Introduction to integrated methods in the vegetable garden
chapter crop sol
Compost production for a vegetable garden
Click on ♦ to go to a page in the chapter
Analysis of the physico-chemical properties of cultivated soils ♦
. Texture and structure of cultivated soils ♦
. Clay-humus complexes and cation exchange capacity ♦
. Other interesting data that may be included in a laboratory analysis ♦
Influence of pH on the fertility potential of cultivated soils ♦
Humus; formation and evolution ♦
Soil fertility: is the apocalypse coming tomorrow? ♦
The microbial world and soil fertility ♦
Rhizosphere, mychorizae and suppressive soils ♦
Correction of soils that are very clayey, too calcareous or too sandy ♦
stimation of humus losses in cultivated soil ♦
⇒ Compost production for a vegetable garden
Composting with thermophilic phase ♦
Weed management in the vegetable garden ♦
To plow or not to plow? ♦
The rotary tiller, the spade fork, and the broadfork ♦
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Medium-term fertilising composts.
An optimal mixture of fresh organic matter for composting should be close to the following values: water 50 to 60%, C/N ratio 30 to 40, pH between 6.5 and 8.5 (1). To get as close as possible to these values, it is necessary to vary the sources of organic matter and adjust the proportions. According to standard NF U 42-001 A1, these composts are considered organic fertilisers. The diversity of fermentable domestic bio-waste, particularly from crop residues, grass clippings and kitchen waste, means that it must be combined with structuring biomaterials of complementary composition in order to produce medium-term humus compatible with market gardening. Far too much domestic plant waste is burned or sent to landfill when it could be used to produce compost after being shredded. There are also other interesting sources.
Wood chips from untreated sawmills can also be used as structural biomaterials (nowadays, sawmill oils are biodegradable (2) and are disposed of in thermophilic composting). Sawmill residues consisting of fine chips mixed with wood powder can be purchased at a low price. Composting sawmill residues, dead leaves and shredded hedge trimmings, mixed with highly putrescible organic materials, produces a humus comparable to mull. To do this, you will need approximately:
- 3 volumes of structural materials.
- 2 volumes of easily fermentable bio-waste.
- 1 volume of manure, when available.
It is not easy to present a model that is valid for everyone when it comes to precisely determining the volume of each material in these three categories, because for each type of organic matter, the C/N ratio varies considerably depending on the cultivation method, the time of harvest of the residues, the climate, etc. As a guide, grass clippings have an N/C ratio of between 10 and 17, kitchen waste between 10 and 25, vegetable crop residues between 15 and 25, manure between 10 and 19, leaves between 20 and 60, cereal straw between 50 and 150, and sawdust between 150 and 500.
In terms of the nutrient content of compost, the addition of dead leaves from large trees offers an undeniable advantage. Tree roots grow deep into the soil and provide trace elements from the decomposition of bedrock, which are found in dead leaves in the autumn. For this reason, I strongly recommend systematically adding tree leaves to medium- or long-term compost.
Composts producing long-lasting humus
Composts with a C/N ratio greater than 40 are produced from a large volume of organic matter rich in cellulose and lignin. These composts comply with standard NFU 44-051, which defines organic amendments intended for crop soil maintenance and the replenishment of organic matter stocks. These composts are useful in agriculture because they are known to evolve into very stable, long-lasting humus. However, they provide very few fertilising elements to the soil in the short term. Unlike medium-term humus, humus with a high C/N ratio contributes to nitrogen storage (3). However, the nitrogen, phosphorus and potassium content must be less than 3% in the raw product and the sum of these elements must be less than 7%. These composts have the advantage of producing C.A.H that are very stable over time, thus indirectly improving the fertility of cultivated soils.
The decomposition of biowaste lasts longer when it contains a lot of plant debris rich in cellulose and lignin; at least one year or more. These composts, when incorporated into the crop soil, can cause ‘nitrogen starvation’, which refers to the absorption of all the nitrogen reserves in the soil by bacteria to metabolise the excess carbon, resulting in a nitrogen deficiency for plants. However, some of the fixed nitrogen is released by the death of the bacteria when the soil C/N ratio becomes more balanced.
Nitrogen-enriched composts: are they truly organic?
Medium-term fertilising composts are richer in mineral salts that can be absorbed by plants. However, due to nitrogen losses during composting, the contribution of these fertilisers to plant nitrogen nutrition remains low unless corrected by adding a mineral or organic nitrogen fertiliser at the time of composting. Mineral nitrogen-enriched fertilisers sold in garden centres are called organo-mineral fertilisers. Their advantage is that they offer a synergy of effects due to their organic base and mineral supplement. The NF U 42-001 standard requires that these fertilisers contain at least 1% organic nitrogen of animal or vegetable origin.
Composts enriched solely with organic matter receive various types of manure during the composting process, some of which are rich in nitrogenous matter, such as poultry manure or guano. These composts, which are approved for organic farming (and can be found in garden centres, agricultural cooperatives and on websites), are not always truly organic, as most are produced from manure from conventional farms that use plants grown with synthetic fertilisers and pesticides.
The nitrogen reserve can also be replenished during the spreading of compost used as a base fertiliser by adding a mineral fertiliser.
Compost production and copper treatment of plants.
Organic waste that has been heavily treated with copper-containing substances such as Bordeaux mixture should not be added to compost, a situation frequently encountered in organic farming (e.g. apple tree leaves treated for scab, tomato crop residues treated for mildew). During the composting process, at least 80% of the organic matter is lost, but not the copper, which is not biodegradable. Ultimately, this results in a significant increase in the concentration of copper in the compost, which is toxic to the environment. The incineration residues of copper-treated plants cannot be recovered for the same reasons.
Compost replacing farm manure
The use of farm manure is not mandatory for improving garden soil. As the nitrogen content of grass clippings is generally higher than that of farm manure, the latter can be replaced by compost made from grass clippings or meadow grass mixed with organic matter that is richer in carbon. This means that straw can be recycled without going through livestock farms, which has another advantage: nitrogen losses are lower because one step in the recycling of organic matter is eliminated. For those who do not have enough grass clippings to compost, adding pelletised urea or ammonium sulphate (or ammonium nitrate for farmers) is more than enough to obtain a balanced compost.
Composting methods and local regulations
Before choosing a composting method (in a heap or using a composter), it is necessary to check local regulations (e.g. regulations for a group of municipalities or a housing estate) to find out about any restrictions. In France, home composting for recycling kitchen waste and garden waste does not require a special declaration. Many models of home composters have emerged in recent years, encouraged by local authorities. There are various models approved for home use, with some composters able to hold up to 900 litres of fresh organic matter.
Ammonia and methane production from poorly controlled composting
Regardless of the composting method used, whether cold or hot, it is important to note that a poorly controlled composting process can release large amounts of methane and/or ammonia. Ammonia is released into the atmosphere and/or dissolved in water, with the risk of being carried deep into the groundwater. Methanisation is a process of organic matter degradation caused by microorganisms in the absence of oxygen. Poor material selection and lack of periodic aeration are often the cause of these environmentally hazardous material losses.
It should be noted that losses of methane, ammonia and nitrous oxide cannot be avoided during composting. These losses are the cause of well-known environmental pollution from agriculture, which has worsened in recent years.
Here is an example of a composition by M.O.F for composting intended to improve the humus content of cultivated soil without using animal manure (a situation most often encountered by amateur gardeners):
- Organic matter that is more or less rich in nitrogen and highly fermentable (1/3): coffee grounds and tea leaves, crushed horn, dried blood, animal hair, hay, seaweed, freshwater plants that thrive in ponds, cereal grains, manure, fruit and vegetable peelings, easily decomposing dead leaves, non-straw crop residues.
- Carbon-rich organic matter (2/3): shredded oak or plane tree leaves, wood powder and very fine sawdust from sawmills, shredded hedge trimmings, cereal straw.
Composting must be initiated according to the procedures specified below for cold or hot composting.
Cold composting
Most individuals carry out cold composting by gradually accumulating organic matter. Composting takes place at low temperatures, facilitated by numerous useful organisms that colonise the bin. This composting is fed from time to time with kitchen waste, grass clippings, crop residues, dead leaves collected here and there, etc. Cold composting has major drawbacks :
- It does not destroy weed seeds or pathogens present in crop residues, dead leaves, peelings, etc., which requires a very strict selection of compatible materials. Animal product residues that could attract flies and produce unpleasant odours are specifically excluded.
- Adding manure to low-temperature composting is also not recommended, as manure contains many undigested weed seeds. Manure may also contain pathogenic microorganisms (and their spores) from infected plants.
When organic matter is removed from cold composting to be incorporated into garden soil, seeds often germinate if the gardener has incorporated kitchen waste such as melon seeds or grass clippings, proving that this composting system is not very effective due to the absence of a thermophilic phase.
Properly maintained composting is ensured by a large number of microorganisms that consume a lot of water and oxygen. The processes involved are complex and also depend on the nature of the organic matter and, to a lesser extent, on the outside temperature, especially for small volumes.
In a natural decomposition process, fungi are the first organisms to appear in compost. White filaments (mycelium) can be seen inside the compost. Macro-organisms (earthworms, insects, mites, myriapods, crustaceans, etc.) become involved when the temperature of the compost is not very high. These beneficial organisms harbour colonies of bacteria in their intestines, and it is believed that these bacteria play an important role in the decomposition of organic matter. Cold composting may experience a slight increase in temperature up to 30°C, which is compatible with the existence of beneficial organisms living in a mesophilic environment.
Worm composting is a variant of cold composting with the same drawbacks: pathogens and weed seeds are not destroyed. Worm composting is not described on this website as it does not reach the high temperatures required to sanitise compost.
Hot composting (composting with thermophilic phase)
Large-scale high-temperature composting in windrows or using appropriate equipment is subject to regulations designed to protect the environment and nearby homes. This type of composting is carried out by local authorities or companies. This type of large-scale composting, which requires specialised equipment, is not covered in this study. Below, I explain how to improve composting carried out using composters approved for domestic use (or when small-scale composting in piles is permitted) by adding a thermophilic phase to the composting process that has no harmful effect on the environment or the neighbourhood. In addition, composting with a thermophilic phase has the advantage of quickly reducing the sources of unpleasant odours, often accompanied by an army of unwanted flies, which are often found in approved household composters.
During the thermophilic phase, the organic matter located around the edges must be moved to the centre from time to time so that all the organic matter reaches a temperature of 55° to 65° for at least 15 days. Composting in piles is better suited to this sanitation process. Depending on local regulations, you may be required to abandon composting in piles in favour of a compost bin. Regardless of the composting method (pile or bin), the successive transfers of organic matter from the edges to the centre require the thermophilic phase to last at least 30 days. It should be noted that some pathogens are destroyed at 40°C (such as the potato rhizoctonia fungus), but the vast majority of pathogens are destroyed at a minimum temperature of 47°C (potato blight, fungi causing tomato stem or cucumber root rot, white rot of aubergines, etc.). In the laboratory, many nematodes are destroyed within a few hours at a temperature of around 45°C, but some pathogens require higher temperatures and/or longer periods of time. It is generally accepted that an average temperature of 60°C is required to eliminate the maximum number of pathogens.
Temperature is not the only factor responsible for eliminating pathogens. Certain substances produced during composting are toxic to pathogens. Antagonisms between pathogens and dominant thermophilic flora also play an important role.
High-temperature composting in summer requires a volume of organic matter of around 600 to 900 litres, which corresponds to the capacity of some composters authorised for domestic use. Below 600 litres, you will find it difficult to maintain a temperature above 50°C for 30 days. For 600-litre composters, avoid bins that promote heat loss (rectangular shape, walls that are too thin). Octagonal composters with thick walls and lids are preferable.
The larger the volume of the composter (over 600 litres), the easier it will be to achieve high temperatures. A 600-litre composter can only be used in summer due to its small volume and requires frequent renewal of highly fermentable organic matter during the thermophilic phase. The 800-litre Picumus and Compostys composters from Quadria, distributed by certain local authorities (4), are very well suited to this type of composting. Approved composters with the Afnor NF environment label, such as the 900-litre Thermo-King composter, which I recommend, can be found on websites or in garden centres.
Some wooden or plastic compost bins are best avoided: ridiculously thin wooden slats, fragile fastening systems that cannot withstand the pressure of organic matter, and compost removal doors that are too small, if they exist at all. You may be less disappointed if you build your own compost bin using pallets and reclaimed wood (check local regulations).

Bac à composter de 600 l
A 600-litre household composter with numerous holes to allow for proper ventilation, but it has the following drawbacks :
- Its elongated shape makes it difficult to turn over organic matter.
- The square shape does not allow for uniform humidity and temperature at the corners, resulting in the accumulation of poorly decomposed organic matter.
- The compost discharge doors are too small.
- The panels are pushed apart at the bottom by the pressure of the organic matter
- The system for fixing the panels using a few screws is too fragile, which meant that after two years of use, it had to be reinforced by installing steel brackets.
- This composter is still useful for storing fresh organic matter (while waiting for it to be processed in the thermophilic phase) or compost in the maturation phase.
High-temperature sanitation composting is very effective at destroying most pathogenic microorganisms (also known as phytopathogenic organisms) and weed seeds. At a temperature of 55/60°C, seeds are destroyed depending on their depth in the compost. At 30 centimetres, all seeds are destroyed within 24 days. At 90 centimetres, all seeds are destroyed in 3 days (5). With a few exceptions specified in the article “Pathogens resistant to the sanitation phase”, most pathogenic microorganisms are neutralised (fungi, bacteria and parasitic nematodes). Viruses such as the one that causes bean mosaic are also destroyed, even though they are more resistant to composting than other pathogens.
This type of composting requires a lot of fermentable material and nitrogenous products to reach a temperature of 55°/65°. Manure does not always contain sufficient nitrogen, requiring the addition of a nitrogen supplement. The use of mineral nitrogen fertilisers (urea or ammonium nitrate) is met with ideological resistance from environmental activists, even though this method is very reliable and inexpensive for safely recycling and sanitising most organic matter of plant origin. Dried blood and roasted horn, which contains 13% nitrogen, can be added, but this will make the compost much more expensive to produce. Adding a mineral nitrogen supplement compensates for the inevitable nitrogen losses due to ammonia volatilisation during the composting process. Without the addition of nitrogen supplements, the final compost may be unbalanced (low in nitrogen and rich in potash and phosphate). Composts derived solely from the decomposition of manure are known for their low nitrogen content. A nitrogen supplement is all the more necessary when the C/N ratio of organic matter is high.

Bac à composter de 900 l
900-litre Thermo-King composter with panels on the floor reinforced by vertical metal bars to prevent them from warping under the pressure of organic matter. The composter must be installed on a level, flat surface, otherwise the panels will warp and block the drainage hatches.
Avantage : deux trappes d’évacuation du compost bien dimensionnées, forme octogonale facilitant une uniformisation du compostage et le brassage de la matière organique avec un brass’compost. Volume suffisant pour atteindre de hautes températures.
Disadvantage Ventilation may be insufficient, but this can be corrected by drilling holes with a drill. These holes also allow temperature measurements to be taken and pressurised air to be introduced.
The dose of granular urea (46% urea nitrogen in BUNIFERT granules (6)) added to the compost corresponds to approximately the volume of a good coffee cup for an 800-litre bin (three times more for a supply of roasted horn). As soon as a drop in temperature is noticed, this nitrogen supply should be renewed until the temperature can be readjusted. You can also spread 150 g per m² of calcium cyanamide on successive 20 cm layers of plant waste. Calcium cyanamide more easily destroys weed seeds, fungal spores, pathogenic bacteria and harmful insects. However, it has the disadvantage of increasing the limestone content, which is incompatible with soils that are too rich in limestone.

Composting in 2 m³ piles surrounded by wire mesh supported by metal rods to facilitate aeration.
Composting carried out using dead leaves (oak, lime, plane tree), sawdust and powder from hardwood and softwood, hedge trimmings, crushed oak acorns, kitchen and crop residues. Addition of urea pellets and highly fermentable organic matter every four weeks to maintain the thermophilic phase in winter for three months.
Many domestic composters do not allow for proper aerobic composting due to an insufficient number of openings for aeration. If the raw material coming out of a compost bin smells like sewage, this indicates anaerobic fermentation. In an anaerobic environment, toxic substances are formed. It is therefore important to prevent composting from entering an anaerobic phase if you do not want it to become a source of pollution for cultivated land after spreading. Composters with multiple rows of openings on all four sides are more likely to undergo aerobic fermentation.
To start fermentation, there is no need to use compost activators. A bucket of organic matter taken from older compost is just as effective, and this process is less expensive.
In winter, due to heat loss, it is advisable to gather at least one cubic metre of fresh organic matter. The organic matter is enclosed in a wire mesh frame, which allows for good ventilation. With this type of composting, temperatures above 65°C can be reached in winter if the pile contains enough highly putrescible organic matter. The compost should be turned every two weeks. A similar result can be achieved with 900-litre Thermo-King compost bins.
Tip :
Is this the most favourable season to start hot composting?
It is advisable to carry out hot composting in April-May so that the cooling phase begins in early summer. This will give beneficial organisms time to colonise the compost throughout the summer, especially rose chafer beetle larvae, which play an important role in the decomposition of organic materials.

Brass’compost
In compost bins, without the gardener turning the organic matter, it ends up piling up. Anaerobic composting then takes place, producing toxic residues. Weed seeds are not destroyed, even though many earthworms and other useful creatures thrive in better-aerated areas of the composter. Fortunately, there is a great tool that makes it easier to aerate a compost bin: the compost mixer.
Fortunately, there is a great tool that makes it easier to aerate a compost bin; the brass’compost. This is a spring that is screwed into the mass of organic waste to remove a core of organic material. By performing this operation about ten times, the organic matter is well aerated again. During the thermophilic phase, this stirring should be repeated and watered when the temperature drops.
It is possible that during stirring with this tool, water vapour will be released from the compost with a puff of heat indicating that the temperature is very high and that stirring was not necessary.
Stirring should be avoided when the temperature has not dropped below 45/50°. Brass’compost is now available on several websites..
The compost turner is 65 cm long. This tool cannot therefore reach the bottom of the composter if the height of the latter exceeds the length of the compost turner. However, during the thermophilic phase, the level of organic matter drops very quickly. This drop can reach 10 cm on the first day, which means that after a few days, the deeper layers can be aerated with the compost turner.
Trip :
Using the brass’compost.
The brass’compost spring ends with a rubber guard to prevent injury. This guard must be removed before starting to turn the compost. The stainless steel spring section is more than strong enough to withstand repeated use without becoming permanently deformed.
To improve the insertion of the spring, it is useful to sharpen its tip at an angle, with the cutting blade facing downwards.
Do not force the device all the way to the handle if the resistance of the materials is too strong. Mixing must be carried out in several stages, layer by layer, by screwing the tool clockwise. Then remove the core. It is impossible to injure yourself, as the tool is equipped with a sturdy plastic handle.
You need to apply a little force to remove the core, but if it is too difficult, unscrew the tool until you can remove the core without too much effort, then repeat the operation.
Resistance is often caused by undecomposed twigs. When the core is tipped to one side, a hole remains, allowing the compost to be mixed more deeply. Mixing is carried out as many times as necessary to ensure that all organic matter is mixed to a depth of at least 70 cm, including on the sides of the composter. Undecomposed organic debris brought to the surface by the carrots must be returned to the centre of the compost. To do this, select this plant debris by placing it to one side or temporarily depositing it in a small bin, then remove several carrots from the centre of the compost to dig a hole
For people prone to lower back pain, leaning slightly forward over the composter and pulling the compost upwards, even when standing on a stool, puts pressure on the spine in the opposite direction, increasing the risk of compression of the sciatic nerve roots. To avoid sciatica, it is essential to wear a protective belt and avoid pulling too hard.
in a compost bin, adding urea pellets (unless there is sufficient highly fermentable organic matter) with 10 to 20 litres of water immediately triggers the thermophilic phase. The temperature is checked with a laboratory thermometer through the bin’s ventilation holes. If the temperature does not exceed 50°C, highly fermentable organic matter and/or urea pellets (or ammonium nitrate for farmers who have the option of using this nitrogen fertiliser) must be added.
Some authors recommend covering compost piles with a waterproof sheet to prevent moisture loss, protect them from heavy rainfall, and prevent the introduction of weed seeds and unwanted insects. However, compost in the active phase always needs to be well aerated and consumes a lot of oxygen, especially during the thermophilic phase. Any obstacles that prevent air circulation must therefore be avoided; otherwise, ventilation openings must be provided. To cope with possible heavy rainfall, a folded tarpaulin is placed near the compost heap.
An interesting solution is to have two compost bins, one reserved for dry storage of organic matter (or compost in the maturation phase), and the other for starting composting with a thermophilic phase when the appropriate volume is reached. The bottom of the bin should not be waterproof so that beneficial organisms can find refuge during the thermophilic phase. To speed up the movement of earthworms, turn the soil with a spade directly above the bin on at least two sides, with the other two sides reserved for gardeners to carry out aeration operations above the bin, requiring the use of a stool, for example, to position themselves at the right height.
The different stages of composting with a thermophilic phase are described by clicking ici.
1) Godden 1995 – signalé dans Infos CTIFL N°225 octobre 2011
2) condat – produit – huiles de lames de scie ♦
3) COMIFER – Calcul de la fertilisation azotée ; guide méthodologique pour l’établissement des prescriptions locales -Edition 2013.
4) quadria composteur picumnus ♦
5) RAGDALE et al. (1992)
6) Azote uréique BONIFERT : vendu dans les COOPS agricoles par sac de 50 kg. Tenir compte de son dosage très élevé : en azote 46 % pour une fertilisation directe du sol censée corriger une carence en azote.
