How Peter makes his compost and goes on to make his potting mixes and other things
|The great man himself|
I am privileged that Peter Williams, microbiologist, horticulturist and gardener and my dearest friend has written this article especially for us. In it he gently chides my own methods
If you are a regular reader of The No Dig Gardener you will have realised the enormous depth and breadth of Roger’s gardening expertise. You might be also impressed by the trouble he takes to research both traditional and novel gardening activities and by his ability to formulate and present insightful comments. You might however, have noticed one rather glaring omission. There has never been a post on composting. The reason is simple. Roger does not compost. You may well ask, but I couldn’t possibly comment upon what Roger actually does with all the grass he cuts, the prunings he removes, and the vast amount of dead plant material generated annually by his herbaceous borders and strange vegetable garden. All I know is that it never appears on a compost heap – Composting at Roger’s is even rarer that digging!
1) Background issues
Despite the mystery that surrounds composting and the production of the perfect ‘crumbly compost’, the basic principle is really quite simple – make your surplus vegetation into a pile and let it rot.
Composting is the decomposition of organic matter by soil organisms and is an essential component of the recycling of nutrients in ecosystems. Organic matter is the general term for plant, animal and microbial debris. Soil organisms attack organic matter to obtain the energy they need to live and the raw materials they need grow and reproduce. In other words, organic matter is the ‘food’ of the soil organisms.
Soil organisms belong to very diverse groups - the microflora includes, bacteria, fungi and protozoa and the microfauna includes numerous arthropods, nematodes and diverse other groups of invertebrates. In some composting systems, earthworms and other relatively large members of the macro-fauna play an important role in pre-digesting and mixing the organic material with the soil particles.
Collectively soil organisms can eventually break down virtually all types of organic matter but the rate of decomposition, and the nature of the end product, depends upon a number of factors. In this article I hope to discuss some of these factors and to simplify issues that television gardeners do their best to complicate or confuse. At the outset however, you can be reassured that whatever composting techniques you adopt, or even if you do nothing with your dead plant material, you will ultimately produce some sort of ‘compost’ that will be of use in the garden.
If you look at your garden in late winter or spring you will see partially decomposed plant material lying on the surface of the soil. The magnolia leaf below shows decomposition in practice. The easily decomposable ‘soft’ tissues of the leaf lamina have largely disappeared whilst the much more resistant water and sugar conducting elements remain.
Victorian artists used various techniques to produce leaf skeletons for use as decoration. They usually heated leaves with a variety of caustic agents before bleaching the resistant skeletons and arranging artistically.
|Skeletal leaves used to form an art work|
The surface of an undisturbed woodland soil has a deep layer of organic matter. Freshly deposited and partially decomposed leaves lie on the surface. Beneath, is the crumbly leaf mould that has the wonderful ‘earthy’ smell and is in effect, a complex mixture of plant and microbial residues and intermediate products of decomposition.
|Woodland surface with freshly deposited leaves scraped away in foreground to reveal leaf mould|
|Section through the top layers of a woodland soil. The organic layer here is 15cm deep|
In garden or field soils, the O horizon is absent because it has been thoroughly mixed into the A horizon by cultivation (However, this may not be the case on the No Dig Gardener’s plot!). Lower layers (B horizon) are effectively the sub-soil where root growth is relatively poor.
Organic matter enters the soil throughout the year but there is a great increase in deposition in autumn when deciduous plants shed their leaves and annual plants die. The processes that operate in the surface layers of soils are fairly slow and predominantly aerobic in nature. The ideal compost heap should work in essentially the same manner as the organic layer in a woodland soil, but because considerably greater amounts of organic matter are added over a short time period, and in a confined space, there are important differences.
Hot and cold composting
At this point the distinction must be made between ‘hot’ and ‘cold’ composting. Hot composting is the only kind that I use. It involves constructing a heap on a single occasion from previously stored organic materials (grass clippings, leaves and other plant remains) and aims to induce a rapid aerobic decomposition of organic matter that liberates heat that kills weed seeds, pests and pathogens. The process is completed in a matter of weeks or months. Cold composting involves serial additions of organic material over a period of weeks, months or years. This is essentially a slower, largely anaerobic process in which no noticeable heat is generated and the production of a crumbly final product may take years, or may not occur at all.
Another really important consideration is the rational for composting. Whilst I use hot composting to dispose of waste materials, my principal aim is the production of a very desirable end-product that I use for mulching and in potting substrates. Cold composting is essentially a waste disposal system and the ubiquitous plastic compost bin typically used by many households is used to this end. In this type of cold composting, all manner of organic material, including kitchen waste, is essentially ‘binned’ in the hope that something ‘good’ may be formed in the bottom of the container. In my experience this is more likely to result in the owner finding a family of well-nourished rats than a supply of valuable compost.
We are fortunate to have a local council that operate a recycling scheme. All plant and food remains are collected every two weeks and processed in an efficient, industrial, anaerobic composting facility. The end product is sterile, finely sieved, useful organic material that is offered to gardeners and growers either free or at very small cost. All my food waste and weeds are disposed of in this way and none enters my compost heap.
2) A few more details
a) Although the details in the table above are generally true, the real situation is far more complex because of the many micro-environments that occur in a compost heap. Most of the microbes that decompose aerobically, can also do so anaerobically if the oxygen levels become lowered so there will be some anerobic processes in a hot heap and some aerobic ones in a cold heap.
Factors that favour rapid decomposition include a lightly constructed heap that is porous to air and water and contains material with an appropriate carbon to nitrogen ratio.
b) Carbon:Nitrogen (C:N) ratio
The ideal carbon:nitrogen ratio for compost is about 28C:1N. At this ratio, about three quarters of the carbon is used as an energy source and mineralised, and the remaining carbon and nitrogen is converted to make new soil organisms. This is exactly how humans and other animals use food both for energy and for raw materials for growth. Walter de la Mere clearly understood this and wrote in the first part of his humorous poem Miss T.
“It's a very odd thing - As odd can be - That whatever Miss T eats Turns into Miss T "
The same goes for soil organisms – much of what you put onto your heap essentially turns into soil organisms, at least in the first instance.
Whilst it may be satisfying to know about C:N ratios all you really need to know is that living ‘green’ materials tend to have narrow C:N ratios and dead dry matter like grass, woody materials and old leaves have wide ratios. Most ‘equalish’ mixtures of green and brown material will decompose rapidly.
(More about C:N ratios for really serious composters)
If the C:N ratio of the materials in the heap is wide i.e. significantly greater than 35:1, there are probably plenty of carbon-rich materials that could provide energy for the soil organisms but a relative shortage of nitrogen-rich materials that are needed for protein manufacture and population growth of soil organisms.
Decomposition of high C:N ratios is at first slow but will occur, and as it does, the C:N ratio will narrow and the process will then accelerate so long as other factors are not limiting. Proprietary compost accelerators are usually nitrogen rich materials that function by narrowing the C:N ratios
The practice often advocated by television gardeners of adding lots of cardboard to compost heaps “to feed the microbes” is one that I would never contemplate. This material has a very wide C:N ratio (perhaps 200 to 500:1) and in almost all cases reduces the rate of decomposition unless additional narrow C:N compost accelerators are also added.
If the C:N ratio of your compost heap is narrow, i.e. less than approximately 20:1, there will still be plenty of carbon rich compounds to provide energy but a relative over provision of nitrogenous compounds. Decomposition proceeds rapidly and the surplus nitrogenous compounds may be released to the atmosphere as ammonia. This explains why there is often a smell of ammonia around used bedding straw removed from animal pens – Animal wastes have a narrow C;N ratio (10-15:1) because animal urine is very rich in nitrogenous compounds and this is why old and not so old, gardeners frequently urinate on their compost heaps!
c) Water availability
The factor most often overlooked by television gardeners and magazine articles is the need for the compost material to be wet. Dry heaps will not decompose rapidly however favourable the C:N ratio and other factors.
I make use of this fact throughout the grass cutting season. All my mowings are simply dumped in a containing area and left until autumn/winter when I construct my heap. The heap is not covered to exclude rain but even so, the contents remains too dry for rapid or prolonged decomposition to occur. A pile of grass clippings collected over a period of weeks or months might well appear damp at the surface, but if the outer layer is removed, the older material will appear dry and grey coloured.
|Very dry, partially decomposed grass revealed when surface layer removed|
d) The size of the compost heap
In composting size really does matter – small heaps are less likely to heat up and retain their heat for long enough for effective decomposition to take place. In addition, the lack of heat means that potential pests, pathogens and weed seeds will remain. The reason is the relationship between surface area and volume. Small heaps – the size offered by commercial plastic compost bins – have a large surface area to volume ratio. This means that they are prone to loosing heat quickly and do not get hot unless they are well insulated. Failure to generate and store heat, prevents those microbes that require high temperatures from growing.
Larger heaps are far better at reducing heat loss and the ideal size is probably of the order if 1-5 cubic metres. Even larger heaps may suffer from the problem of becoming anaerobic because diffusion of oxygen is impaired and cannot enter fast enough when decomposition is at the highest rate.
e) The need to shred compost
The surface area of the material on the heap will affect how rapidly it decomposes and the smaller, the better. This is the surface area effect mentioned above. Again here, the smaller the pieces, the bigger the surface area but this time a large surface to volume ratio is favourable because it enhances the rate of decomposition. Since the majority of my material is grass clippings leaves and small branchlets blown out of deciduous and coniferous trees and collected via a rotary mower – no further treatment is needed. If you have generally leafy or woody material it would help to crudely chop, mow or shred before composting.
f) Other factors
I have never bothered to check the pH of my compost although all my plant material comes from vegetation growing on a very acid soil with pH 5.5.
In terms of aeration, I load my heaps simply by forking the stored grass etc into the composting bay and only gently firming down – usually with the fork, or at the end by walking on the surface.
3) Practical matters
a) Bin structure
My composting area is now made up of three contiguous bays each 1.2m tall. 1.7m wide and 2m deep giving a volume of 4 cubic metres each. The bins are constructed from preserved fencing materials and rabbit netting available cheaply from farm stores. The ones shown are ten years old and were built in a day
|Initial composting area|
b) Filling the bin
I usually start sometime after the middle of November when a substantial volume of leaf material is available. The first layer is usually composed of fresh grass and fallen leaves. Collecting the leaves together with fresh grass using a rotary mower is helpful because it thoroughly mixes the two components.
If I start later as I did this year when grass mowing has finished for winter, I toss in about 15 cm of ‘old grass clippings’ and then about the same volume of leaves and gently mix the two together with a fork.
Every 30 centimetres I water the mixture thoroughly. In practice I just leave the hose pipe running continuously when I am adding the components and keep moving the hose pipe about in the bay. I repeat the process until the bin is full – usually a couple of hours or so. I give the completed heap a final watering and then cover with a layer of dry leaves for insulation and then just leave it.
|Completely filled bin with cap of dry leaves - 6th January 2019|
c) Temperature and volume changes
The results for this year’s composting that started in January 2019, with plant material stored during 2018 is shown below.
|Graph updated to March|
The heap was completed on the 5th of January 2019 and the temperatures shown for the few days before this were from the stored grass cuttings.
The plotted results are similar to ones that I normally observe. The temperature rises after just a day and then accelerates to reach a maximum in the high 60’s C. The highest temperature that I have ever recorded was 72C. A temperature of 50C or higher, is usually suggested to be necessary to kill pathogens, pests and weed seeds and as the graph shows was maintained for 16 days.
The average outside air temperature during this period (January 2019) was approximately 3C with frequent night frosts. In late January, night temperatures were of the order -5 to -8C and day temperatures rarely rose above freezing point.
Microbial populations will change dynamically as the compost ages. Even after the temperature falls back to near ambient, the microbial processes will continue slowly. At the time when the heap is at its highest temperature the predominant organisms are likely be the fascinating aerobic thermophilic bacteria that have an optimum temperature around 50-60 C. When you consider that it is very unpleasant/harmful to immerse your hand in water at 50 C for more than a few seconds you can realise just how hot this is.
As decomposition occurs and the temperature rises, the volume of the heap decreases. After three weeks the volume had decreased by 25%. Past experience suggests that the volume will further decrease slowly over the next two or three months before I use the material. At this time the volume is usually approximately 50-60% of that at the start. In years when I start composting early, or where I have a large surplus of material, I top up the heap with fresh material after about three or four weeks.
I do not ‘turn’ my compost heap at any stage – I set it going and simple use the end product. Turning may be helpful to mix up, and re-aerate and possibly re-hydrate the decomposing mass, but it is very hard work and with my size of compost bins, not needed.
4) Uses of compost
a) Mulching borders
a) Mulching borders
I generally begin to use the compost in spring – four to five months after the process was started. The surface layer is removed and stored for future composting because it has undergone only minimal decomposition. The main body of compost is damp but virtually odourless and relatively easy to remove with a fork.
For mulching I simply transfer to a wheel barrow and chop coarsely with a spade before depositing in a 10cm layer over clean, bare soil.
|Ready for mulching|
|Azalea borders mulched|
|Tree roots that have colonised the pile of compost – exposed after the compost heap was removed|
The second principal use for my compost is in making potting media. For this activity I transfer the compost to my polytunnel and roughly rake into a bed approximately 20cm deep. After two or three weeks I make into a pile and sieve the material through a large coarse sieve made to fit over a wheelbarrow and then it is stored either in a pile, or in 120 litre containers.
In the dried, sieved material, remains of the grass and leaves can still be seen, but this is quite resistant to further rapid breakdown and maintains its structural integrity well. However, potting media made with a high proportion of compost does tend to shrink a little over a period of a year or so, much like most proprietary brands of multipurpose.
I normally mix my compost with stored garden soil and gravel or Perlite. The proportions vary depending on what I am growing but usually it is 50% soil, 25% compost and 25% grit or Perlite. For woodland species I often omit the perlite or grit and perhaps use 60%soil, 40% compost. Hardy cyclamen and hepaticas do really well in this latter mixture.
In addition to the bulk components, I also add 12-14 month slow-release fertiliser at rates varying from 1-3 grammes per litre of compost
When making potting compost for especially valuable plants the soil I use is derived from stored grass turves that have rotted down over a period of a three years. This was the original basis of John Innes compost but I doubt that much if any commercial compost uses stored turves today.
|Soil store - the original stacked turves can still be seen|
|Showing that the soil in the storage breaks up beautifully twhen disturbed with a small trowel|
|Compost sieving and storage pile|
For many years I was rather like Roger and was in denial about composting. I simply dumped lawn cuttings and other materials on an ‘out of sight’ area and allowed it to ‘disappear’ naturally or put it on a bonfire. When I did collect leaves, I returned them to the wooded area of our garden. My concern about composting was that the result of my unsatisfactory efforts with plastic compost bins. I never produced useful compost and usually ended up with wet, sticky, and rather unpleasant material. This was probably because I did not think about the process carefully enough.
When we started opening our garden for charity events, I did not want visitors to see the scruffy area where I dumped waste vegetable matter so built the system that I now use. At first, I was very reluctant to spread my compost as mulch because I feared that it still might contain weed seeds that had not been killed, My worry was that I would effectively spread new weeds all around my generally weed free beds. Having started to use it however, I am now a total convert and produce as much as I can each year. I cannot make enough to mulch all beds each year so I use a rotational system.
I felt similarly reluctant to make my own potting substrate because I did not have the facilities to sterilise the garden soil I was using. However, once again I am converted to this system. The results are excellent and, in many cases, far better than I obtained using compost bought from the local garden centre. A few weeds do pop up but they can be easily removed and I am not aware of increased problems from pests and diseases.
If you would like more information on how Peter makes up his potting mixes insert compost in the search box and scroll through the posts
If you want to read more posts written by Peter go to the link Peter Williams in the theme column
Picture for Mal
A new service - supporting picture for comment column
|Absence of allelopathic toxins|
|Saruma and seedlings|