They are three to five inches in length, dark red in colour, and will tolerate temperatures from 12 to 30 degrees Celsius. They prefer to live in the dark and moist places, and about half a kilogram of Red Wigglers is needed to start a colony.
The worms are very sensitive to fluctuations in moisture and temperature, however, and need a continuous supply of organic material for ‘food’. To protect the worms from predators, a solid base is needed as they are also attacked by ants and termites.
Some experienced farmers use ‘vermiwash’, the liquid collected from the compost heap after sprinkling, as a leaf fertilizer and plant tonic. This can even help plants to get rid of pests, such as aphids and diseases. Vermicompost can also be used to make compost tea.

How to proceed for vermicomposting:

Build a brick and mortar enclosure with a concrete bottom, one or two chambers and proper water outlets. Convenient chamber size is 2 m x 1 m x 0.75 m. However, the size of the chambers should be determined according to the volume of the composting material. Alternatively, a sizeable plastic or metal container or wooden boxes with a secure and removable lid to keep out predators and with ventilation holes on the side walls and holes on the bottom to release excess moisture from the container, but small enough to keep out fl ies if possible. The ‘four tank’ or ‘four chamber’ method of chamber construction is also commonly used because it facilitates easy and continuous movement of earthworms from one chamber with fully composted matter to a fresh chamber. Whatever container is used or built, it should be placed in a dark and damp place.

  • A layer of good moist loamy soil (vermin bed) is placed at the bottom, about 15 to 20 cm thick above a thin layer (5 cm) of broken bricks and coarse sand.
  • Earthworms are introduced (about 150) into the loamy soil, which the worms will inhabit as their home.
  • Then, a small quantity of fresh cattle dung is placed over the vermin bed.
  • The compost pile is then layered to about 5 cm with dry leaves or preferably chopped hay/straw or agricultural waste biomass such as vegetable peels, leftover food, dead leaves and plants. Egg shells can also be broken into small pieces and added to the pile.
  • For the next 30 days, materials are continuously added to the pit until it is full and is kept moist by watering it whenever necessary. Meat or fish scraps, greasy foods, dairy products or bones should not be added into the pile, as these will attract ants and rodents. The pile should be covered with porous material to keep off predators.

The compost should be ready within 60 to 90 days. The material will be moderately loose and not as heavy and with a dark brown colour.
In the two or four pit system, watering should be stopped in the first chamber so that worms will automatically move to another chamber where the required environment for the worms are maintained in a cyclical manner and harvesting can be done continuously in cycles.
To remove some of the compost, let the top of the heap dry out by discontinuing the watering for two to three days so that the worms move down to the cool base of the heap. Compost can then be removed and taken back to a fresh pile.

Proposed Group Exercise: Discussion: Is farmyard manure just a waste product?

Discuss with the farmers the role farmyard manure plays in plant nutrition in local farming systems. How is it stored, how is it applied? If possible, visit a local farmer, who practices appropriate treatment of manure. With the farmer and the group, discuss the advantages, constraints and possibilities for storing farmyard manure.

Farmyard manure

Farmyard manure commonly describes a more or less decomposed mixture of livestock dung and urine (mostly from cattle) mixed with straw and litter, which was used as bedding material. It may also contain residues from the fodder fed to the cattle and decomposed household waste.
Farmyard manure is an extremely valuable organic manure. Farmyard manure contains large amounts of nutrients. The availability of phosphorus and potassium from farmyard manure is similar to that of chemical fertilizers. Chicken manure is rich in phosphorus. When dung and urine from cattle are mixed, they form a well-balanced source of nutrients for plants.
Many farmers still underestimate the value of animal manure. In many places, it is dried and burned for cooking or just not recognized as a source of nutrients and organic matter. By drying or burning farmyard manure, large quantities of organic matter and nutrients are lost from agricultural systems. Appropriate recycling of nutrients on the farm, especially if it comes from a high-value source, is a principle of organic farming. Therefore, proper handling and use of animal manures are essential to ensure that the nutrients in the manure are preserved and the risks of causing environmental pollution are minimized.
Most farmers do not own animals, and neither do they have access to animal manure. Growing animal feed and integrating livestock into the farm not only provides milk and or meat and other animal products, but also some animal manure. In areas with mixed crop-livestock farming systems manure is likely to be available to most households, although at varying levels.

    Improving the value of animal manure

    Farmers should optimize the use and effectiveness of animal manure. Rather than apply raw animal manure, the farmers should be encouraged to compost the manure from cattle and other ruminants, while making liquid fertilizer from poultry manure, which is less suitable for composting due to its high moisture content.
    Farmyard manure is ideally collected and stored for a while before use. When used fresh the manure can inhibit crop growth considerably. Fresh manure can result in a temporary nitrogen lock-up, as it is used by the microorganisms to decompose the fresh manure, and it also does not contribute to improving soil humus. Animal manure with a small amount of litter is best composted or mixed with plant material for composting. Manure with a high proportion of litter, however, is best stored under anaerobic conditions. Compression of manure slows down decomposition and prevents overheating and thus reduces loss of nutrients. Collection of farmyard manure is easiest if the animals are kept in stables. For storage, the manure should be mixed with dry plant material such as straw,  grass, crop residues or leaves to absorb the liquid. Straw that has been cut or mashed by spreading it out on a roadside can absorb more water than long straw.
    The manure can either be stored next to the stable in covered heaps or pits. Or it is stored within the stable as bedding, provided it is covered with fresh bedding material. To minimize nutrient losses, the farmyard manure should be protected from sun, wind and rain. Ideally, a trench collects the liquid from the manure heap and the urine from the stable. A dam around the heap prevents uncontrolled in- and outflow of urine and water.
    Water-logging as well as drying out should be avoided. If white fungus appears (threads and white spots), the manure is too dry and should be dampened with water or urine. A yellow-green colour and/or bad smell are signs that the manure is too wet and not suffi ciently aerated. If the manure shows a brown to black colour throughout the heap, the conditions are ideal.
    Storing manure in pits is particularly suitable for dry areas and dry seasons. Storage in pits reduces the risk of drying out and the need to water the pile. However, there is greater risk of water-logging and more effort is required, as the pit needs to be dug out. For this method a 90 cm deep pit is dug with a slight slope at the bottom. The bottom is compressed and then fi rst covered with straw. The pit is filled with layers about 30 cm thick and each layer compressed and covered with a thin layer of earth. The pit is fi lled up until it stands about 30 cm above ground and then covered with 10 cm of soil.

    The quality and value of manure can be improved by the following approaches:

    • Proper design of the animal housing to facilitate easy and effi cient collection of manures.
    • Provision of adequate bedding material of straw or dry grass to capture as much excreta as possible. The more bedding is used the better.
    • Composted animal manure proves to be more effi cient on yield in acidic, sandy soils than when applied directly, even if nitrogen is lost in the composting process.

    Proposed Group Exercise: Discussion on investment in livestock

    Encourage a discussion with the farmers on investments in livestock production. Discuss benefits of integration of livestock in the farm including income generating options such as dairy production, increase of overall farm productivity and improved access to animal manure for crop production. Which challenges do farmers see?

    Resources and further readings

    Composting:

    • Preparation and use of compost. Agrodok 8. 2005. Agromisa Foundation, NL. www.agromisa.org
    • Enriched Compost for Higher Yields. CTA Practical Guide Series, No. 7. 2007: Technical Centre for Agricultural and Rural Cooperation CTA, NL. www.anancy.net
    • Composting in the Tropics. 1998. Henry Doubleday Research Association HDRA. www.gardenorganic.org.uk
    • Composting in the Tropics II. 2001. Henry Doubleday Research Association HDRA. www.gardenorganic.org.uk
    • On-Farm Composting Methods. R.V. Misra, R.N. Roy, H. Hiraoka. 2003. Food and Agriculture Organization of the United Nations FAO. www.fao.org
    • How to make and use compost. Sue Edwards & Hailu Araya. 2010. Food and Agriculture Organization of the United Nations FAO. www.fao.org
    • On-farm composting methods. R.V. Misra & R. N. Roy: Food and Agriculture Organization of the United Nations FAO, Rome. www.fao.org

    Green manuring:

    • Green fertiliser. Conservation Farming Handbook No.3. 2002. Study Circle Material. Land Management and Conservation Farming programme. Republic of Zambia. Ministry of Agriculture & Cooperatives
    • Green manure / cover crops for biomass transfer. Action sheet 39. www.paceproject.net
    • Green manure information leafl ets from CIAT-Africa. www.ciat.cgiar.org
    • Green manure. Farmers’ Training Notes. Kenya Organic Agriculture Network KOAN. www.koan.co.ke
    • Green manure crops. 1985. Echo technical note. Educational Concerns for Hunger Organization ECHO, US. www.echonet.org
    • Green Manure / Cover Crops and Crop Rotation in Conservation Agriculture on Small Farms. 2011. Plant Production and Protection Division. FAO. www.fao.org
    • Leaflets on green manure species. Henry Doubleday Research Association HDRA. www.gardenorganic.org.uk

    Use of animal manure:

    • Better manure, better crops. Kenya Agriculture Research Institute KARI, Henry Doubleday Research Association HDRA. www.kari.orgmers and extension workers in Africa. 2005. International Institue of Rural Reconstruction IRRI; African Conservation Tillage Network AC
    • Manure Handling and Storage. Study Circle Manual. 2004. Kasisi Agricultural Training Centre and Swedish Cooperative Centre. Zambia. www.loyno.edu; www.sccportal.org

    Soil fertility management:

    • Sustainable Land Management in Practice – Guidelines and Best Practices for Sub-Saharan Africa (2011). TerrAfrica, World Overview of Conservation Approaches and Technologies WOCAT and Food and Agriculture Organization of the United Nations FAO. www.wocat.net
    • Integrated soil, water and nutrient managment in semi-arid Zimbabwe. Farmer Field School Facilitators’ Manual, Vol. 1. 2005. Zimbabwe.  FAO. www.fao.org
    • Integrated Soil Fertility Management in Africa: Principles, Practices and Development Process (2009). www.ciat.cgiar.org
    • Managing Nutrient Cycles to Sustain Soil Fertility in Sub-Saharan Africa. 2004. Academy Science Publishers ASP in association with the Tropical Soil Biology and Fertility Institute of CIAT. www.aasciences.org
    • Guidelines and Reference Material on integrated Soil and Nutrient Management and Conservation for Farmer Field Schools. 2000. FAO. www.fao.org
    • Farmer Field Schools Facilitators’ Manual – Volume 1. Integrated Soil, Water and Nutrient Management in Semi-Arid Zimbabwe. 2005. FAO. www.fao.org
    • Sustainable Agriculture. Study circle material. 2007. Kasisi Agricultural Training Centre and Swedish Cooperative Centre. Zambia. www.loyno.edu; www.sccportal.org
    • Sustaining Growth. Soil fertility management in tropical smallholdings. 1994. Müller-Sämann & Kotschi. GTZ/CTA.
    • Soil fertility management. Agrodok 2. 2007. Agromisa Foundation, NL. www.agromisa.org
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