Journal of Thermal Engineering, Vol. 5, No. 6, Special Issue 10, pp. 196-204, December, 2019 Yildiz Technical University Press, Istanbul, Turkey

# ENERGY POTENTIAL FROM MUNICIPAL SOLID WASTE (MSW) FOR A DEVELOPING METROPOLIS

A.T. Akinshilo
1,\* , J.O. Olofinkua1, O. Olamide2, E.A. Asuelinmen3

**ABSTRACT** In many developing cities around the world, the shortage of energy and environmental degradation are currently two vital issues affecting sustainable development. The migration of people from villages to one of Africa’s rapidly growing city Lagos, Nigeria has led to the generation of tons of municipal solid waste (MSW) daily. This is one of the important contributors to environmental degradation. Harnessing the useful potential of MSW for power generation adopting the incineration technology will enhance the intermittent power supply and also help with waste management, which has threatening effect on the populace. Therefore this paper focuses on energy stored in waste generated and the power potential of this MSW through an energy recovery method to generate other forms of energy for use has an alternative energy. From the waste characterization exercise, the main components of the Lagos MSW were found to be food, metal and plastic; making the average moisture content of the MSW high. It was illustrated from analysis that a high power potential of over 10,000 MW can be obtained adopting the incineration process, starting with data from 2016 with an exponential increase over the years.

## Keywords: Solid Municipal Waste, Site Selection, Waste Forecast, Energy Recovery Potential, Lagos

_Metropolis_

**INTRODUCTION** Waste arises from human activities such as domestic, commercial, industrial, agricultural and so on. These wastes if channeled to resourceful applications can make meaningful contribution to energy generation but when not properly utilized, it will have a negative impact on the living conditions. Municipal solid waste contains glass, paper, plastic, food waste amongst other putrescible. A wide range of substrates are available for conversion to bio-energy. The most commonly used methods include incineration, biomethanation/anaerobic digestion and gasification \[1- 4\]. The incineration technology involves burning of solid waste which is capable of reducing waste to 70% by mass and 90% by volume, producing steam for electricity and cogeneration. Biomethanation or anaerobic digestion process, an environmentally friendly energy conversion process utilizes micro-organism in decomposing biomass to produce biogas which may be used for combined heat and power generation while the gasification process involves the partial combustion of shredded wastes to generate biogas. However several solid waste mainly agricultural produce, wood and plastics are types of waste that can be gasified without pre-treatment, the producer gas obtained is used for energy production. In the effort to study power production Omari \[5\] carried out a thorough characterization of municipal solid waste of the city of Arusha, Tanzania where he showed the higher heating value, thermo-degradation analysis to determine the activation energy. The possibility of increasing the energy production was investigated by Alex \[6\] using waste through the solid waste to energy advanced thermal technology system and analytical cost models. Porteus \[7\] did a review of energy generation from waste incineration with emphasis on the effect of greenhouse gas emissions which is compared with emerging practices such Pyrolysis and gasification. \[8-9\] presented a review of energy recovery from burning solid municipal waste; where they reviewed the use of energy component obtained in form of steam, electricity or sale as solid fuel. Kalanatarifard \[10\] evaluated the composition and characteristics of solid waste for the purpose of obtaining information about the quantity of plastic that can be recovered at Bukit Bakin landfill, Malaysia. Gohlke \[11\] presented how greenhouse gas produced as a result of waste treatment can be _This paper was recommended for publication in revised form by Regional Editor Jaap Hoffman Hoffman_ _Mechanical Engineering Department, University of Lagos, Akoka-Yaba, Nigeria._ _Mechanical Engineering Department, Federal University of Agriculture Abeokuta, Nigeria._ _Architecture Department, University of Lagos, Akoka-Yaba, Nigeria_ \* _E-mail address: [ta.akinshilo@gmail.com](mailto:ta.akinshilo@gmail.com)_ _Orcid id: 0000-0002-6436-3420, 0000-0003-4873-7864, 0000-0001-6197-0359, 0000-0003-2193-0883_ _Manuscript Received 28 October 2017, Accepted 04 March 2018_

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Journal of Thermal Engineering, Technical Note, Vol. 5, No. 6, Special Issue 10, pp. 196-204, December,

described in simplified manner using energy indications. Themelis et al. \[12\] presented a study that showed technology implications of managing municipal solid waste in New York, they showed that Waste to Energy (WTE) processing of solid municipals reduces fuel consumption and is better compared to landfilling. Koten \[19\] evaluated the performance of diesel engine within multi-dimensional framework in the bid to determine it optimal power generation while Abay et al. \[20\] presented flow and combustion of diesel engines utilizing computational fluid dynamics techniques. Improvement of renewables power quality and control was investigated by Dehini and Berbaoul \[21\] adopting the multilayered feed forward scheme. With respect to past research, the present paper aim to investigate the energy potential from solid municipal waste which may be obtained from landfills in Lagos state, Nigeria due to its peculiarity, as the commercial center of Africa, its rapid urbanization, meteoric population rise and problem of proper waste disposal methods. Therefore the potential in municipal solid waste for energy generation could serve as a source of alternative energy to the intermittent power supply experience across the state.

## SITE SELECTION

The site selection for any waste to energy (WTE) technology which could be incinerator plants with energy recovery, biomethanation/ anaerobic digestion or gasification should be based on factors other than the mere availability of land due to the effect of carbon footprints on high population density. For most developing countries the practice as being mass burning of wastes i.e. to have an open piece of land for burning the large amount of waste produced daily. This practice has produced it numerous environmental effects such as environmental degradation and spread of contagious diseases. Environmental impact of waste to energy facilities are observed in the reduction of landfills as well as gas emissions. Thermal process involved in the combustion of MSW leads to incomplete thermal reactions leading to the release of heavy metals and harmful gases from MSW incinerators. Most notable are Dioxin/furans which are classes of chlorinated organics. These compound been found in incinerator stacks have been proven to be highly toxic on wildlife and human occupation. Although utilization of incinerator in a metropolis such as Lagos State requires the satisfaction of Federation environmental laws such as 247 criminal code Act CAP C38 LFN, 2004. Making it an offence to pollute air in a manner noxious to human health. However organic compounds emission can be destroyed during combustion process by adopting efficient incinerator design to achieve complete oxidation of hydrocarbon species and the use of air pollution control mechanism to bring to bearest minimal organic compound escaping the incinerator stack such that human life and environment are not threatened. The design of the WTE site significantly impacts the cost of the facility, the control and the efficiency of the truck traffic flow. Location of a site can significantly affect dispersion of the plume from the chimney in the case of the incinerator, which in turn affects ambient concentrations, disposition and exposures to workers and the community. The population needs to be studied to determine the density and projected estimate for a known period into the future taking into consideration its mode of population growth. This information needs to be available because of it necessity knowing that population determine to a large extent the amount of waste to be considered and therefore total incineration needs of the community, both present and future. The following are some other factors that need to be considered in site selection for a WTE technology: Present and anticipated use of the land in the neighborhood under consideration, Accessibility of the location, Present and projected needs of the community, Availability of nearby areas requiring landfill, Coordinated road network around the intended plant and plants should be at least 300 to 500 meters from residential zones. Based on the above considerations with respect to geomorphological terrains of Lagos state. Ibeju Lekki, Ikorodu and Ojo Local government areas are the most suitable location for waste to energy (WTE) site having a low population density \[15\], accessible road network and nearness to coastal regions.

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Figure 1. Map of Lagos state showing population density of local government

WASTE GENERATION FORECAST
Waste incinerators are used to destroy solids, sludge’s, liquids, and tars. Depending upon the physical,

Waste incinerators are used to destroy solids, sludge’s, liquids, and tars. Depending upon the physical,
chemical characteristics of the waste and the handling they require. It been estimated that the average waste
generated per person per day is about 0.65kg/person/day \[13\],with a growing population of about 18,000,000 as at
year 2015 with an increase rate in population of about 3.2 % \[15\]. Therefore the amount of solid municipal waste
generated daily with the population growth rate can be projected as follow in the Table 1, assuming the average
waste generated per person remains constant. It obvious there will be an increasing amount of solid waste available
throughout the state as shown on Table 1, which will create a chronic problem for residents if not properly and
efficiently managed. However these massive quantity of solid municipal waste though largely wet are good source
of Refuse derived fuels for electricity generation.
Table 1. Trend in waste generation

Table 1. Trend in waste generation

| Year | Population | Waste/day(kg) | Waste/year(Ton) |
| --- | --- | --- | --- |
| 2015 | 18000000 | 11700000 | 4270500 |
| 2016 | 18576000 | 12074400 | 4407156 |
| 2017 | 19170432 | 12460780 | 4548185 |
| 2018 | 19783886 | 12859526 | 4693727 |
| 2019 | 20416970 | 13271031 | 4843926 |
| 2020 | 21070313 | 13695704 | 4998932 |
| 2021 | 21744563 | 14133966 | 5158898 |
| 2022 | 22440389 | 14586253 | 5323982 |
| 2023 | 23440389 | 15053013 | 5494349 |
| 2024 | 23899553 | 15534709 | 5670169 |
| 2025 | 24664339 | 16031820 | 5851614 |
| 2026 | 25453598 | 16544839 | 6038866 |
| 2027 | 26268113 | 17074273 | 6232110 |
| 2028 | 27108692 | 17620650 | 6431537 |
| 2029 | 27976171 | 18184511 | 6637347 |
| 2030 | 28871408 | 18766415 | 6849742 |

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Journal of Thermal Engineering, Technical Note, Vol. 5, No. 6, Special Issue 10, pp. 196-204, December,
2019

With the rapid increase in waste generation across various parts of the state over the years, the tonnage of
combustible waste can be used to support the electric power production across the state. This will further boost
developmental projects, assist small and medium enterprises, and also complement the intermittent power supply
from the various electricity distribution companies.

ENERGY POTENTIAL FROM MUNICIPAL SOLID WASTE

Figure 2. Chart showing the waste structure of Lagos State \[13\]

The bulk of solid waste in Lagos state are food wastes as shown in Figure 2 which as high moisture
content. This is due to the lack of proper waste treatment and disposal method. However a high tonnage of waste is
available for energy generation which will be of immense benefits to both domestic and commercial/industrial
consumption.

Estimation of Carbon Component of Solid Waste

Table 3. Ultimate analysis of solid municipal waste \[16\]

a: putrescible,glass,fines, etc.

| Combustibles | C | H | O | N | S |
| --- | --- | --- | --- | --- | --- |
| Vegetables | 48 | 6.4 | 37.6 | 2.6 | 0.4 |
| Paper | 43.5 | 6.0 | 44 | 0.3 | 0.2 |
| Plastic | 60 | 7.2 | 22.8 |  |  |
| Textiles | 55 | 6.6 | 31.2 | 4.6 | 0.15 |
| Othersa | 49.0 | 6.0 | 42.7 | 0.2 | 0.10 |
| Total | 255.5 | 32.2 | 178.3 | 7.7 | 0.85 |

Here we proceed by determining the various proportions in solid municipal waste generated across the state
per year (tonnage) as shown in the Table 1 using the waste structure of Lagos state as illustrated in the Figure 2.
Thereafter the carbon component of the various waste structure is determined with respect to the ultimate analysis of
solid municipal waste in Table 3, where it can be easily shown from analysis that 1kg of municipal solid waste will

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Journal of Thermal Engineering, Technical Note, Vol. 5, No. 6, Special Issue 10, pp. 196-204, December,

generate 0.6683 kg of Carbon i.e. 1 tonnage of MSW will generate 668.3kg of carbon. This is illustrated in the

Figure 3 below.

**Figure 3. Analysis of Carbon component in Lagos State solid waste**

The Figure 3 which shows the yearly generation of carbon constituent in tons from solid waste illustrates that the yearly Carbon constituent increases steadily due to the increase in waste generation across the state. **Estimation of Methane (CH4) from Carbon Generation**

# C + 2H2O CH4 + 2O2 (1)

From the above chemical reaction, it can be demonstrated that 1 mole of carbon (C) reacting with 2 moles of water will yield 1 mole of Methane, releasing 2 moles of oxygen. With the aid of Table 2. It is illustrated that 1 kg of carbon (C) will produce 1.333Kg of Methane, which is applied to the yearly output of carbon produced. Therefore the yearly Methane obtained from MSW is demonstrated in the Figure 4 below:

**Figure 4. Estimation of Methane obtained from chemical reaction**

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Journal of Thermal Engineering, Technical Note, Vol. 5, No. 6, Special Issue 10, pp. 196-204, December,
2019

It can be depicted from the Figure 4 that Methane production from chemical reaction of Carbon with water
under thermodynamically stable condition yields an increasing production of Methane which increases steadily each
year as a result of increasing release of carbon constituent form solid waste.

Estimation of Energy Generation Potential

To determine energy generation potential from MSW, mass burn incineration is adopted where total waste
is considered. However due to the high moisture content in Lagos State waste created by lack of proper sorting
method and waste disposal. It is assumed 35% of total wastes/day as expressed in Table 1 is dry waste. Where the
energy content in various waste material are expressed in the Table 4 where the last two column depicts the total
energy content and lower heating value (LHV) of waste constituent.

Table 4. Energy content of different waste constituents \[14\]

| Material | Kwh/Kg in material | Kwh/Kg in waste |
| --- | --- | --- |
| Paper | 4.39 | 1.21 |
| Plastic | 9.05 | 0.46 |
| Glass | 0.00 | 0.00 |
| Textile | 5.20 | 0.22 |
| Organic matter | 1.55 | 0.10 |
| Others | 3.36 | 0.28 |

Total energy content of mass burn can be depicted from the energy content of waste constituent, Table 4 as
2.27(Kwh/Kg). Therefore for a ton of MSW considering the waste structure of Lagos state as expressed in Figure 2,
it can be easily interpreted that a ton of MSW contains 313.4Kwh/day energy content. Energy recovery potential
(ERP) is expressed in Gwh/day as adopted by \[14\]:

Emathit P!\\left(\\frac{G Wmathit}d\\mathit y\\right)!=!\\left(\\mathit D r y w a s t e!\\left(\\frac{K\\mathit g}{d y}\\right\ \ x\\!!\ \ \ H\\mathit V o f\\mathit{w a s t e}!\\left(\\frac{K\ W mathit h h}{K\ g}\\right)\\right)

(2)

Figure 5. Energy recovery potential forecast for Lagos metropolis

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Journal of Thermal Engineering, Technical Note, Vol. 5, No. 6, Special Issue 10, pp. 196-204, December,

As observed in the energy recovery potential (ERP) Figure 5, it is evident that despite low dry waste, the energy potential is sufficiently high for daily generation, which increases steadily for year output production. The net generation potential (NGP) for electrical power is defined as \[14\]:

# 10 NGP ==hhPGP xERPx (3) 24

Utilizing electrical power efficiency as low as 18%. Substituting values of appropriate parameters into the Eq. 3.The NGP forecast is expressed for yearly output as Figure 6.

**Figure 6. Net generation potential forecast for Lagos metropolis**

Figure 6 illustrates a promising power generation potential from MSW for the Lagos community, where it

is observed that a high power potential of over 10,000 MW of power from year 2016 can be obtained through MSW. Rather than the mass burning of waste in landfills creating atmospheric pollution and other forms of environmental degradation with no particular benefit obtained from the huge solid waste. More so it is observed that Figure 6 follows almost a linear trend; this is due to earlier assumptions of constant average waste generation with population growth rate as it affects MSW production.

## Economic Viability of the Waste to Energy Technology (WTE)

Since energy generation from municipal solid waste is highly intensive, especially processing cost of waste. There is need to analyze cost requirements and compare the cost involved with other relevant energy resource. Therefore comparison with fossil fuel oil based energy is considered. Since this is one of the major source of power generation in Nigeria.

**Table 5. Processing cost of waste treatment**

Waste treatment cost/tonnage Cost (NGN Naira) Separation of waste 100.00 Drying of waste 250.00 Storage of waste/day 150.00 Total Cost 500.00

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Table 6. Determination of substitution effect of waste to fuel oils

| 1 Tonnage of processed waste(A) | N500.00 |
| --- | --- |
| $^{a}$RDF available for purchase(B) | 4500.834tons |
| Cost of RDF(A x B) | N2,250,417 |
| $^{b}$Energy derivable in RDF(C) | 313.4Kwh/ton |
| Energy obtained from RDF(B x C) | 1,410,561.38Kwh |
| \[18\]Energy derivable from Diesel Oil | 100Kwh/ltr |
| Cost of Diesel Oil substitute(D) | N2,821,122 |
| Variation of fuel substitute\[(A x B)-D\] | N570,705 |

a. 35% of waste generation per day as at year 2018, b. See estimation of energy potential section

Table 6 illustrates energy derivable from MSW/day from the Lagos State metropolis compared with diesel
fuel oil. As observed from analysis despite high processing cost of MSW demonstrated in Table 5, it still proves
favorable against fossil fuel oil.

CONCLUSION
In many growing cities where population rate over shoots infrastructural development. Solid wastes, a

FUNDING STATEMENT

In many growing cities where population rate over shoots infrastructural development. Solid wastes, a
domestic energy resource with the potential to provide a significant amount of energy \[2\], is often over looked and
pushed aside. Taking 2016 as a reference, it is illustrated that there is an energy recovery potential of over 1300
GW/day with a high power potential of over 10,000 MW of power. This is observed to only increase due to
corresponding increase in population of the metropolis over the years as well as solid waste. This is not to spell
doom but to create a channel of alternative resource for the Lagos metropolis if the various landfill sites can be
converted to waste to energy (WTE) technology sites and in turn energy resources can be harnessed for other uses to
serve the growing population. In this article, a relationship between the parameters that makes up a proximate
analysis with energy content of MSW and its conversion to power is presented.

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The authors declare no conflicting interest as regards publication of this study.

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