Research Article | | Peer-Reviewed

Attitudes and Environmental Awareness of Vehicle Service Technicians in Generating and Disposing of Waste Lubricant Oil in Ghana: Barriers to the Circular Economy

Received: 4 June 2026     Accepted: 16 June 2026     Published: 17 July 2026
Views:       Downloads:
Abstract

Inappropriate handling and disposal of waste lubricant oil (WLO) can lead to detrimental effects on soil and water matrices. Despite the documented economic and energy value of WLO, developing countries have not yet harnessed these opportunities due to a lack of information on quantities generated, perceived value, and infrastructure for collection, reuse, recycling, or disposal. In this study, the quantity of WLO generated and attitudes and environmental awareness of vehicle service technicians (n=329) were assessed in seven regions of Ghana. The mean volume of WLO generated was 35.6 L/shop/week, with southern urban suburbs generating more than their northern counterparts. Most (53%) technicians dispose of WLO by selling it, while 83.3% are aware that inappropriate disposal is detrimental to the environment. However, 10% discarded the WLO into sewers and soil. About two-thirds (63%) of vehicle service technicians are willing to use waste management services to dispose of WLO, but only 33% are willing to pay for such services. The study shows that closing the circular economy loop for the lubricant oil sector will have minimal barriers. Municipal waste management companies should invest in WLO collection infrastructure to help drive the circular economy of synthetic lubricating oils, reduce the fire hazard posed by improper WLO storage, educate technicians to eradicate soil and water contamination from poor waste oil handling and disposal practices, and safeguard ecosystem and human health in developing countries.

Published in International Journal of Science, Technology and Society (Volume 14, Issue 4)
DOI 10.11648/j.ijsts.20261404.11
Page(s) 131-139
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2026. Published by Science Publishing Group

Keywords

Waste Lubricant Oil, Vehicle Technicians’ Attitudes, Waste Quantification, Environmental Awareness, Circular Economy, Ghana

1. Introduction
Waste lubricant oil (WLO) is a hazardous waste with immense ecotoxicological potential and human health consequences if poorly managed. In the European Union, WLO ranked as the most voluminous hazardous waste generated, with an estimated 16 million tonnes produced per annum . In Africa, the leading economy in the generation of used lubricant oil, Alexandria in Egypt, discards 64% of the 1.4 × 105 tonnes of WLO annually into sewers, at the detriment of the environment . The damaging impacts of WLO discharged into environmental systems include heavy metal pollution of soil , changes in soil quality and ecology , water pollution (Parekh et al., 2024), food crops contamination with polyaromatic hydrocarbons and several ecotoxicological and human health risks . For example, the germination and seedling growth of lawn grass and tropical food crops were impeded by WLO-contaminated soil . Chromium, manganese, iron and zinc concentrations were higher in WLO-contaminated soil, resulting in elevated hazard quotients . Furthermore, without adequate regulatory oversight, WLO has also been used for environmentally unfriendly purposes, such as fuel in bakeries, weed killer, dust suppressant on dusty roads and bare grounds, and for rust prevention on spare vehicle parts . Not only are these uses greatly detrimental to the environment and ecosystems, but they also cause economic losses . To prevent the environmental degradation caused by the inappropriate disposal or use of WLO, a circular economy approach, which seeks to eliminate waste through product life cycle analysis, co-designing and greener energy alternatives to close the loop on material flow , should be adopted.
Life cycle assessment (LCA) of spent/used lubricant oils demonstrates that effective management of WLO as a resource rather than waste yields superior economic, social and environmental outcomes, vis-à-vis discharging into environmental matrices . Transforming the WLO to add value, a process known as valorisation, is highly recommended by circular economists and life cycle assessors . Valorisation of WLO can be achieved through various approaches, but energy recovery and base oil regeneration are the two major pathways . These pathways result in reduced soil and water degradation, lower greenhouse gas emissions , sustainable raw material usage, and increased revenue generation, while supporting Sustainable Development Goal (SDG) 12, which urges responsible consumption and production . Nonetheless, effective collection, transportation and recycling of WLO to realise the full enviro-socioeconomic benefits depend on up-to-date of location, frequency and quantity of the waste generated in the sector and a well-trained workforce to handle the waste. But data on industrial waste is scanty, with no specific study on WLO generation.
For several decades, Ghana has been experiencing an upward economic growth from increased government-private sector spending , stimulating industrialisation, agricultural expansion, increased mineral extraction, higher employment rates and a rise in vehicle ownership . These phenomena predict an upward trend of vehicle servicing and maintenance activities, and consequently rising levels of WLO generation. The management of WLO removed during the maintenance, inspections and repairs of commercial and private vehicles and heavy-duty machinery requires specialist services to safely handle and appropriately dispose of or recycle this hazardous waste. Managing waste with such high environmental risks requires clear policies, appropriate waste technologies, and well-trained personnel to support the sustainable development of cities . Therefore, recovery and proper valorisation or disposal of WLO to eliminate the adverse environmental effects associated with this hazardous waste cannot be achieved without insights into data on vehicle servicing technicians' waste management attitudes and environmental risk awareness. In this study, the volume of WLO removed from vehicles during servicing in seven regions of Ghana was evaluated. The environmental awareness of vehicle technicians of the damage caused by the inappropriate disposal of WLO, access and willingness to patronise waste management services for the disposal of WLO, and their current method of disposing of waste oil were also assessed. Insights from this study will inform planning, collection and recycling of WLO. The findings will also enable regulators to formulate functional policies, devise training/educational interventions for vehicle technicians to improve WLO collection and valorisation.
2. Materials and Methods
2.1. Description of the Study Area
This mixed-methods cross-sectional study was conducted in seven of the sixteen regions in the Republic of Ghana, situated on the coast of the Gulf of Guinea in Western Africa. The country is bordered to the North by Burkina Faso, East by Togo, South by the Atlantic Ocean and West by Côte d’Ivoire, with a total land area of 238,540 km2. The geographic coordinates of the land lie between 800N latitude and 200W longitude and hold about 31 million inhabitants . The cities and towns in the country have makeshift conglomerates of vehicle maintenance shops, such as Abossey-Okai in Accra, Suame Magazine in Kumasi and Kokompe in Takoradi, where engine and gearbox oil changes are conducted regularly for commercial and private vehicles . Often, these vehicle maintenance and service premises do not have concrete flooring with facilities to collect and treat oil spillages, leaving soil to absorb spilt oils.
2.2. Sample Size, Locations and Collection
A convenience sampling approach was employed to engage mechanics at vehicle servicing workshops in the suburbs of seven regions in Ghana. The survey was conducted in the regions of Greater Accra (Adenta, Tema Communities 1, 2 and 3, Gbawe, Oyarefa), Ashanti (Abrepo, Emina, Suame Magazine, Ohwim, Obuasi - Nyameso), Central (Cape Coast - Ayensudo, Assin Fosu), Eastern (Nkawkaw), Western (Kokompe -Takoradi), Western North (Sefwi Wiawso) and Upper West (Wa), shown in Figure 1. At each vehicle maintenance shop, informed consent was obtained from the lead service technician to participate in a week-long study where they saved all the waste lubricant oil removed from vehicle engines or gearboxes for the research team to measure the following week. After six working days, the research student returned to the workshop to measure the quantity of WLO collected. A total of 329 vehicle service stations in 17 districts and towns in 7 regions were assessed for the amount of WLO generated weekly.
Figure 1. Location of vehicle service stations where waste lubricant oil was quantified.
2.3. Quantification of Waste Lubricant Oil at Vehicle Maintenance Shops in Ghana
The volume of the WLO stored at the vehicle servicing station was measured by transferring the oil in the storage drum into a graduated 5 L Lube Oil container, which was subsequently poured into an empty drum and tallied. This method was repeated until the entire volume of WLO in the storage drum had been transferred and quantified. Appropriate personal protective equipment, including goggles, face masks, gloves, safety shoes, and protective clothing, was donned before handling the WLO.
2.4. Questionnaire Administration
A questionnaire was also completed with a senior vehicle technician at each sampled location. Demographic characteristics of the technicians, their method of disposal for WLO, access to MWMS and willingness to pay for such a service, as well as their environmental awareness of the consequences of improper disposal of WLO, were collected through the research instrument.
2.5. Ethical Approval and Consent to Participate Declaration
The methodology and the questionnaire for the study received ethical approval (HuSSREC/AP/279/VOL.4) from the Humanities and Social Science Research Ethics Committee at the Kwame Nkrumah University of Science and Technology (KNUST) before engaging with the participants. On each visit to the vehicle service technicians, informed consent was obtained from the participants, conforming to the ethical clearance requirements and the KNUST research ethics policy. Data collected did not include personally identifiable information, and participants were informed of their right to withdraw from the study if they wished to do so.
2.6. Data Analysis
The responses from the administered questionnaires were processed using the Statistical Package for Social Sciences software version 20 to generate descriptive statistics of the amount of WLO produced and the heavy metal content in the soil samples. Inferential statistics were also conducted on the responses to extrapolate and establish the correlations and associations between demographic characteristics of participants and their views on environmental impacts from their occupation and waste management preferences.
3. Results and Discussion
3.1. Amount of Waste Lubricant Oil Generated in Selected Regions of Ghana
The mean volume of WLO measured at vehicle service stations in Ghana was 35.6 L per week (Figure 2). The range of WLO in the study shops was between 1.2 L and 225 L per week. It was observed that highly populated urban towns and cities generated more WLO, with the highest found at Suame Magazine, an established area for vehicle maintenance, servicing and repairs in the country. To reduce the occurrences of WLO contamination of soil and water, high-generation areas where production exceeds the national average per week per shop should have designated tanker trucks for the WLO collection from the source to the refinery. These areas include Suame Magazine (108.5 L/w/shop), Abrepo (57.4 L/w/shop), Oyarefa (49.3 L/w/shop), Gbawe (35.5 L/w/shop) and Kokompe in Takoradi (66.5 L/w/shop), shown in Figure 2.
Figure 2. Waste lubricant oil generated at vehicle maintenance shops in regions and suburbs of Ghana.
3.2. Demographic Characteristics of Respondents
The vehicle service mechanics predominantly involved in the generation and handling of waste lubricant oil are mostly male (96.7%), aged below 40 years (77.8%), and have attained basic (40.4%) or secondary (44.7%) education (Table 1). Approximately one-third (78.4%) of the service station mechanics are highly experienced, with more than five years in the business. The male dominance in the sector is confirmed by . The laborious and exhaustive nature of this work may explain why females rarely engage in vehicle repairs, as observed by . In most African countries, females work in physically less demanding jobs, such as dressmaking , whereas work involving manual handling is often done by males . The age distribution of the vehicle servicing technicians is comparable to findings by . The low representation of technicians over 60 years may be attributed to the strenuous nature of the job, often requiring mechanics to work in hot weather for long periods, mostly carrying heavy loads, which may be difficult for technicians over 60 years. Furthermore, the Retirement age for men in Ghana is 60 years, and therefore, shop owners above this age work more in supervisory/management roles in the auto industry, as there is no state pension for non-government retirees. Among the respondents, 40.4% had completed basic education, 44.7% had completed senior high, and only a small fraction had completed tertiary or had no formal education. In Ghana, tertiary education is a significant financial burden for most families, and therefore, individuals seeking to work in apprentice-related careers often do not attain third-cycle education. This trend in the level of education among vehicle service mechanics is similar to that among fashion designers . Others also decide to drop out of school, as mechanics who are recruited at a very tender age grow into it and master its skills much earlier . Since most of the respondents were young, it confirms the results obtained on their years of experience, as the majority (35.6%) of them had 5 - 10 years of experience. The mechanic shops under study were more populated in the urban cities of Greater Accra and Ashanti regions than the rural cities of the other regions. This could be because it is assumed that urban cities open more opportunities to make wealth as they hold larger populations and hence more vehicles to service .
3.3. Disposal Preferences and Environmental Awareness of Vehicle Service Technicians
The method of WLO disposal used by respondents ranged from selling (52.9%) to collection by traders or WMS (32.2%), pouring into drains or on the ground (10.3%), and reuse or recycling (1.2%), as depicted in Table 1. This distribution is consistent with waste-disposal practices observed among secondhand clothing sellers in the Kumasi Metropolis, where rejected clothing from bale sorting was valued and often sold . The fraction of respondents who dispose of WLO inappropriately by pouring it into drains (10.3%) is comparable to those unaware that it is detrimental to the environment (16.7%) (Table 1). WLO discarded into drains and gutters forms an oil film on water surfaces that obstructs sunlight from reaching aquatic plants, making it difficult for photosynthesis to occur. This oil film also prevents oxygen diffusion into the water, restricting the respiration of fish. The oil layer also increases the BOD, leading to further depletion of dissolved oxygen in the water and suffocation of fish . The toxic substances, including polyaromatic hydrocarbons and heavy metals, in the WLO may also kill aquatic primary consumers that support the food chain . In Ghana, it is typical for rural dwellers to rely on streams and rivers for cooking, bathing, washing, and sometimes drinking . Downstream users of WLO-contaminated waterbodies may suffer health consequences .
The proportion of respondents who sold their WLO in this study (52.9%) is also similar to the observations elsewhere . Most (83.3%) of the respondents were aware that inappropriate disposal of WLO has adverse environmental impacts (Table 1), a finding that correlated with respondents' educational attainment (Table 2). Most (63.8%) service technicians expressed interest in using municipal waste management service (WMS) to reduce the environmental hazards, if the service were provided. Nevertheless, 67.2% of the study sample were unwilling to pay for such services. This may be due to the profit from selling the WLO, causing them to be reluctant to patronise another alternative, even though they recognise the environmental benefit of WMS in handling this hazardous waste correctly. Technicians' willingness to pay for WMS for the collection and disposal of WLO was also found to correlate with their age (Table 2), whilst their attitudes toward WLO disposal also correlated with their disposition to use WMS if available (Table 3).
Table 1. Sociodemographic characteristics, waste management practices and environmental awareness of respondents.

Demographics and perceptions

Options to question

Frequency

Percentage

Gender

Female

11

3.3

Male

318

96.7

Age

18 - 25

57

17.3

26 - 30

91

27.7

31 - 40

108

32.8

41 - 50

53

16.1

51 - 60

19

5.8

>60

1

0.3

Educational level attained

No formal education

133

40.4

Basic

28

8.5

Secondary

147

44.7

Tertiary

21

6.4

Years of experience as a service technician

< 5 years

71

21.6

5 - 15 years

188

57.1

>15 years

70

21.3

How do you dispose of your waste lubricant oil?

Collected by MWS

28

8.5

Collected by traders

78

23.7

Poured into drains or on the ground

34

10.3

Recycle/reuse

4

1.2

Sell

174

52.9

Other

11

3.3

Does the inappropriate disposal of WLO damage the environment?

Yes

274

83.3

No

55

16.7

Are you willing to use MWMS for oil disposal

Yes

210

63.8

No

119

36.2

Are you willing to pay for MWMS to collect the waste oil

Yes

108

32.8

No

221

67.2

Table 2. Correlation of respondents’ sociodemographic variables with their waste management preferences and environmental awareness.

Demographics of respondents

How do you dispose of your WLO?

Does inappropriate WLO disposal damage the environment?

Would you use MWMS if it were available?

Would you pay for such a service?

GENDER

Pearson corr. coeff.

.114*

-.038

.001

-.086

Sig. (2-tailed)

.039

.492

.989

.119

N

329

329

329

329

AGE

Pearson corr. coeff.

-.096

.046

-.141*

-.284**

Sig. (2-tailed)

.081

.401

.011

.000

N

329

329

329

329

EDUCATION

Pearson corr. coeff.

-.066

.113*

.056

.066

Sig. (2-tailed)

.232

.041

.308

.231

N

329

329

329

329

YEARS OF EXPERIENCE

Pearson corr. coeff.

-.075

-.119*

.046

.072

Sig. (2-tailed)

.176

.032

.407

.193

N

329

329

329

329

*. Correlation is significant at the 0.05 level (2-tailed); **. Correlation is significant at the 0.01 level (2-tailed).
Table 3. Correlation between participants’ waste management practices and their environmental awareness.

Would you use MWMS if it were available?

Would you pay for MWMS to dispose of your waste oil?

How do you dispose of your waste oil?

Pearson Correlation

-.151**

-.100

Sig. (2-tailed)

.006

.070

N

329

329

Does inappropriate waste oil disposal damage the environment?

Pearson Correlation

-.015

-.034

Sig. (2-tailed)

.784

.542

N

329

329

**. Correlation is significant at the 0.01 level (2-tailed). The correlation coefficients were interpreted as negligible (0.00-0.09), weak (0.10-0.39), moderate (0.40-0.69), strong (0.70-0.89), and very strong (0.90-1.00), as described by Schober and Schwarte (2018).
3.4. Implications: Opportunities and Threats
Currently, there are approximately 3 million registered vehicles in Ghana, estimated based on the 2.1 million registered vehicles in 2017 and the one million vehicles imported each decade . On average, private vehicles in Ghana cover 14,000 miles annually, higher than most European personal cars . Based on the recommended frequency for engine oil change after every 5000 to 10000 miles, from Toyota RAV4 models 2013 to 2022 manuals and a survey of drivers’ attitudes in Europe , while factoring in the age of the vehicle, poor road conditions, dust and traffic jams, vehicles’ engine oil may be changed three times each year in the country. Using an average engine oil sump capacity of 4.5 L for a 1.5 to 2 dm3 engine , an estimated 40.5 million litres of WLO would be removed by vehicle servicing technicians.
Through effective waste management practices, the estimated WLO could be recycled into base oil for the production of engine oil or burnt as fuel to provide energy for electricity generation, capturing the carbon dioxide emitted , serving as a major resource for the energy and oil manufacturing sector and closing the circular economy loop . With many African countries, such as Nigeria and Ghana, struggling to generate adequate electrical energy to meet domestic and industrial needs , effective collection and reuse of WLO in power stations could serve small communities or vital institutions, such as hospitals, during load shedding, increasing the nation’s energy security and productivity. Alternatively, recycling the 40.5 million litres of WLO generated per annum in the country could produce up to 36% yield of base oil , reducing the need for crude oil extraction (new resources) for base oil production .
However, failure to collect and appropriately valorise the 40.5 ML of WLO, a hazardous waste containing heavy metals and PAHs , poses a significant risk to water and soil contamination from WLO disposal practices. Improper disposal and unfriendly uses of the waste oil may result in severe ecological and human health risks from WLO entering the Ghanaian environment,
4. Conclusion
This research assessed the volume of waste lubricant oil generated in vehicle maintenance shops, vehicle technicians’ demographics, attitudes to waste disposal, awareness of environmental impacts, willingness to patronise and access to waste management services. The volume of WLO oil generated per shop is 35.6 L/week. Most vehicle service technicians are males (97%), formally educated (60%), and recognise that inappropriate WLO disposal is detrimental to the environment (83.3%). The majority dispose of WLO by selling (53%), but 10% pour it into drains, gutters or soil. 63% of vehicle service technicians are willing to pay for waste management services, which correlated with their age and disposal method. The study findings show that waste management companies should invest in the collection, recycling and disposal of this hazardous waste. The Ghana Environmental Protection Authority should educate and train vehicle technicians, improve monitoring of premises and enforce the guidelines to protect soil and water bodies in the country.
Abbreviations

LCA

Life Cycle Assessment

SDG

Sustainable Development Goal

WLOO

Waste Lubricant Oil

WMS

Waste Management Services

MWMSM

Municipal Waste Management Services

Author Contributions
Lawson Mensah: Conceptualization, Resources, Supervision, Writing – original draft
Nahima Mahama: Formal Analysis, Methodology, Data curation
Gideon Nkrumah: Data curation, Validation, Visualization
Bright Kwaku Agbekey: Methodology, Supervision, Data curation, Formal analysis
Evans Kwarteng: Conceptualization, Writing – review & editing, Data analysis
Ethel Bentil: Supervision, Writing – original draft
Lina Appiah-Nuamah: Data curation, Methodology, Writing – review & editing
Data Availability Statement
All the data supporting the findings of this study are included in the manuscript.
Conflicts of Interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
References
[1] Cabrera-Escobar, C., Moreno-Gutiérrez, J., Rodríguez-Moreno, R., Pájaro-Velázquez, E., Calderay-Cayetano, F., & Durán-Grados, V. (2025). A review on global recovery policy of used lubricating oils and their effects on the environment and circular economy. Environments, 12(5), 135.
[2] Waste Framework Directive. (2026). European Commission. Available online:
[3] Hassanain, E. M., Yacout, D. M., Metwally, M. A., & Hassouna, M. S. (2017). Life cycle assessment of waste strategies for used lubricating oil. The International Journal of Life Cycle Assessment, 22(8), 1232-1240.
[4] Okebalama, C. B., Onwurah, C. L., Jidere, C. M., & Okolo, C. C. (2024). Disposal of spent oil into soils around auto parts markets impacts heavy metal concentrations and poses a potential ecological risk. Environmental Systems Research, 13(1), 15.
[5] Nowak, P., Kucharska, K., & Kaminski, M. A. (2020). The new test procedure for group-type composition of base oils of lubricating oils, especially emitted into the environment. Energies, 13(15), 3772.
[6] Parekh, K., Gaur, R., & Shahabuddin, S. (2024). A facile approach for refining waste lubricant oil: A hazardous water contaminant. Materials Today: Proceedings.
[7] Tiwari, R., Agrawal, P., Bawa, S., Karadbhajne, V., & Agrawal, A. J. (2023). Soil contamination by waste transformer oil: A review. Materials Today: Proceedings, 72, 306-310.
[8] Ossai, I. C., Hamid, F. S., Aboudi-Mana, S. C., & Hassan, A. (2024). Ecotoxicological effects, human and animal health risks of pollution and exposure to waste engine oils: a review. Environmental Geochemistry and Health, 46(10), 416.
[9] Gawryluk, A., Stępniowska, A., & Lipińska, H. (2022). Effect of soil contamination with polycyclic aromatic hydrocarbons from drilling waste on germination and growth of lawn grasses. Ecotoxicology and environmental safety, 236, 113492.
[10] Ngozi, E. J., Ifechukwu, A. E., & Lawrence, A. N. (2017). Effects of used engine oil polluted-soil on seeds’ germination and seedlings’ growth characteristics of some tropical crops. International Journal of Environment, Agriculture and Biotechnology, 2(2), 812-818.
[11] Ikhajiagbe, B., & Ogwu, M. C. (2020). Hazard quotient, microbial diversity, and plant composition of spent crude oil-polluted soil. Beni-Suef University Journal of Basic and Applied Sciences, 9(1), 26.
[12] Pinheiro, C. T., Quina, M. J., & Gando-Ferreira, L. M. (2020). Management of waste lubricant oil in Europe: A circular economy approach. Critical Reviews in Environmental Science and Technology, 51(18), 2015-2050.
[13] Boadu, K. O. (2020). Removal of Contaminants In Used Lubricating Oil With Chemical Activated Carbons From Palm Kernel And Coconut Shells. (Doctoral dissertation, University of Port Harcourt).
[14] Kalmykova, Y., Sadagopan, M., & Rosado, L. (2018). Circular economy-From review of theories and practices to development of implementation tools. Resources, conservation and recycling, 135, 190-201.
[15] Jerez, S., Ventura, M., Molina, R., Pariente, M. I., Martínez, F., & Melero, J. A. (2021). Comprehensive characterization of an oily sludge from a petrol refinery: A step forward for its valorization within the circular economy strategy. Journal of Environmental Management, 285, 112124.
[16] García-Gutiérrez, P., Tonini, D., Klenert, D., Marschinski, R., & Saveyn, H. G. (2025). Environmental and economic assessment of waste lubricant oil management in the EU. Journal of Cleaner Production, 492, 144878.
[17] United Nations Department of Economic and Social Affairs, Sustainable Development, The 17 Goals, Available from:
[18] Mensah, L., Bentil, E., Agbekey, B. K., Nkrumah, G., Aidoo, I. A., Oti-Boakye, A., Owusu Sekyere, D., Sackey, L. N. A. (2026). Textile Waste from Fashion Shops and Imported Second-hand Clothing in the Greater Kumasi Sub-Region of Ghana: A Call for Policy Change, Environmental Challenges, 22,
[19] Aduteye, E. K., Tsatsu, S., Adjeiwaa, E. O., & Addo, F. (2023). Analysis of Ghana’s Gross Domestic Product from 1960-2019. J. Econ. Sustain. Dev.
[20] Atombo, C., Akuh, R., Turkson, R. F., & Liggie-Kudonoo, F. (2025). Examining fatal and non-fatal injuries of drivers in single-vehicle-involved crashes on urban roadways using random parameter logit model. International Journal of Injury Control and Safety Promotion, 32(1), 130-144.
[21] Daskal, S., Ayalon, O., and Shechter, M., (2019). Closing the loop: The challenges of regulation in municipal solid waste management. Detritus, (5).
[22] Ghana Statistical Service (2021), Population and Housing Census: General Report.
[23] Acheampong, F., Akenten, J. W., Imoro, R., Agbesie, H. R., & Abaye, D. (2016). Evaluation of Heavy Metal Pollution in the Suame Industrial Area, Kumasi, Ghana. Journal of Health and Pollution, 6(10), 56-63.
[24] Jayeola, O., Sidek, S., Owoeye, I., & Kazeem, Y. K. (2020). Gender and the performance of informal sector enterprises. European Scientific Journal, 16(4), 57-73.
[25] Monney, I., Bismark, D. A., Isaac, O. M., & Kuffour, R. A. (2014). Practices among vehicle repair artisans in an urban area in Ghana. J Environ Occup Sci, 3(3), 147.
[26] Enyoh, C. E., & Isiuku, B. O. (2020). Characterisation of some soils from flood basin in Amakohia, Owerri. Nigeria Int. J. Environ Anal Chem.
[27] Azorji, J., Okechukwu, R. U., Udebuani, A. C., & Duru, C. M. (2022). An Appraisal of the Volume, Potential Use and Disposal Methods of Spent Engine Oil Generated in Selected Mechanic Workshops in Imo State, South-East Nigeria. Journal of Environmental Treatment Techniques, 10(3), 228-234.
[28] Enwezor, W. O., Ohiri, A. C., Opowaribo, E. E., & Udo, E. J. (2020). A review of soil fertilizer use in crops in Southeastern zone of Nigeria (in five volumes). Produced by the Fed. Min. Agric and Nat. Re. Lagos.
[29] Morshed, M., Hosen, M., & Asaduzzaman, M. (2021). A Review on pH, DO and BOD of the Sitalakhya River during Last Four Decades. Asian J. Fish. Aquat. Res, 14(1), 25-42.
[30] Vural, U. S. (2020). Waste Mineral Oils Re-refining with Physicochemical Methods, Turkish Journal of Engineering, 4(2), 62-69.
[31] Michael, A. (2015). Used oil storage and disposal practices in automobile repair garages in Ghana. International Journal of Science, Technology and Society, 3(4), 191-201.
[32] Ayetor, G. K., Quansah, D. A., & Adjei, E. A. (2020). Towards zero vehicle emissions in Africa: A case study of Ghana. Energy Policy, 143, 111606.
[33] Ackom, G. (2017). Vehicle emission enforcement, Air Quality and Mobility Unit, United Nations Environmental Development Programme.
[34] Gössling, S., Kees, J., & Litman, T. (2022). The lifetime cost of driving a car. Ecological Economics, 194, 107335.
[35] Wolak, A., & Zając, G. (2019). An empirical study of the variables affecting the frequency of engine oil change in the environmental aspect. Environmental Protection Yearbook, 21.
[36] Kyando, M. J., Ntalikwa, J. W., & Kivevele, T. (2025). Effects of Mileage on Engine Oil of an Aged Spark Ignition Retrofitted Engine Fueled by Gasoline and Compressed Natural Gas. International Journal of Energy Research, 2025(1), 9989894.
[37] Maceiras, R., Alfonsín, V., & Morales, F. J. (2017). Recycling of waste engine oil for diesel production. Waste management, 60, 351-356.
[38] Avordeh, T. K., Salifu, A., Quaidoo, C., & Opare-Boateng, R. (2024). Impact of power outages: Unveiling their influence on micro, small, and medium-sized enterprises and poverty in Sub-Saharan Africa-An in-depth literature review. Heliyon, 10(13).
[39] Prempeh, K. B. (2023). The impact of financial development on renewable energy consumption: new insights from Ghana. Future Business Journal, 9(1), 6.
[40] Ani, I., Okafor, J., Olutoye, M., & Akpan, U. (2015). Optimization of base oil regeneration from spent engine oil via solvent extraction. Adv Res, 4(6), 403-411.
[41] Hegazi, S. E. F., Mohamd, Y. A., & Hassan, M. I. (2017). Recycling of waste engine oils using different acids as washing agents. International Journal of Oil, Gas and Coal Engineering, 5(5), 69-74.
Cite This Article
  • APA Style

    Mensah, L., Mahama, N., Nkrumah, G., Agbekey, B. K., Kwarteng, E., et al. (2026). Attitudes and Environmental Awareness of Vehicle Service Technicians in Generating and Disposing of Waste Lubricant Oil in Ghana: Barriers to the Circular Economy. International Journal of Science, Technology and Society, 14(4), 131-139. https://doi.org/10.11648/j.ijsts.20261404.11

    Copy | Download

    ACS Style

    Mensah, L.; Mahama, N.; Nkrumah, G.; Agbekey, B. K.; Kwarteng, E., et al. Attitudes and Environmental Awareness of Vehicle Service Technicians in Generating and Disposing of Waste Lubricant Oil in Ghana: Barriers to the Circular Economy. Int. J. Sci. Technol. Soc. 2026, 14(4), 131-139. doi: 10.11648/j.ijsts.20261404.11

    Copy | Download

    AMA Style

    Mensah L, Mahama N, Nkrumah G, Agbekey BK, Kwarteng E, et al. Attitudes and Environmental Awareness of Vehicle Service Technicians in Generating and Disposing of Waste Lubricant Oil in Ghana: Barriers to the Circular Economy. Int J Sci Technol Soc. 2026;14(4):131-139. doi: 10.11648/j.ijsts.20261404.11

    Copy | Download

  • @article{10.11648/j.ijsts.20261404.11,
      author = {Lawson Mensah and Nahima Mahama and Gideon Nkrumah and Bright Kwaku Agbekey and Evans Kwarteng and Ethel Bentil and Lina Appiah-Nuamah},
      title = {Attitudes and Environmental Awareness of Vehicle Service Technicians in Generating and Disposing of Waste Lubricant Oil in Ghana: Barriers to the Circular Economy},
      journal = {International Journal of Science, Technology and Society},
      volume = {14},
      number = {4},
      pages = {131-139},
      doi = {10.11648/j.ijsts.20261404.11},
      url = {https://doi.org/10.11648/j.ijsts.20261404.11},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.ijsts.20261404.11},
      abstract = {Inappropriate handling and disposal of waste lubricant oil (WLO) can lead to detrimental effects on soil and water matrices. Despite the documented economic and energy value of WLO, developing countries have not yet harnessed these opportunities due to a lack of information on quantities generated, perceived value, and infrastructure for collection, reuse, recycling, or disposal. In this study, the quantity of WLO generated and attitudes and environmental awareness of vehicle service technicians (n=329) were assessed in seven regions of Ghana. The mean volume of WLO generated was 35.6 L/shop/week, with southern urban suburbs generating more than their northern counterparts. Most (53%) technicians dispose of WLO by selling it, while 83.3% are aware that inappropriate disposal is detrimental to the environment. However, 10% discarded the WLO into sewers and soil. About two-thirds (63%) of vehicle service technicians are willing to use waste management services to dispose of WLO, but only 33% are willing to pay for such services. The study shows that closing the circular economy loop for the lubricant oil sector will have minimal barriers. Municipal waste management companies should invest in WLO collection infrastructure to help drive the circular economy of synthetic lubricating oils, reduce the fire hazard posed by improper WLO storage, educate technicians to eradicate soil and water contamination from poor waste oil handling and disposal practices, and safeguard ecosystem and human health in developing countries.},
     year = {2026}
    }
    

    Copy | Download

  • TY  - JOUR
    T1  - Attitudes and Environmental Awareness of Vehicle Service Technicians in Generating and Disposing of Waste Lubricant Oil in Ghana: Barriers to the Circular Economy
    AU  - Lawson Mensah
    AU  - Nahima Mahama
    AU  - Gideon Nkrumah
    AU  - Bright Kwaku Agbekey
    AU  - Evans Kwarteng
    AU  - Ethel Bentil
    AU  - Lina Appiah-Nuamah
    Y1  - 2026/07/17
    PY  - 2026
    N1  - https://doi.org/10.11648/j.ijsts.20261404.11
    DO  - 10.11648/j.ijsts.20261404.11
    T2  - International Journal of Science, Technology and Society
    JF  - International Journal of Science, Technology and Society
    JO  - International Journal of Science, Technology and Society
    SP  - 131
    EP  - 139
    PB  - Science Publishing Group
    SN  - 2330-7420
    UR  - https://doi.org/10.11648/j.ijsts.20261404.11
    AB  - Inappropriate handling and disposal of waste lubricant oil (WLO) can lead to detrimental effects on soil and water matrices. Despite the documented economic and energy value of WLO, developing countries have not yet harnessed these opportunities due to a lack of information on quantities generated, perceived value, and infrastructure for collection, reuse, recycling, or disposal. In this study, the quantity of WLO generated and attitudes and environmental awareness of vehicle service technicians (n=329) were assessed in seven regions of Ghana. The mean volume of WLO generated was 35.6 L/shop/week, with southern urban suburbs generating more than their northern counterparts. Most (53%) technicians dispose of WLO by selling it, while 83.3% are aware that inappropriate disposal is detrimental to the environment. However, 10% discarded the WLO into sewers and soil. About two-thirds (63%) of vehicle service technicians are willing to use waste management services to dispose of WLO, but only 33% are willing to pay for such services. The study shows that closing the circular economy loop for the lubricant oil sector will have minimal barriers. Municipal waste management companies should invest in WLO collection infrastructure to help drive the circular economy of synthetic lubricating oils, reduce the fire hazard posed by improper WLO storage, educate technicians to eradicate soil and water contamination from poor waste oil handling and disposal practices, and safeguard ecosystem and human health in developing countries.
    VL  - 14
    IS  - 4
    ER  - 

    Copy | Download

Author Information
  • Abstract
  • Keywords
  • Document Sections

    1. 1. Introduction
    2. 2. Materials and Methods
    3. 3. Results and Discussion
    4. 4. Conclusion
    Show Full Outline
  • Abbreviations
  • Author Contributions
  • Data Availability Statement
  • Conflicts of Interest
  • References
  • Cite This Article
  • Author Information