De Montfort Medical Waste Incinerator

Target SDGs

Market Suggested Retail Price

$1,500.00

Target Users (Target Impact Group)

Small and Medium-sized Enterprises, Public Sector Agencies

Distributors / Implementing Organizations

WHO, MSF, the British Council, UNICEF, the Salvation Army and Technology Without Borders

Competitive Landscape

Direct competitors include T4T Mak IV Incinerator.

Manufacturing/Building Method

Manufactured locally, with schematics and instructions available online

Intellectural Property Type

Open-source

User Provision Model

The designer, Professor D.J. Picken, provides schematics online so the incinerators can be manufactured locally using the provided schematics. NGOs have used these designs.

Distributions to Date Status

Over 1,000 distributions worldwide.

Design Specifications

The De Montfort Mark 8a has a capacity of 12 kg/h and takes 3-4 days to build. There is a concrete foundation of L x W x H = 2 m x 2 m x 0.15 m and refractory bricks of L x W x H = approx. 230 x 110 x 65 mm (the mortar is refractory cement (high alumina)). The body will have 13 layers. Other components include the top frame, loading door, ash door, chimney, shelter, and outer wall. The De Montfort Mark 9 has a capacity of 50 kg/h and takes 5-6 days to build. For the foundation, a concrete platform of at least 3 m x 2 m x 150 mm thick should be prepared on the chosen site, ideally with a roof about 3 m high to protect the incinerator and the operator from weather. The body will have 14 layers. Other components include the top frame, loading door, ash door, chimney, shelter, and outer wall. List of materials and their dimensions for the Mark 8a and Mark 9 can be found on the instructions for the model.    

Product Schematics

Technical Support

Technical support is provided in an operation manual and maintenance instructions, otherwise users are expected to maintain the incinerator on their own.

Replacement Components

The chimney, chimney support plate, sand seals, ash door, and bricks all need to be maintained and replaced as needed.

Lifecycle

3-5 years

Manufacturer Specified Performance Parameters

The incinerator was designed to meet the criteria of a temperature of above 800^oC with a residence time of over 1 second.

Vetted Performance Status

The original (Mark 1) incinerator had been tested by CSIR, in South Africa, in December 1999. Representative samples of waste from a typical primary health care centre were prepared by the South African Department of Health at the CSIR testing facilities. The principal findings were: “The medical waste tested in the trial was rendered non-infectious, the syringes were destroyed and the needles were rendered unsuitable for use. The emission of particulates, metals and chlorides comply with South African regulations for primary health care clinical waste used in the South African trials on small scale incinerators and the fuel to waste feed conditions for the tests. The combustion efficiency does not comply and the organic emissions are higher by a factor of at least 20 times.” The author noted that the test had been carried out at temperatures below 600°C, and that an undue quantity of wood was burned during the tests, which contributed to the high organic emissions. The next test was of a Mark 2 incinerator at the De Montfort University and was reported by DJ Picken in January 2001. The principal findings were: 1. “The combustion chamber temperature was above 800°C for most of the test; 2. For most of the running time there was no visible smoke emission. Only rarely did the smoke level exceed that which is considered acceptable in a diesel engined road vehicle; 3. Such smoke as was collected proved to contain only carbon. No metallic elements were present; 4. The flue gas was found to contain virtually no dioxins or furans. 5. Oxygen level in the flue gas varied between 4% and 16% 6. Carbon monoxide level was mostly in the region of 100 ppm, with levels above 400 ppm occurring only rarely.” A third test was carried out on the Mark 3 incinerator in the presence of observers from Médecins Sans Frontières in December 2000. Again the results were reported by DJ Picken. This test was carried out to test the efficacy of the incinerator to burn wet textiles as well as general clinical and household waste. The principal results were: “In all cases, at least one of the temperature zones through which the flue gas had to pass exceeded 800°C. CO could not be measured precisely at this low value. O2 levels fluctuated depending on how recently the load door had been opened, and the type of load. Rate of burning was very high, in the region of 50kg/h, again depending on load material. This meant that loading had to be very frequent, in the region of every 5 minutes.” For the fourth test, a Mark 8a incinerator was constructed at a site in Leicestershire and 8000 hypodermic syringes were sent to the site by WHO. Casella CRE Emissions of Cheltenham were engaged to sample and analyze the exhaust gases, and the incinerator was operated by the designer and a technician. Two 2-hour tests were carried out, one at maximum loading rate, and one at a loading rate designed to limit smoke production. Loading rates, temperatures and smoke levels were recorded as well as the gas samples. In both cases none of the 12 dioxin-like PCBs targeted were detected in the samples collected, although detection limits were substantially higher than usual. In both tests, the temperature of the gas path reached 800°C for nearly the whole test. Smoke levels were unacceptably high for test one where loading rate was at a maximum, but lower for test 2. A WHO assessment of De Montfort Incinerators in Tanzania found, "Out of 26 incinerators found during the assessment only 2 (7.6%) were not De Montfort models. Keeping De Montfort incinerators functioning appeared to be the main challenge. The study found that out of the 24 incinerators assessed, 7 (29%) were had not been operating for a period varying of 2 months to 3 years, mainly due to structural defects, which seemed caused by the non-adherence of contractors to use recommended construction materials, and particular specifications and designs for De Montfort incinerator to operate properly and at the right temperature. The study revealed that all of the 7 non-functioning incinerators had been constructed of burnt bricks obtained locally rather than the recommended firebricks." Toxins released can be viewed in the report.

Safety

• Incinerators emit significant levels of dioxins and furans, with 40 grams of Toxic Equivalent (g-TEQ) in air emissions and ash residues per kilotonne of waste burned, even when properly operated.
• The designer acknowledges that the incinerator will not render all flue gases smoke-free and will not meet clean air requirements in all situations or with all loads.
• When burning waste, particularly infectious waste, the operator must be in constant attendance.
• The incinerator is not suitable for short, sharp burns without a warm-up period.
• It is not suitable for operation in a closed room.
• Smoke will be emitted whenever the loading door is opened.
• A roof may be fitted to protect the operator from rain, but only minimum walls should be used.

Complementary Technical Systems

None

Academic Research and References

Compliance with regulations

Depends on location.

Evaluation methods

The manufacturer evaluated the incinerator and states when properly operated it will achieve 800°C for at least one second and provides these disclaimers.

Other Information

The instructions for this model (The De Montfort Mark 8a)  can be found here. The instructions for this model (The De Montfort Mark 9) can be found here. Technical support is provided in an operation manual and maintenance instructions. Other chemical detection can be viewed in the report. Operation and maintenance instructions are found here. Links to laboratory testing for air pollutant emissions is found here. Emissions Tests on De Montfort Medical Waste Incinerators can be found here.