Int. J. Environment and Waste Management, Vol. 26, No. 1, 2020 Downstream market analysis of used oils in Trinidad and Tobago to inform an appropriate waste management strategy Donnie Boodlal* Department of Process Engineering, The University of Trinidad and Tobago, Point Lisas Campus, Esperanza Road, Brechin Castle, Couva, Trinidad and Tobago Email: donnie.boodlal@utt.edu.tt *Corresponding author David Alexander Department of Petroleum Engineering, The University of Trinidad and Tobago, Point Lisas Campus, Esperanza Road, Brechin Castle, Couva, Trinidad and Tobago Email: david. alexander@utt.edu.tt Sarim Al-Zubaidy Office of the President, The University of Trinidad and Tobago, O’Meara Campus, Lots 74-98, O’Meara Industrial Estate, Arima, Trinidad and Tobago Email: sarim.alzubaidy@utt.edu.tt Maurissa Charles Basel Convention Regional Centre for Training and Technology Transfer in the Caribbean (BCRC-Caribbean), 8 Alexandra Street, St. Clair, Port of Spain, Trinidad and Tobago Email: maurissa.charles@bcrc-caribbean.org Abstract: The major issues with waste oil management in T&T are the lack of adequate strategies, technologies and collectors, which are addressed in this study. A survey of stakeholders’ views revealed that most preferred proper recycling and proper disposal and that they are prepared to enter into agreement with collectors to achieve these ends. The waste oil market in T&T was found to be sophisticated and partially unregulated. From data gathered, it is seen that the market volume of base oil in T&T is limited to 15 million litres/pa as this is the amount used in the nation’s sole blending facility. It was also found that the fuel oil market is saturated at 2.2 billion litres, which represented exports in 2016. The market volume for off-specification diesel could not be estimated as the only possible consumers and retailers of this product in T&T is disinterested in this product. Copyright © 2020 Inderscience Enterprises Ltd. 59 60 D. Boodlal et al. Keywords: waste oil management; market study; market survey; waste management. Reference to this paper should be made as follows: Boodlal, D., Alexander, D., Al-Zubaidy, S. and Charles, M. (2020) ‘Downstream market analysis of used oils in Trinidad and Tobago to inform an appropriate waste management strategy’, Int. J. Environment and Waste Management, Vol. 26, No. 1, pp.59–74. Biographical notes: Donnie Boodlal is an Associate Professor in Process Engineering at the University of Trinidad and Tobago. His main research areas include environmental management and clean production. He is also well renowned for his work in the field of GHG quantification and mitigation strategies. David Alexander has been a Lecturer and researcher at the University of Trinidad and Tobago (UTT) since 2007. He is currently the Overall Programme Leader of the Petroleum Engineering programmes at UTT. He has a wealth of experience in strategies for reducing anthropogenic greenhouse-gas emissions including enhanced oil recovery. Sarim Al-Zubaidy is the President and Acting Provost of the University of Trinidad and Tobago. He is a well published chartered environmentalist and has a wealth of experience in systems engineering, fluid handling systems, thermodynamics and environmental management. Maurissa Charles is a Project Execution Officer at the BCRC – Caribbean. She has a wealth of experience and research interest in the area of sustainable and environmental engineering. At the BCRC-Caribbean, she supports the implementation of projects that promote technology transfer and public awareness of environmentally sound management of hazardous wastes. 1 Introduction The used/waste oil market is one of the overlooked markets in the oil and process industries and therein lies one of the major problems (DETR, 2001; The Corporate Link Management Consultants, 2002). Used/waste oil plays an important role in the downstream industry and can potentially be a very profitable industry, but for this to happen there needs to be more research done. Development of infrastructure, financial incentives and legislation need to be put in place to facilitate a growing used/waste oil market as it represents a significant amount of the pollutants in the environment and thus needs to be treated with extra care. Based on the Washington State Legislature Standard, used oil means any oil that has been refined from crude oil, or any synthetic oil, that has been used and as a result of such use is contaminated by physical or chemical impurities. This definition is well accepted in T&T. An example of used oil would be oil that was drained from the engine of a truck or vehicle, lubricating oils, hydraulic fluids, metal working fluids, heat transfer fluid and insulating fluid to name a few. The definition of the term ‘waste oil’ is given in the Waste Oils Directive as any mineral-based lubrication or industrial oils, which have become unfit for the use for which they were originally intended, and in particular used Downstream market analysis of used oils in Trinidad and Tobago 61 combustion engine oils, gearbox oils, mineral lubricating oils, oils for turbines and hydraulic oils. Some of the constituents of used/ waste oils are water, fuel, carbon, metals and oxidation products. Probably the most common facility that generates waste oils is the automotive sector. Used/waste oils are generated in the service stations, garages, new car dealer showrooms and other retail establishments. In areas that are more highly industrialised, a majority of the used/waste oils are generated from the trucking, transportation and construction fleets along with public transportation and airports, which are also major contributors to the used/waste oil volumes. Second is often the industrial sector where the main used/waste oil are lubricating oils which include: turbine oils, gas engine oils, refrigeration oils, compressor oils and heat transfer oils (Boodlal et al., 2017). Third is the marine sector where a large number ships and vessels use huge volumes of lubricating oils and greases. They have collection tanks to retain the used/waste oil. These tanks are later discharged during port calls. A large volume of used/waste oil may also come from leakage/spillage from tankers which would have a plethora of negative environmental effects. Of paramount importance in this study is the determination of the sources, varieties, volumes and methods used to treat used oils generated in T&T. To provide a practical insight into all the above parameters of used oils of interest in this study, due cognisance was taken of the four principal sources of used lubricants – maritime, industrial, transportation, and others – as encapsulated in Figure 1. Figure 1 Principal sources of used oil (see online version for colours) Note: Please note this is not proportion representative. These used oils are classified as hazardous waste in many countries. If not managed properly, used oils can cause significant health and environmental problems. The proper 62 D. Boodlal et al. disposal of waste oil is vital in reducing these risks, as failure to do so can result in percolation through the soil and contamination of ground water. Subsequently this can lead to the destruction of both land and marine flora and fauna in proximity to the contamination. Some of these threats are explained below: • Just one gallon of used/ waste oils can make a million gallons of fresh water undrinkable (Sabock, 1994) • A film of used/waste oils prevents oxygen from entering the water and blocks sunlight, therefore plants will not be able to undertake photosynthesis and the effects will be compounded by the fact that oils tend to spread out more on the surface of the water thus affecting a larger area than predicted. • Dumping of used/ waste oils on lands can lead to the soils becoming unproductive. • Waste oils degrade very slowly, thus leading to extended periods where the effects of these in the environment can be felt. • Waste oils contain contaminants that are carcinogenic in nature and thus if ingested via contaminated drinking water or foods, can lead to serious side effects for humans and animals. New motor oils do have some traces of lead, which can cause mental retardation in children or if really bad, even death. • Uncontrolled burning of used/waste oils may result in significant levels of hazardous emissions to the environment. It follows therefore that more emphasis should be paid to the recycling (both at national and micro-enterprise levels), and/or re-refining of used/ waste oil. Recycling and recovery of used/waste oil will not only mitigate the negative impacts on health and the environment, but it can also help to conserve finite resources (Church, 2000; Motshumi et al., 2013). Simultaneously, these recycling and recovery processes often can yield significant benefits through the creation of profitable end products at the micro-enterprise level and the national level. There are three potential treatments of used/waste oil which will be considered in this study. All of these can give positive returns from this waste type. The first two of these fall under recovery, and the third under recycling (Danish Topic Centre on Waste and Resources, 2006). The first is direct use as a fuel. This may or may not require previous removal of water content in the waste oil. Users of waste oils as fuels have included cement kilns, combined heat and power and district heating plants (Giovanna et al., 2003; Chari et al., 2012). Plants burning waste oils direct are covered by the Incineration Directive which has set tight emissions standards. The second involves re-refining of waste oils to fuel oil. The resulting fuel oil is no longer considered as a waste and can be used as a fuel in any power plant or facility which can use this fuel type (Motshumi et al., 2013; Canadian Council of Ministers of the Environment, 1989). The third is the regeneration of waste oils to base oil which can be used as the basis for new lubricants (Hsu et. al., 2009; El-Fadel and Khoury, 2001). Side products from this process are fuel oil, oil sludge and wastewater. Only waste oils which have earlier been used as lubricants can be regenerated to base oil (i.e. which fall under category Water content should not be more than 10%). Base oil can be sold to lubricant blenders or mixed directly with various additives to produce lubricants of various qualities. There are many environmental Downstream market analysis of used oils in Trinidad and Tobago 63 benefits for these potential treatments, based on the surveyed literature (GEIR, 2016). These include: • Reduction in CO2 emissions The proposed recycling targets for waste oils would contribute to supporting the targets set by the European Union on CO2 emission reductions. Waste oil re-refining contributes to CO2 reductions associated with extracting and processing crude oil (AEU Technology, 1999). With modern re-refining technologies, CO2 emissions (kg of CO2 per ton of base oil) can be reduced by more than 50% as compared to the conventional production of base oil (Grice et al., 2014). • More sustainable production In comparison to the primary production of lubricants, re-refined waste oils save up to 30% of energy in the entire operation. The European Commission outlined in its Environmental Action Programme for 2020 (Endl and Berger, 2014) that the energy recovery (burning) should be limited to non-recyclable products. Modern re-refined base oils fulfil high standards on low sulphur, aromatic or phosphorus content and deliver a high viscosity index (Abdulkareem et al., 2014). • Avoidance of illegal dumping of used oils Recycling targets translate into higher collection rates, which reduce the potentially severe risks for human health and the environment arising from illegal dumping in water or soil or uncontrolled energy recovery (energy recovery (burning)) (Sigman, 1998). Illegal dumping of used oils in water could have serious environmental impact. Estimates indicate that one gallon of used oil dumped in water can contaminate up to 1 million gallons of clean water (McKenzie-Mohr & Associates, n.d.). • Improved life-cycle analysis (LCA) Based on commonly accepted LCA data, waste oil re-refining attributes positive environmental benefits. This is well documented in IFEU (2005). This paper seeks to address the best strategy for waste oil management in T&T using a market survey approach. In particular, the following are addressed: • Identification of the main sources of used oils in the country and estimations of the quantities and types of used oils produced, stored and disposed. • Identification of the key stakeholders in the waste used oil market in the country (mainly those in the production, distribution, storage, refining and utilisation). • Identification of existing disposal and treatment facilities and their capacities. 2 Method of study The research (taking due cognisance of the framework of the oil market in T&T) was carried out using a combination of desk study, primary data collection through the development and administration of questionnaires, and field visits. Primary data sources 64 D. Boodlal et al. were explored to generate the information required for various aspects of the study. The survey instruments to obtain primary data were sets of questionnaires addressed to the following groups of respondents: 1 the producers/importers of lubricating oils 2 the users of lubricants/generators of used oils 3 the dealers in used oils 4 the users of used oils. These structured questionnaires were prepared for the key target groups. They were aimed, among others, at the: • estimation of levels of usage of the different lubricants • estimation of the levels of generation of used oils from the different uses • determination of the roles of each stakeholder in the management of used oils in the country. For Trinidad, 63 stakeholders were identified. All of these were targeted with the survey instrument. However, only 26 responded. This represented approximately 41% of the identified population, which is still acceptable and consistent with historical sample sizes for surveys in Trinidad. These companies represented a range of industries, including vehicle maintenance and servicing, heavy industry, oil and gas and power generation. For Tobago 51 stakeholders were identified. All of these were targeted with the survey instrument. Responses were received from 48. This represented a 94% of the identified population, which is far beyond historical sample sizes for surveys in Tobago. This large sample size was possible as a ‘face-to-face’ approach was utilised in Tobago. 3 The market of base oils and virgin oils in Trinidad and Tobago Our interest in establishing the level of base oils entering T&T’s market in this study stems from the fact that it is a useful basis for estimating the level of generation of used oils. Consequently, the major marketers and the independent marketers were surveyed in this study. Prior to discussing the results of this survey, we establish the base oil volumes in T&T along with the major stakeholders. At the time of this study, T&T had its own crude oil refinery. At this refinery, crude oil from T&T’s production as well as imported crude oil is refined into many products for local consumption and export. Table 1 illustrates the local and export sales of some of these products manufactured from the Trinidad’s refinery process in 2016. Interestingly, from this data, we can see that no base oils from our refinery (most likely captured under the column ‘other refined/unfinished products’) were sold locally in T&T in 2016. Upon further investigations this trend also held for previous years. Most of the base oils produced from our refinery is exported. As such, one had to peruse the imported records for base oils to ascertain information on the supply of this commodity for T&T’s market. It should be noted however, that it was difficult to identify base oils from blended oils using T&T’s import records. Notwithstanding this, (with respect to base oils use in T&T), there appears to be one major actor. This is the state-owned Trinidad and Tobago National Petroleum Marketing Company (NP). Downstream market analysis of used oils in Trinidad and Tobago Table 1 65 Local versus export sales for products from Trinidad’s refinery Product Liquefied petroleum gas Motor gasoline Naphtha Aviation gasoline Kerosene/jet Gas oils/diesel Fuel oils Bitumen Sulphur Other refined/unfinished product Total Total sold locally (barrels) Total exported (barrels) 710,383 4,590,362 0 0 1,058,544 3,712,754 0 0 53,380 0 10,125,423 0 13,210,178 0 0 4,452,777 12,034,889 14,102,189 0 59,431 348,021 44,207,485 Source: MEEA (2016) This was verified when one compared the total import volumes of base oil in T&T with actual import volumes provided by NP. While the importation records suggest there are dispersed minor independent marketers for base oil in T&T, these are very insignificant volumes and were imported for use directly as lubricating oils. As such, no evidence of any operational oil blending facility was found in T&T, other than NP. It should be noted that while information was acquired that indicated the presence of another blended facility in Point Lisas, this facility is not operational at present, having ceased operations in 2016. 3.1 Levels of lubricating oil importation in T&T As stated earlier, the only possible major producer of virgin base oil in T&T is the country’s refinery. However, it seems that all of these are exported. As such, the base oil that is used in T&T (either pre or post blended), enters the T&T market as imports. When one examines this actual importation records for T&T, in 2015 it can be ascertained that from this alone, it is difficult to distinguish base oils from blended oils. The importation records are divided into four major categories; lubricating oil (paraffinic type), lubricating oil, waste oil and other lubricating preparations (such as greases). The respective amounts for these are shown in Table 2. Please note that since no volumes were provided for ‘other lubricating preparations’, this category is illustrated as a mass. Table 2 Oil importation records for T&T (2015) Oil importation categories Lubricating oil (paraffinic type) Lubricating oil Waste oil Other lubricating preparations (cutting oils, greases etc.) Volumes imported (litres) or mass imported (Kg) 51,000 litres 9,724,750,677 litres 235,650 litres 1,464,663 Kg It can be seen from this data that a total of 9,725,037,327 litres of lubricating oil (base and blended) was imported into T&T in 2015. In order to have a better appreciation of 66 D. Boodlal et al. the amount of this volume that is blended to produce virgin oils as compared to the amount already imported in a blended state, critical data from state owned NP (the only operational blending facility in T&T) was acquired and is expanded upon below. 3.2 Levels of production of virgin oils in T&T Base oils are imported into T&T and blended into virgin oils. At present, this is done via one facility and the base oils are supplied from the USA and blended into different grades of lubricants. Approximately 15 million litres of base oil are imported annually for this purpose, of which 80% is grade II and 20% is grade I. The categories of virgin oils produced from these base volumes are shown in Figure 2. Figure 2 Categories of virgin oil produced in T&T (see online version for colours) 3.3 Imported base oil volumes, sales and market share of companies in T&T Table 3 illustrates the imported base oil volumes along with sales and market share for various companies in T&T. These volumes all refer to engine oils, hydraulic/cylinder oils, outboard engines and gear/transmission oils. Table 3 Major marketers of base and/or blended oils in T&T Company/product name Level of importation of base oils (million litres/annum) Level of sales (million litres/annum) Market share Major shareholder Shell Castrol Total Supreme ESSO Kendall Chevron Valvoline Penzoil 15 0 0 0 0 0 0 0 0 0 17 (est.) 11 7 5.5 4 3.5 3.5 3 2 2 22% 16% 10% 8% 6% 5% 5% 4% 3% 3% 67 Downstream market analysis of used oils in Trinidad and Tobago Table 3 Major marketers of base and/or blended oils in T&T (continued) Company/product name Mobil Quaker State Conoco Amsoil Gulf Royal Purple Redline Liquimoly Schaeffer TOTAL Level of importation of base oils (million litres/annum) Level of sales (million litres/annum) Market share 0 0 0 0 0 0 0 0 0 15 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 72 2% 2% 2% 2% 2% 2% 2% 2% 2% 100% As such, the volume of base oil consumed in T&T annually is 15 million litres through one major shareholder. This accounts for about 22% of the total virgin oil market in T&T. As such, if this figure is extrapolated, 100% of the total virgin oil market is approximately 72 million litres annually. Correspondingly, the expected volume of generated waste oil in T&T should correlate to 72 million litres annually. 4 Results Some key aspects of the responses for Trinidad are shown and captioned in Figures 3, 4, 5, 6 and 7. These suggest that based on the sample size surveyed, the majority of waste oil in Trinidad is generated on a cyclic basis and stored in either metal drums, metal tanks or plastic drums before disposal. While a small percentage of stakeholders dispose the generated waste oil themselves, the majority of stakeholders (85%) send their waste oil to collectors. The survey also illustrated that most of the stakeholders in T&T (81%) are aware of waste oil recycling and a fair amount of these stakeholders (62%) are willing to pay to have their waste oil properly disposed. Figure 3 Trinidad responses to ‘Is your waste oil generation steady or cyclic?’ (see online version for colours) 68 D. Boodlal et al. Figure 4 Trinidad responses to ‘How do you store your waste oil before disposal?’ (see online version for colours) Figure 5 Trinidad responses to ‘How do you dispose your waste oil?’ (see online version for colours) Figure 6 Trinidad responses to ‘Are you aware of recycling of waste oil?’ (see online version for colours) Downstream market analysis of used oils in Trinidad and Tobago 69 Some key aspects of the responses for Tobago are shown and captioned in the Figures 8, 9, 10, 11 and 12. The figures suggest that based on this sample size, unlike Trinidad, the majority of waste oil in Tobago is generated on a steady basis and stored in plastic drums. Also interesting is that while the majority of stakeholders dispose their oil in Tobago through a collector (like Trinidad), this percentage is less than that of Trinidad (71% in Tobago versus 85% in Trinidad). This speaks to a more sophisticated market for waste oil management in Trinidad. This could be correlated to the higher levels of industrialisation in Trinidad when compared with Tobago. Again, the majority of respondents indicated that they are aware of the negative environmental effects of indiscriminate dumping of waste oil and the existence of waste oil recycling. This is an important behavioural characteristic for both markets, as it indicates that generators of waste oil would be more inclined to participate in a waste oil management system. Also, just as in the Trinidad market, the majority of respondents (79%) indicated that they would be willing to pay for collection, albeit this cost must be minimal. Figure 7 Trinidad responses to ‘Are you willing to pay to have your waste oil properly disposed?’ (see online version for colours) Figure 8 Tobago responses to ‘Is your waste oil generation steady or cyclic?’ (see online version for colours) 70 Figure 9 D. Boodlal et al. Tobago responses to ‘How do you store your waste oil before disposal?’ (see online version for colours) Figure 10 Tobago responses to ‘How do you dispose your waste oil?’ (see online version for colours) Figure 11 Tobago responses to ‘Are you aware of recycling of waste oil?’ (see online version for colours) Downstream market analysis of used oils in Trinidad and Tobago 71 Figure 12 Tobago responses to ‘Are you willing to pay to have your waste oil properly disposed?’ (see online version for colours) 4.1 The potential market for used oils in Trinidad and Tobago The used oil market in Trinidad appears to be very sophisticated. In addition, it was extremely difficult to acquire data on volumes of oil collected and for what purpose. Based on feedback from the survey instrument and related further interviews, many waste oil collectors were identified in Trinidad (as shown below). Though NP collects waste oil from their products, they contract the services of one or more of the previously identified dealers for eventual disposal. The team tried feverishly to acquire data from these dealers directly with respect to volumes and eventual disposal and/or usage but was not 100% successful. Many of these stakeholders were very secretive about their volumes and eventual use. Table 4 anonymously summarises the direct responses acquired from some of these stakeholders. Table 4 Company Waste oil collectors and dealers in Trinidad Annual volumes (litres) Eventual use A Less than 1,900,000 Recycled into low-grade base oil and exported B 1,200,000 Exported directly as waste oil for processing C 960,000 Used to run incinerators D 5,000 No data E 2,000 No data In addition to the above, indirect information was received that illegal dumping of waste oil is also taking place in T&T (particularly Guapo) and out at sea. However, no further data was received to verify these claims. Based on primary data acquired from T&T’s Customs and Excise Division, the total volume of exported used lubricating oils in T&T for 2016 was 242 million litres. This varies significantly with the annual volumes reported by the major waste oil dealers (which is approximately 4 million litres). In addition, this export volume also varies with the total amount of expected waste oil generated in T&T annually. This is interesting and somewhat perplexing. It seems as though one or a combination of the following scenarios apply: 72 D. Boodlal et al. • The volumes declared by the waste oil dealers are significantly less than actual. A more detailed waste oil inventory for Trinidad is required for this apparent gap to close. • It is possible that waste oil is being imported into Trinidad for the sole purpose of export. However, this was not illustrated in the data acquired. Further clarification was sought through the Environmental Management Authority (EMA) to elucidate into the two scenarios above. This response deduces the presence of the illegal export of waste oil from Trinidad. Volumes are being exported through the notification procedures to Nepal and the USA for the purpose of recovery. However, based on EMAs response, these volumes are small in comparison to other acquired data through Customs and waste oil dealers. 5 Conclusions In the final analysis, the volume of base oil consumed in T&T annually is 15 million litres. There is only one major player in the local blending market who converts these into virgin oil products for eventual use in T&T. This accounts for about 22% of the total related market in T&T, which is estimated at 72 million litres annually. As such, the expected volume of generated waste oil in T&T should correlate to 72 million litres annually. Based on the market survey across T&T, more stakeholders seem to be interested in a waste oil management system that ensures proper disposal and/or recycling of waste oil. The majority of them are willing to pay for proper disposal of their waste oil. Presently, most of these stakeholders already partake in an arrangement with collectors with respect to their generated waste oil. The island of Trinidad seems to have the more sophisticated collection system than Tobago. The analysis suggests the presence of eight major waste oil dealers in operating in Trinidad and eight in Tobago. While all the dealers in Tobago are only involved in collection and disposal, the dealers in Trinidad also seem to be involved in recycling, re-using and export. The three major possible products that can emanate from these along with their global prices (as no data were given for local prices) are given in Table 5. Please note that as identified in Section 2, the total volumes of waste oil that can be used for these products in T&T is 72 million litres. However, it seems as though some amount of this is already exported through the existence of a sophisticated collection and re-use market in Trinidad. Nonetheless, based on declared volumes from the associated collectors and dealers, a large amount may still be available for a waste oil management system in T&T. Table 5 Possible products and prices from waste oil Possible product Average global price Source Base oil 2.90 (USD/gal) NP Fuel oil 298.00 (USD/mt) WBP 1.80 (USD/gal) – estimate US EIA Off-specification diesel Downstream market analysis of used oils in Trinidad and Tobago 73 One valuable piece of information was that the price of waste oil collection in Tobago ranged from 100–400 TTD per barrel whilst in Trinidad the range was 80–200 TTD per barrel. While no explicit reason for this price variation was gathered from stakeholders, it could be due to the extra cost incurred for marine transportation from Tobago to Trinidad. References Abdulkareem, A.S., Afolabi, A.S., Ahanonu, S.O. and Mokrani, T. (2014) ‘Effect of treatment methods on used lubricating oil for recycling purposes’, Energy Sources, Part A: Recovery, Utilization, and Environmental Effects, Vol. 36, No. 9, pp.966–973. AEU Technology (1999) The reduction of greenhouse gas emission from the oil refining and petrochemical industry, s.n., UK. Boodlal, D., Alexander, D. and Seetahal, S. (2017) Downstream Market Analysis of Used Oil in T&T, Technical Report, BCRC-Caribbean WOMS-TT Project. Canadian Council of Ministers of the Environment (1989) Code of Practice for Used Oil Managment in Canada, Moneco Consultants Ltd., Ontario. Chari, K.R., Maurya. N., Tatia. P., Puri. N. and. Bir A. (2012) Compendium of Recycling and Destruction Technologies for Waste Oils, United Nations Environment Programme, s.l. Church, D. (2000) Used Oil Recovery, Reuse and Disposal in New Zealand: Issues and Options, Ministry for the Environment, Manatū Mō Te Taiao. Danish Topic Centre on Waste and Resources (2006) Dropping the Requirement for Waste Oil Regeneration-potential Socio-economic Impacts for Denmark, Højbro Plads 4, Copenhagen. Department of Environment, Transport and the Regions (DETR) (2001) UK Waste Oil Market, Oakdene Hollins Ltd., s.l. El-Fadel, M. and Khoury, R. (2001) ‘Strategies for vehicle waste-oil management: a case study’, Resources, Conservation and Recycling, Vol. 33, No. 2, pp.75–91. Endl, A. and Berger, G. (2014) The 7th Environment Action Programme: Reflections on Sustainable Development and Environmental Policy Integration, European Sustainable Development Network, Vienna, Austria. GEIR (2016) Waste Framework Directive Revision: European Waste Oil Re-refining Industry Position, Brussels: s.n. Giovanna, F., Khlebinskaia, O., Lodolo, A. and Miertus, S. (2003) Compendium of Used Oil Regeneration Technologies, United Nations Industrial Development Organization, Trieste. Grice, L. et al. (2014) ‘Life cycle carbon footprint of re-refined versus base oil that is not re-refined’, ACS Sustainable Chemical Engineering, Vol. 2, No. 2, pp.158–164. Hsu, Y., Lee, C. and Kreng, V. (2009) ‘Analysis and comparison of regenerative technologies of waste’, Transactions on Environment and Development, Vol. 5, No. 3, pp.295–301. IFEU (2005) Ecological and Energetic Assessment of Re-refining Used Oils to Base Oils: Substitution of Primarily Produced Base Oils including Semi-synthetic, GEIR, Heidelberg. McKenzie-Mohr & Associates (n.d.) Used Motor Oil Disposal, s.n., s.l. Ministry of Energy and Energy Affairs (MEEA) (2016) Energy Bulletin Reports, Ministry of Energy and Energy Industries [online] http://www.energy.gov.tt/publications/ (accessed 12 August 2017). Motshumi, J., Edison, M., Tsietsi. P. and. Mansoor, M. (2013) A Comparison of Waste Lubricating Oil Treatment Techniques, pp.106–109, s.n., Malaysia. Sabock, D. (1994) Water Quality Standards Handbook, Shippen, R.S. (Ed.), United States Environmental Protection Agency, The United States Water Resources Centre, Washington, DC. 74 D. Boodlal et al. Signman, H. (1998) ‘Midnight dumping: public policies and illegal disposal of used oil’, Rand Journal of Economics, Vol. 29, No. 1, pp.157–178. The Corporate Link Management Consultants (2002) Economic and Environmental Performance of Alberta’s Used Oil Program, s.n., s.l.