http://dx.doi.org/10.23881/idupbo.017.1-5i

ARTÍCULOS–INGENIERÍAS

 

EVALUATION OF LANDFILL BIOGAS POTENTIAL IN BOLIVIA TO PRODUCE ELECTRICITY

 

EVALUACIÓN DEL POTENCIAL DE BIOGAS DE RELLENOS SANITARIOS EN BOLIVIA PARA PRODUCIR ELECTRICIDAD

 

 

Juan Pablo Vargas Bautista and Jorge Calvimontes

Centro de Investigaciones Ópticas y Energías(CIOE)
Universidad Privada Boliviana

jpvargas@upb.edu

(Recibido el 14 mayo 2017, aceptado para publicación el 23 junio 2017)

 

 

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ABSTRACT

The potential to produce electricity using landfill biogas in Bolivia was studied in this article. There important locations (Santa Cruz, La Paz and Cochabamba) and their solid waste disposal characteristics were considered. LandGem first–order degradation model was used to quantify the biogas production from the landfill. Recommend values of k and Lo available in the open literature were used since in Bolivia there are few landfills and no specific data are available (humidity, nutrients, pH, temperature, etc.). An average of 55.2% of the total solid waste in Bolivia is organic waste that can be used in landfills. The results showed that Santa Cruz can produce more landfill biogas than La Paz and Cochabamba. Using the methane obtained from the landfill biogas in reciprocating combustion engines, it was found that Santa Cruz can produce more electricity (265 GWh) than La Paz (175 GWh) and Cochabamba (110.4 GWh). The current electricity price in Bolivia (35 U$D/MWh) was used to evaluate the prefeasibility of the project, representing an average income of 281,061.0 U$D/y for Santa Cruz and 161,000.0 U$D/y for La Paz and Cochabamba, respectively. However, the economic analysis showed that IRR of 6.2%can be achieved for Santa Cruz and 7.9% for La Paz and Cochabamba, respectively, also higher payback periods were obtained (more than 9 years). La Paz and Cochabamba had the higher IRR and less payback period since only one reciprocating engine was chosen to cover the largest period of methane production while Santa Cruz used two. The economic indicators can be improved if international electricity prices are applied. The results presented in this article could provide valuable information to the solid waste management industry, policy makers and investors.

Keywords: Landfill Biogas, Solid Waste Management, Alternative Power Generation, Bolivia.

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RESUMEN

En el presente artículo se estudió el potencial de producción de electricidad con biogás de rellenos sanitarios en Bolivia. Se consideraron las ciudades más importantes (Santa Cruz, La Paz y Cochabamba) y sus características de eliminación de residuos sólidos. Se utilizó el modelo de degradación LandGem de primer orden para cuantificar la producción de biogás del relleno sanitario. Se usaron valores recomendados de k y Lo disponibles en la literatura abierta ya que en Bolivia hay pocos rellenos sanitarios y no hay datos específicos sobre la característica del desecho (humedad, nutrientes, pH, temperatura, etc.). Un promedio de 55.2% del total de desechos sólidos en Bolivia son residuos orgánicos que se pueden usar en rellenos sanitarios. Los resultados mostraron que Santa Cruz puede producir más biogás en vertederos que La Paz y Cochabamba. Usando el metano obtenido del biogás de relleno sanitario en motores de combustión interna, se encontró que Santa Cruz puede producir más electricidad (265 GWh) que La Paz (175 GWh) y Cochabamba (110.4 GWh). Se utilizó el valor actual de la electricidad en Bolivia (35 U$D/MWh) para evaluar la factibilidad del proyecto, lo cual representó un ingreso promedio de 281,061.0 U$D/año para Santa Cruz y 161,000.0 U$D/año para La Paz y Cochabamba. Sin embargo, el análisis económico mostró que un TIR de 6.2% se puede lograr para Santa Cruz y 7.9% para La Paz y Cochabamba respectivamente, también se obtuvieron mayores períodos de recuperación (más de 9 años). La Paz y Cochabamba tuvieron la TIR más alta y menos periodo de recuperación de la inversión, ya que sólo se eligió un motor de combustión interna para cubrir el período más largo de producción de metano, mientras que Santa Cruz utilizó dos. Los indicadores económicos pueden mejorarse si se aplican los precios internacionales de electricidad. Los resultados presentados en este artículo podrían proporcionar información valiosa a la industria de gestión de residuos sólidos, a los encargados de formular políticas y a los inversionistas. 

Palabras clave: Rellenos Sanitarios, Manejo de Residuos Sólidos, Generación Alternativa de Electricidad, Bolivia.

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1. INTRODUCTION

A landfill is a placed were all the waste from a region (city, municipality, county, among others) is disposal. Landfill biogas can be produced using organic waste from foodstuff (fruits, vegetables, greases, among others), yard grass, yard trimming, wood, straws and any other organic matter.  Microbial anaerobic digestion occurs in the organic waste and depending of the environment, disposal and organic composition, biogas is generated. Landfill biogas is compound mainly of methane CH₄(60% approximately) and carbon dioxide CO₂(40% approximately) [1]. The composition of the biogas is affected by the composition of the waste, landfill characteristics, local weather conditions and waste treatment, mainly.

The biogas that is generated in the landfill can be used to generate electricity using generators of internal combustion, also can be used as a fuel for water heaters. In this way, not only useful energy can be obtained from the landfill but also contaminants can be reduced as leachate contamination of surface and groundwater, and the release of greenhouse gases (GHG) to the atmosphere[2].

There are several projects worldwide that reports the feasibility of use landfill biogas to generate electricity instead of only incinerate the biogas [3-5]. The studies show the potential of electricity generation using landfill biogas models under specific conditions where two main parameters such us the methane generation potential (Lo) and the methane generation rate (k) are estimated for each case. These two parameters cannot be generalized and vary depending on the landfill characteristics.

No information exists in the open literature about the prefeasibility of electricity generation plants using landfill biogas in Bolivia, so this article will be focus on estimate the potential generation of landfill biogas to produce electricity, the reduction of GHG gases and its feasibility. Besides, in Bolivia there are only 3.1% of landfills, the rest are open dumping [6].These landfills burn up the biogas (methane and carbon dioxide) that is generated [7].

According to the Department of Environment, in Bolivia around 5470 t of solid waste are generated every day, equivalent to 1.99 million tons of solid waste per year from which 87.9% is generated in the urban area and the remaining 12.1% is generated in the rural area. The average generation per capita in Bolivia is of 0.5 kg of solid waste per day. The states that produce more solid waste are Santa Cruz (30.6%), La Paz (27.4%), and Cochabamba (17.2%). The average composition of the solid waste is showed in Figure 1, as it can observe, only 55.2% is organic matter from the solid waste that can be used in the landfill to produce biogas [6].

Figure 1 - Average composition of the solid waste in Bolivia[6].

In this article the solid municipal waste from Santa Cruz, La Paz and Cochabamba will be studied. First a description of a power generation plant using landfill biogas will be described to understand the necessary equipment to generate electricity. Then the model and the most important parameters to evaluate the landfill biogas and methane generation will be introduced. Finally, the estimation of the electrical generation using methane from the landfill and a simple economic analysis will be presented to estimate the feasibility of the project.

 

2. DESCRIPTION OF THE POWER GENERATION USING LANDFILL BIOGAS

Figure 2 shows the main components of a power generation from landfill biogas, as it can see the biogas is extracted from the landfill through a series of pipes then is storage and processed in order to use the biogas as a fuel in a reciprocating combustion engine which drives generators to produce electricity. The generated electricity is sent to a transformer to rectify the KVA according to the electric grid demand. It is important to mention that the combustion engine needs an exhaust chimney for the combustion gases and a cooling tower to chill the water that goes to the reciprocating engine[8-9].

Figure 2 -Scheme of a power generation using landfill biogas [10].

There are works that explain in detail all the process (collection field, collection piping, storage, filtration, among others) to obtain the biogas from the landfill to use it as a fuel to generate electricity [1, 2, 5, 8, 11, 12].

 

3. MATHEMATICAL MODEL TO PREDICT LANDFILL BIOGAS AND ELECTRICITY GENERATION

Landfill methane models are tools used to predict methane generation over time from a mass of waste in the landfill. These models have advantages in terms of low cost and relatively rapid results compared to other alternatives such as installation of test wells in the landfill to recover and measure the biogas [13].

Thanks to landfill gas models, it is possible to size the gas collection system, evaluate and project the available energy, size equipment, estimate costs, and evaluate the life time and feasibility of the landfill biogas.

Most widely accepted and used models are the first-order kinetic models [14]. These empirical models are adapted to specific landfills where the amount of waste, the gas formation potential, and effect of the age on the gas formation are the most important variables. Reinhart et al. analyze the different models to predict landfill biogas generation, as a conclusion they found that model parameters are highly dependent on moisture conditions and capture efficiency which are values difficult to quantify since more data from full-scale landfills are needed[14]. They found that U.S EPA LandGem model appears to fit the data of wet landfills. The Intergovernmental Panel on Climate Change (IPCC) outline the First Order Decay (FOD) methods to predict the methane generation from solid waste disposal sites, however, this method was not well adopted due to some key parameters dependent on country-specific conditions, and currently there are not enough data available to give reliable default values[15]. The empirical models are available in the open literature and open software [16-19].

In this article, the LandGem first-order degradation model was used to quantify the biogas production from the landfill, as seen in Equation 1.

(1)

Where:

Q… is total landfill biogas emission rate per year, m³/y
n… is the number of years of waste placement
k … is the landfill gas generation rate constant, y^-1
Mi … is the mass in mega grams of the solid waste section placed in year i, Mg
L0… is the methane generation potential, m³/Mg
ti ……is the age of the waste section placed in year i, y

Parameter k is selected in function of the humidity, nutrients, pH and temperature, when no information of these factors are available, the main factor is the rain precipitation of the place [16, 17], the typical range is between 0.01 to 1.Parameter Lois a function of the organic content of the residual waste mainly, the value of Lo varies from 56 to 198 m³ per ton or mega gram of solid waste [16, 17]. 

Table 1 shows the values that were used to estimate the landfill biogas and methane generation for the urban areas of Santa Cruz, La Paz and Cochabamba. Default and recommended parameters of k and Lo also were used in the absence of in-situ specific data,[16, 20, 21]. Slowly decay rates were considered since no data on types of organic waste are available in the open literature for Bolivian landfills[6], [18]. The mass of solid organic waste in the landfill is considered from data in section 1 and Figure 1. Details of the location and weather conditions from Santa Cruz, La Paz and Cochabamba can be seen in reference [6] and [8]. A conservative value of 50% is considered for the methane obtained from the landfill biogas.

TABLE 1 - PARAMETERS TO EVALUATE THE LANDFILL BIOGAS AND METHANE GENERATION

4. RESULTS AND DISCUSSION

Figure 3 shows the methane obtained from the landfill using Equation 1 and considering the data of 0. The year 2017 was assumed as the started year of the landfill. As it can be observed, the city of Santa Cruz can generate more methane from the landfill biogas than La Paz and Cochabamba due to more solid waste is available and higher value of k is assumed, based on that in Santa Cruz have higher decomposable waste environment than La Paz and Cochabamba [6], [14]. The maximum value for the three cases is obtained in 2028 where the landfill is closed and no more solid waste is placed, after that the generation of methane starts to reduce.

Figure 3 -Methane generation obtained from the landfill.

To estimate the electricity generation that can be obtained using the methane in a reciprocating combustion engine generator, the following equation was used:

(2)

where:

E.E.… is the electrical energy generated, GWh/y
… is the volumetric flow of methane CH₄, m³/y
LHV… is the low heating value of methane CH₄, GJ/m³
… is the efficiency of the reciprocating combustion engine generator

Figure 4 -Annual electricity potential generation.

The annual electricity generation using methane from the landfill as a fuel in the reciprocating combustion engine generator is shown in Figure 4. The results were obtained using the data of Table 1, Figure 3 and the Equation 2. A typical efficiency of a combustion engine of 34% was used [22], the altitude of the landfill was not considered for this evaluation. As it was expected, Santa Cruz can produce more electricity than La Paz and Cochabamba since more methane as a fuel is available. However, technical limitations do not allow using all the available methane in reciprocating combustion engine generators to produce electricity since it is not practical to put different capacities of combustion engines along the year to recover all the available methane. For example, Figure 5 shows the electricity that can be obtained in Santa Cruz using 2 reciprocating engines of 500 kW each one. Under this strategy, 10 GWh can be generated each year from 2022 to 2042 after that year, there is no enough methane to supply to the two reciprocating engines and only one will continue operating producing 5 GWh of electricity from 2042 to 2055. That means, from all the potential electricity that can be obtained in Santa Cruz (478 GWh) using the methane from the landfill, only 265 GWh (55.4%) can be available to use it. An average of 8.03 GWh per year could be delivered from 2022 to 2055.Considering the electricity price in Bolivia for generators of 35 U$D/MWh [23] a total income of 9.27 million U$D can be obtained in 33 years, which means an average income of 281,061 U$D per year.

Figure 5 -Available electricity generation in Santa Cruz.

Following the same procedure for La Paz and Cochabamba, Table 2 shows the potential electrical energy that can be generated using the methane obtained from the landfill, the available energy when reciprocating combustion engines are used, the total income obtained from the sales of the available electricity, and the average income per year that it can be obtained in the period that the electricity is available. For La Paz 175 GWh of electricity can be generated from 2021 to 2059 using one reciprocating engine of 500 kW, for Cochabamba 110 GWh of electricity can be generated from 2022 to 2046. As it can be observed, the results show that Santa Cruz has higher values than La Paz and Cochabamba for all the parameters presented in Table 2. Cochabamba and La Paz have similar average income of 161,000 U$D/y, 42.7% less than Santa Cruz due to the less available energy is obtained and only one reciprocating engine is used. The electricity price of 35 U$D/MWh is the same for the three cases.

TABLE 2 - SUMMARY OF RESULTS

Considering an investment cost of 2,000 U$D/kW and O&M cost of 13 U$D/MWh for the reciprocating combustion engine system [19], [21], and cycle life of 20 years, Table 3 presents a simple economic evaluation [24] to estimate the feasibility of the electricity generation using methane as a fuel from the landfill biogas. The cost of voltage transformers, electrical substations, and maintenance costs of the landfill, inflation and taxes were not considered in this analysis and only has to be used as a reference.

TABLE 3 - RESULTS OF THE SIMPLE ECONOMIC ANALYSIS OF THE RECOVER
LANDFILL BIOGAS TO PRODUCE ELECTRICITY

The results show that Cochabamba and La Paz have higher internal rate of return (IRR) and smaller payback period than Santa Cruz due to only one reciprocating engine was chosen to cover the largest period of methane production while Santa Cruz used two. Although the internal rates of return are positives for the three cases, these values could not be attractive for investors. However, more exhaustive and rigorous analysis has to be performed in order to obtain reliable values.

 

5. CONCLUSIONS

In this article the evaluation of landfill biogas potential in Bolivia is performed in order to estimate the electricity that can be generated if the methane obtained from the Biogas is used as a fuel in a reciprocating combustion engine. The LandGem model and the available data of the solid waste characteristics of the most important cities in Bolivia (Santa Cruz, La Paz and Cochabamba) were used to quantify the potential methane generation obtained from the landfill. The results shown that Santa Cruz can produce more methane than La Paz and Cochabamba (see Figure 3).

Santa Cruz could generate 265 GWh of electricity using the methane in reciprocating combustion engine while La Paz and Cochabamba could generate 215 and 110 GWh of electricity respectively (see Table 2). This represent an average income for 281,061.0 U$D/y for Santa Cruz and 161,000.0 U$D/y for La Paz and Cochabamba, respectively (see Table 2). Considering a commercial electricity price in Bolivia of 35 U$D/MWh [23], the economic analysis showed that IRR of 6.2% can be achieved for Santa Cruz and 7.9% for La Paz and Cochabamba, respectively, also higher payback periods were obtained (more than 9 years), see Table 3. Cochabamba and La Paz had the higher IRR and less payback period since only one reciprocating engine was chosen to cover the largest period of methane production while Santa Cruz used two. It seems that the low price of electricity in Bolivia is one of the main factors to obtain low IRR and high paybacks, for example, if an international electricity price of 70 U$D/MWh is considered, higher IRR are obtained (at least 20%) and less payback periods are achieved (around 4 years) for the three study cases. More exhaustive and rigorous economic analysis has to be performed in order to obtain reliable values.

A sensitivity analysis and an optimization of the capacities of the reciprocating combustion engine can be performed as a future work to determine the optimum number of generators and to identify important variables that affect the technical and economic feasibility of the project. Also environmental analyses can be added to the study to identify the GHG reduction using the methane to produce electricity instead of releasing to the atmosphere.

Other models to predict the generation of landfill biogas as IPCC can be used; also in situ data from the landfills have to be obtained for better prediction of methane efficiency capture and production especially for the k and Lo parameters.

Better policies, incentives and regulations are still needed in Bolivia like more competitive electricity prices, regulations to incentive the installation of landfills, among others.

The results presented in this article could provide valuable information to the solid waste management industry, policy makers and investors.

 

6. ACKNOLEDGMENT

The authors want to express their acknowledgment to the Research Department of UPB for the economic support, to Dra. Carla Quiroga for her technical support and recommendations.

 

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