The design and construction of this vermicomposting toilet system is very simple. It needs no external energy input or machinery to process the sewage. There are two main components: an insulated tank which houses the worms with their associated ecosystem, and a ‘greenfilter’ or soakaway area to allow the vermifiltered water to be cleaned further and returned to the environment. This simplicity allows for a lot of flexibility in how the system is implemented to adapt to individual sites.
Siting the vermicomposting toilet system
The vermicomposting toilet system revolves around biologically active aerobic processing of sewage, so the ‘greenfilter’ or soakaway section of the system needs to be kept within the topmost 0.5m of soil where worms and aerobic soil biota thrive. This is the main determining factor in how the system should be designed and situated. The worm tank, being a self-contained unit, has more flexibility.
At its simplest, the system is gravity-fed, so is best suited to sloping sites or sites where the waste pipe outlet from the flush toilet is at least half the height of the tank (0.5m) above ground level.
Siting the tank in a basement is possible, drainage possibilities permitting, as there’s no odour from the system when it’s working properly.
On flatter sites, the tank can be sunk up to half a metre into the ground without compromising the proper functioning of the system, but any more and the drainage from the tank starts to get too deep into the soil. Don’t forget to allow for the minimum drain slope (see below) in the piping between tank and ‘greenfilter’ beds/trenches/mulch pits when working out how far down you can sink the tank.
Can I bury the worm tank?
Burying the tank is conceivable, but in most contexts not advisable for the following reasons …
- IBC tanks weren’t built to be buried so would need a strong containing structure.
- A buried tank can create problems with drainage unless the vermifiltered water can be piped away to surface layers downslope.
- Maintenance and access for refilling is more difficult.
- Adequate air circulation could be an issue without supplemental ventilation.
- There may be problems if the water table rises to within reach of the tank during wet periods, as the tank is lighter than water and will float.
Installing an underground collecting vessel and pump for the vermifiltered water is possible, but risky as pumps often break down. High tech proprietary units with integrated drain water collection which were designed and engineered for burial and installed in Australia and New Zealand have experienced problems.
Consequently, we don’t recommend burying tanks.
If there’s insufficient drop for a gravity-fed system, it would be easier to install a collecting vessel for the sewage and pump it up into the worm tank than it would be to bury the tank. This would involve macerating the solids to make it possible to pump them (less than ideal as the vermicomposting ecosystem then has to separate them out again), but this is probably preferable to attempting burial of the tank.
The vermicomposting toilet worm tank
The worm tank is made from a 1m3 Intermediate Bulk Container (IBC) tote or pallet tank. These tanks make ideal containers with their central access hole at the top and a drain outlet at the base. IBC tanks can be easily sourced second hand in most countries, but since they’re used for bulk transport of all manner of liquids, be sure to acquire one that’s food grade and has only been used to transport non-toxic liquids. Sometimes you’ll find a cup and fork food grade symbol embossed in the plastic of the tank.
The only modification to the tank required is to cut an access hatch in the top of the tank for inspection and to allow periodic additions of the organic material the system needs to function. For ease of access and loading it’s best not to make it too small. Bear in mind that the pipework from your toilet will need to be fixed into the central access hole at the top, so don’t cut the top of the tank right off.
Air needs to circulate within and around the tank to keep the system aerobic. There’s no need for additional ventilation, but don’t make the tank or the tank container airtight. There are no odours to worry about with this system if it’s running as it should be.
Earthworms survive within a temperature range of 5-29°C. Their optimum temperature range is 20–25°C. Cold is not as big an issue for them as heat – while their activity slows down a lot in winter, excessive heat can kill them instantly. To keep them as close as possible to their preferred temperature range, the IBC tank will need to be encased in an insulated housing in most climates.
You can make the housing out of a wide range of materials – brick or blockwork, stonework, wood, etc. It will need a hinged roof for access, also insulated.
Insulation can similarly be provided by a wide range of materials. You could even build the tank enclosure from straw bales and then lime plaster them. The possibilities are almost endless, but the enclosure must be capable of maintaining your worms between 5-29°C in your climate throughout the year. Worms also prefer the dark, so make sure the container is reasonably lightproof.
Run the pipework to the tank in the standard size for toilet waste pipe in your country. Make sure you adhere to minimum drain slope guidelines for the diameter of pipe you’re using over horizontal runs to prevent clogging or solids getting left behind. The final drop into the tank can exceed these slopes.
Plumb the pipework in through the central access hole in the IBC tank. This is important. It ensures even distribution of wastes and helps the worms stay better insulated from external temperature fluctuations if they’re encouraged to congregate in the centre of the tank.
A piece of nylon mesh will be needed to cover the drain hole at the bottom of the tank. This prevents gravel (if used) or organic materials from blocking the outflow pipework. A layer of gravel can be placed at the bottom of the tank if desired, but is not essential.
Starting the ecosystem
Fill the tank half to 2/3rds full with organic material. Use a mix of woody materials that decomposes slowly. Coarse wood shavings, dead leaves, dead bracken, etc, both fresh and partly decomposed, make an ideal mix. (See the section on tank maintenance on the Function and maintenance page for more details.)
Partially finished compost is a good addition, especially initially, as it will contain many of the bacteria your ecosystem will need.
Keep green material to a minimum. You don’t want to encourage too much thermophilic decomposition because the environment will become too hot for the worms.
Fine material like sawdust should not be used. It’s too fine, and will clog the system.
If the organic material is very dry, it will benefit from an initial wetting to provide the optimal moisture level for the worms.
Once the organic material has been added, cover the surface with a layer of partially finished compost and some kitchen scraps. The tank is now ready for worms.
Adding the worms
Worms can be sourced from any animal manure pile where they naturally congregate. (They may not be present in winter though or during droughts or periods of heavy rainfall.) They can be acquired mail order in many countries. The preferred species is Eisenia foetida, also known as redworm, brandling worm, panfish worm, trout worm, tiger worm, red wiggler worm, red Californian earth worm, etc.
The initial number of earthworms you’ll need depends on how many people will be using the system. A 2011 study conducted in India by Yadav et al (*) found that the optimal stocking density of worms for the fastest reproduction and growth rate was 0.5kg worms/m2. Since the tank is 1m2 in area, you can therefore start the vermicomposting toilet system with as little as 0.5kg worms.
Yadav also found that for optimal food intake by worms, a feedstock rate between 0.40-0.45kg feed per 1kg worms per day was best. On average, humans eliminate 128g of fresh faeces per person per day, so you can calculate the initial number of worms you’ll need by allowing 0.5kg for every 2 people using the system. These numbers should keep odours to a minimum while the ecosystem establishes and the worm population grows and adjusts to the feed rate.
What’s the maximum number of people a single system can handle?
Given optimum conditions, adult earthworms can double their number within as little as one month and certainly within 2 months, so the population quickly adjusts to ideal levels and becomes self-regulating thereafter. Once established, the system can cope with larger numbers of users over the short term with ease and doesn’t need any intervention to do so.
With a density of 3kg worms/m2 – the maximum density Yadav et al found consistent with a healthy ecosystem – the system would theoretically be capable of handling the regular input of 12 people. However, the maximum usage number of a single IBC-based vermicomposting system has yet to be determined in practice – to our knowledge, nobody has tested this yet. For this reason, we wouldn’t recommend a single tank system for households with a constant population of more than 8 people, unless several of them are out at work (and hence using other facilities) for most of the day.
The ‘greenfilter’ or soakaway
The vermifiltered water leaving the worm tank can be cleaned further in any of, or a series of, greenfilter beds, on-contour percolation trenches (swales) or mulch pits, sized according to the volume of water passing through the tank.
If grey water is being processed through the tank as well as black water, the ‘greenfilter’ needs to be several times larger than it would be for black water alone.
Sizing the ‘greenfilter’
Greenfilter beds, percolation trenches and mulch pits fed by a vermicomposting toilet are filled with the same organic material as is used in the worm tank. This encourages the development of the same ecosystem within a loose-textured, well-aerated matrix, so similar rapid percolation rates can be expected within the organic layer of the greenfilter as are seen in the worm tank.
Worm eggs will pass out of the tank in the vermifiltered water to colonise the greenfilter areas. While permitting rapid percolation, the organic material will also act as a sponge to hold water for uptake by plants and will serve to improve the texture, fertility and water retention capacity of the surrounding soil as well as forming the principal substrate for a massive increase in the soil biota present. This results in cleaner water with fertility, moisture and fungal communication pathways for the vegetation. It will also lead to improved percolation rates through the surrounding soil as it too is colonised by worms, improving texture and aeration. Earthworms are able to increase the hydraulic conductivity and natural aeration of soil not just through the physical action of burrowing, but by granulating the clay particles which pass through their bodies.
This is a whole different equation to working with an essentially inorganic filtration concept. As with the worm tank, it’s a self-regulating living system.
The minimum recommended soil depth for a conventional septic system to operate effectively is 1 to 1.5m. This is not the case with a vermicomposting system. The ‘greenfilter’ areas need a minimum depth of only 0.5m.
Hydraulic loading rates for domestic septic tank effluent from conventional septic systems are generally based on infiltration rates though clogged soil surfaces. Often soil textural properties are assessed with reference only to the mineralogical properties of the soil itself, not the amount of organic material and soil biota present. Yet it’s the latter which primarily determine how well the waste water is cleaned and purified.
Since water passing through the worm tank has already had upwards of 90% of pollutants removed, the area of greenfilter required can be calculated by reference to soil percolation tests for grey water discharge. Since these are also calculated without taking into account the level of organic material and soil biota present, it’s likely to provide a comfortable margin of error.
Run pipework from the worm tank to a distribution box in the greenfilter area(s) in the same diameter or greater than the tank drain tap. From the distribution box, run smaller diameter perforated pipe through the uppermost 20cm of the organic material. Wrap the perforated pipes in geotextile filter fabric or horticultural fleece to prevent blocking by the organic material.
For on-contour percolation trenches or swales, the perforated pipework should also be laid on contour.
Mulch pits don’t require perforated pipework. Small diameter waste pipes fed from the distribution box are sufficient.
Greenfilter areas serve best to irrigate trees and shrubs, and can include edible species.
Grey Water Central, Oasis Design.
Create an Oasis with Grey Water, Art Ludwig.
Soil Percolation Test
Excavate a percolation hole 300 mm square to a depth 300 mm below the proposed invert level of the effluent distribution pipe. Where deep drains are necessary, the hole should conform to this shape at the bottom but may be enlarged above the 300 mm level to enable safe excavation to be carried out. Fill the 300 mm square section of the hole to a depth of at least 300 mm with water and allow it to seep away overnight. It is important to saturate the soil surrounding the test hole to simulate day to day conditions in an operational drainage field. Next day, refill the test section with water to a depth of at least 300 mm and observe the time (t) in seconds, for the water to seep away from 75% to 25% full level.
Divide this time by 150 mm. The answer gives the average time in seconds (Vp) required for the water to drop 1 mm. Take care when making the test to avoid unusual weather conditions such as heavy rain, severe frost or drought. Carry out the test at least 3 times and take the average figure. At least 2 percolation holes, not less than 5 m apart, should be dug and tested 3 times each to obtain consistent results. The floor area of a sub-surface drainage trench required to disperse effluent from septic tanks may be calculated from –
A = p x Vp x 0.25
where A is the area of the sub-surface drainage trench, in m2 ; p is the number of persons served by the tank; and Vp is the percolation value obtained, as described above, in seconds/mm.
For wastewater that has received secondary treatment followed by settlement or for greywater, this area may be reduced by 20%, i.e.
A = p x Vp x 0.2
Source: Scottish Building Regulations
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