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VOL. 6, NO. 2, February 2016 ISSN 2225-7217
ARPN Journal of Science and Technology ©2011-2016. All rights reserved.
http://www.ejournalofscience.org
60
Used Oil Re-Refining Techniques in Nigeria-Economic Benefits *1 Lukman Animashaun, 2 Adekunle Yekinni, 3 Bethan Warren
1,2 Department of Mechanical Engineering, Lagos State Polytechnic, Ikorodu, Lagos 3 School of Mechanical Engineering, Institute of Functional Surfaces, University of Leeds, UK.
* Corresponding Author:
ABSTRACT The basic functions of lubricating oil in machines are to minimize friction and wear in order to enhance their life-span of
machines. When lubricating oils have been used beyond their recommended life span, improper disposal can be harmful to
the environment. In this paper, used oil sources and different collection techniques were identified with the objective to
show that enhanced collection rate could stimulate used oil re-refining. Based on various used oil re-refining techniques, a
program was formulated that will not place the burden of disposal only at the door step of the facilities generating the
waste oil alone, but also as the collective responsibility of the government and the waste oil processing program
managements. An empirical relationship was obtained for the economic benefit in terms of, the amount of waste oil
drained per car per year and the collection rate of waste oil for any given year above 2009.
Keywords: Lubricant additives, Recycling, Re-refining, Feed stock, Do-it-yourselfers, Do-it-for-me’s
1. INTRODUCTION Lubricating oils are viscous liquids used to
lubricate moving parts of machines and engines. These
oils are mainly composed of complex mixtures of
hydrocarbon molecules and inorganic additives in order to
protect rubbing surfaces from friction, wear and excessive
heating. In addition, further desirable properties of
lubricating oils are sealing of spaces and engine
cleanliness. Lubricating oils can be categorized into;
semi-solid lubricating greases, automotive oils and
industrial lubricating oils.
Lubricating oils are produced during crude oil
refining to give base oil or base stock which is blended
with additives. The lubricant base oil could be either
mineral oil or synthetic base oil (Poly alpha Olefin etc.).
In order to meet the desired functions of these
lubricants under high loads, chemical agents called
additives are added to the base oil at low concentration in
order to reinforce or impact their function by either
interacting chemically or physically with engine metallic
surfaces. These additives can be; antiwear/EP, friction
modifier, oxidation inhibitor, corrosion and rust inhibitor,
dispersant, detergent, viscosity index improver, pour point
depressant, storage inhibitor and foam inhibitor to give
what is known as fully formulated oil.
When fully formulated oil is put into an internal
combustion engine for use, it is essentially degraded by
heating and oxidation to breakdown the additives for
optimum lubrication performance. However, after about
5,000 kilometers of engine use, these additives can no
longer provide desired functions expected of it. Hence, it
is drained off the engine to become what is known as used
oil. Used motor oil is a hazardous waste that is known to
contain heavy metals, contaminants and dirt discarded by
the engine during use. A study of fresh fully formulated
oil with low concentration of heavy metals such as;
Vanadium (V), Lead (Pb), Aluminum (Al), Nickel (Ni)
and Iron (Fe) gave higher concentration in the spent oil
(Adebiyi, Oluyemi, & Peter, 2011; Anoliefo, Ikhajiagbe,
Okonofhua, & Diafe, 2006). Used oil is only dirty but not
worn out, hence the need for re-refining
The main sources of used oils in Nigeria was
categorized as; transportation, industry and private
electricity generation (Anoliefo et al., 2006; Bamiro &
Osibanjo, 2004). Worldwide demand for lubricating oils
for industrial processes, passenger and heavy goods
vehicles was estimated to be about 51.3 billion
liters(Anoliefo et al., 2006; Szramka, 1994). Annual
volume of used oil in Nigeria was estimated as 150
million liters with only about 90 million liters available
for processing based on 30 % collectible (Bamiro &
Osibanjo, 2004).
A convenient way of disposing used oil by auto-
technician and allied artesian is disposal into gutters, open
vacant plots and waterways. This practice can lead to
environmental problems, risk to human health and plants
including microbial activity and fertility in soil (Anoliefo
et al., 2006; McGrath, Chaudri, & Giller, 1995). Another
means of disposing used oil is by burning in furnaces to
generate heat or in power plants to generate electricity. A
blend of used oil can be used; as marine fuel, asphalts
mixture for road paving or used for industrial plant
boilers, space heaters and other industrial heating
applications such as cement kilns and blast furnace whose
product of combustion can exacerbate air pollution
problems. Used oil re-refining is a process of restoring
used oil to new oil by removing water, dirt, heavy metals
and chemical impurities.
This paper will assess the economic benefits of
enhanced management of used oil from increasing motor
vehicle growth.
The objectives of this paper are to;
Literature review on the existing
techniques/procedure/schemes
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61
Proposed techniques for used lubrication oil
recycling
Project motor vehicle growth rate
Establish an economic relationship between
increased used oil processing, number of
vehicles and number of liters of used oil from
cars per service per year.
2. LITERATURE REVIEW OF THE
EXISTING TECHNIQUES /
PROCEDURE / SCHEMES
Used lubricating oil management involves;
1. Collection
2. Re-refining in lubricating oil recovery
3. Re-refining in dedicated grass-root unit
4. Reprocessing in primary refinery
5. Reprocessing to fuel
6. Burning untreated used oil
7. Disposal
In order to conserve the original properties of the
oil for possible re-use, the most feasible first option of re-
refining lubricating oil is recovery. This can be
accomplished through re-refining, recycling and/ or
destruction. Re-refined used engine oil implies using
additional treatment processes to remove soluble and
insoluble impurities, while recycled or reconditioned used
engine oils implies using commercial filtration processes
to remove insoluble impurities
Figure 1 (a) and (b) shows the schematic diagram
of different types of basic used oil refining plants with
Figure 2 indicating typical re-refined used oil is as shown
in compares to used oil.
2.1 Reprocessing
The aim is to produce an end product that is low
in basic sediment and water content with the primary
purpose of not clogging sediment build-up in customer
tanks or system during use. Hence, this is a physical
treatment process that involves settling, filtration or a
combination of these operations. However, these
processes are not sufficient to remove all chemical
contaminants; hence the inclusion of other processes such
as clay contacting and distillation could produce better
results
2.2 Re-refining
This type of used oil recycling involves among
many other options; pre-treatment by filtration, vacuum
distillation with clay contacting. The other option involves
solvent extraction with clay and chemical treatment by
hydro-heating. A typical used oil processing steps is
summarized in Figure 2.
(a)
(b)
Figure 1:Schematic diagram of (a) solvent extraction/clay re-refining used oil processing and (b) acid treatment/clay-
percolation used oil re-refining process(Emam & Shoaib, 2012)
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62
A typical used oil processing steps is summarized in Figure 2.
Figure 2:Used oil processing steps (Harrison, 1994)
2.3 Incineration
When the waste oil is tested to be highly
contaminated with polychlorinated biphenyls (PCB) and
polychlorinated terphenyls (PCT), this method of waste
management offers the best choice. Hazardous waste
incinerators or controlled high-temperature at cement
factories can be used to eliminate organics and
neutralize acids at temperatures in excess of 2400 oC with
continuous monitoring of gas emissions (Arnaout, 1997).
In this way, the amount of heavy metal is expected to be
greatly reduced. A comparison of used oil to re-refined
used oil is as shown in Figure 3,
Figure 3:A typical used oil is contained in the right bottle and left bottle contain re-refined oil (Merai Yash)
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2.4 Used Oil Processing in Nigeria
An extensive study of used oil processing in
Nigeria was conducted by (Bamiro & Osibanjo, 2004)
where the various waste management options considered
is as shown in Figure 4.
Two companies and one government agency
were identified to have attempted to process used oil.
However, these attempts had not yielded desired results
due to financial and technological factors. In addition, a
major constraint towards achieving desired goals by
different companies is the availability of sufficient
quantity and quality of used oil as feedstock. In view of
problems regarding feedstock supply at the right quality
and quantity, poor waste lubricating oil collection
management appears to be a major challenge that needs to
be addressed in order to encourage used oil re-refining in
Nigeria.
Figure 4:Used oil management options for Nigeria(Bamiro & Osibanjo, 2004)
2.5 Type of Products and By-Products
This phase involves targeting customers in order
to make economic decisions. The two primary options are
to recycle used oil to virgin quality base oil market or
distillate fuel requirement (marine diesel oil used to power
medium speed engines). The by-products of used oil
processing plant is as summarized in Figure 5.
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64
Figure 5:Used oil processing steps (Harrison, 1994)
3. FORMULATING USED OIL RE-
REFINING PROGRAM There are two types of people that used oil can
be obtained from. These are do-it-yourselfers and do-it-
for-me’s. Those that change their own oil themselves in
order to save money or take pride in the quality of their
own workmanship are do-it-yourselfers, while do-it-for-
me’s have their oil changed at service stations and other
mechanic places or quick lubes. About 30% of motorists
are known to change their own oil based on a survey,
hence it is important that do-it-yourselfers are encouraged
to re-refining their used oils. In order to encourage this
category of used oil sources, oil waste lubricating oil re-
refining programs need to be located throughout every
locality. Urban areas are particularly in need of this type
of program as more motor oil is used in these areas due to
the large number of vehicles in these areas.
Used oil sources will have to collect used oils in
leak-proof container with secure screw-on top lids. For
do-it-yourselfers, they may choose to reuse the oil’s
original container or utilize another household container
that can prevent leakage or spillage, while for do-it-for-
me’s, large containers like drums are necessary due to
higher volume of generation. The various sources of used
oil are summarized in Figure 6. The challenge is how used
oils can be collected from various sources.
Three approaches could be necessary in order to
meet this challenge; use of curbside collection program
where regular garbage trucks are adapted with metal
storage tanks (this collection program is most suitable for
metropolitan areas), use of service stations, garages and
automotive service centres, and drum collection program
where 55 liters drums are place for collection (most
suitable for rural areas with few service stations or
garages or premises of businesses and government
agencies.
In formulating successful used oil processing
programs, positive economics and reliable technology are
necessary since it involves environmentally unfriendly
waste to a valuable product with motivating factors that
include concern for environmental and legislative
restrictions. In this program, consideration must be given
to the charge stock availability, type of products and by-
products that will be produced from different processes.
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Figure 6:Used oil sources (Andrews, 2008)
3.1 Feed Stock Characteristics
The quality of used oil is certainly variable
which unlike most refineries has reasonably consistent
feed quality. Used oil quality is a function of the materials
dumped into it which can be contaminants, collection
system, and type of sample monitoring and testing.
Contaminates can range from gasoline and diesel
from internal combustion engines, synthetic motor oils,
water, wear metals, tank bottoms, soot and so on. A
method of minimizing the variable quality of used oil is
by collection in larger lots in big tanks in order to
homogenize the final quality.
3.2 Engineering Challenge in Process Facility Design
Used oil by its nature is very corrosive under
certain operating conditions as it contains organic and
naphthenic acids which could be as a result of the
followings; by-products of internal combustion engines,
naturally acids inherent in the oil or acid introduced from
external sources. The resulting effect of these acids on
processing tanks often cause rapid and catastrophic
corrosion failures and /or gradual metal corrosion, hence
the use of some corrosion resistance material without
sacrificing other engineering requirements. In addition,
energy is required to be provided for the heaters and the
entire plant.
3.3 Used Oil Collection Program
This program is essential for any used oil re-
refining processing plans. Figure 7 indicated a generalized
model for used oil collection schemes in order to ensure
adequate supply. A study of collection methods from
different countries around the world revealed that the
Japanese approach will be most suitable for Nigeria. This
approach requires the public to turn in their used oil in
order to buy a new one. In addition, the local government
cooperates with local residence’ association, gas stations
and companies to form small scale generators of waste
oils who forwards the collected used oil to a central
collection centre; State Governments Waste Management
Authorities in Nigeria lubricating oil collection program.
However, a key element in the collection chain is
the carrier or transporter who undertakes used oil
transportation between the small scale generator and
regional collection centre or between the regional
collection centre and the central collection station
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Figure 7:Multi-layered used lubricating oil collection scheme (Andrews, 2008)
3.4 Public Awareness
Used oil collection programs could be enhanced
with increasing publicity through the print and electronic
media to educate and inform the public on how and where
to dispose of their waste lubricating oils and filters. In
addition to these, visual displays could be made on how
used oil should be handled and transferred to collection
sites by automobile parts stores and auto-repair shops.
The public need to be aware of the consequences of
improperly disposed used oil.
3.5 Legislative Support
A cursory view of the legislative instruments for
used oil management in Nigeria as reviewed by (Bamiro
& Osibanjo, 2004)indicated a generalized approach that
gives loopholes to would be offenders. Section (1) of
Regulation 5.1.9 of 1991 regulating pollution abatement
in industries and facilities in Nigeria stipulates that ‘No
oil in any form shall be discharged into public drain,
rivers, lakes, sea or underground injection without a
permit issued by an agency or organization designated by
the Government. Section 11 subsection (1) further stated
that collection, treatment, transportation and final disposal
of waste shall be the responsibility of the industry or
facility generating the waste(Bamiro & Osibanjo, 2004).
A loophole in this legislation is the non-
prohibition of waste disposal on landfill site. An
understandable point here is that most of the present solid
waste management in the country is based on disposal on
landfill sites which pose a health and safety risk to the
public. In addition, placing the responsibility of disposal
solely on the door-step of the facilities generating this
waste leaves room for disposal by burning that can result
in air pollution and threat to public safety. Hence any used
oil collection program will likely fail based on this one-
sided responsibility.
4. SIMULATION STUDIES FOR
EVALUATING THE PERFORMANCE
OF ENHANCED COLLECTION RATE
4.1 Methodology
In this simulation study, oil generation rate from
vehicle based on historical data from the works of
Appendix 1(Chukwu, Isa, Ojosu, & Olayande, 2015) and
Appendix 2 (Badmus, Osunleke, Fagbenle, & Oyewola,
2012). An average of six possibilities is used to predicting
vehicle growth rate, by considering a three year growth
rate (3.3 1% due to economic factors) against two year
decline rate (12.5 1.7 %) in every ten year cycle. In
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67
addition, we assume that used engine oil from every car
serviced after covering 5000 km journey yields two used
oil scenarios; 0.5 liters yield (scenario 1) and1 liter yield
(scenario 2). However, annual distance covered by an
average car in Nigeria had been estimated as 18,300 km
(Oke, 2012). Hence every car is expected to be serviced
about 4 times in a year with two likely scenarios defined
as;
Scenario 1; 0.5 liter of used oil per service to
give 2 liters of used oil per year.
Scenario 2;1 liter of used oil per service to give 4
liters of used oil per year
Collection rates of 30% had initially been
obtained by (Bamiro & Osibanjo, 2004). In this study,
simulation studies of the economic effect of improving the
collection rate to 40, 50, 60, 70, 80 and 90% will be
considered. This will be achieved by determining
quantities of re-refined oil in liters and obtaining the
equivalent amount of crude oil that will be required to
refine the same quantities of re-refined oil using the fact
that 42 gallons of crude oil is required to produce 2.37
liters of lubricating oil that one gallon of re-refined oil
will make (April & Powell, 1994).The economic benefit
has been shown by the number of barrels of crude oil that
would need to be purchased if the waste oil was not re-
refined.
4.2 Results and Discussions
The result of the estimated economic benefits as
shown in Table 1 and Table 2 was plotted against time. A
typical plotis shown in Figure 8 for scenario 1; an
identical plot was obtained for scenario 2, but is not
shown here.
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Table 1: Economic benefit from used oil re-refining from 30 to 50% collection rates
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Table 2: Economic benefits from used oil re-refining from 60 to 90% collection rates
A typical plot is shown in Figure 8 for scenario
1; an identical plot was obtained for scenario 2, but is not
shown here. An empirical relationship was obtained for
the economic benefit in terms of the amount of waste oil
drained per car per year (L), the collection rate of waste
oil as a decimal (i.e. 30% is 0.3) and the year (y), where y
≥ 2009.As seen in equation 1.
Equation 1
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Figure 8:A typical economic benefit curves for scenario 1 up to year 2050
Figure 9:Assessment of economic cost comparison for the two scenarios
Figure 9 indicates the economic benefit of
scenario 1 and scenario 2, between 30% and 90%
collection rate in both cases. The overlapping region
indicates at which percentage collections would be
equivalent for the different drain amounts suggested by
each scenario.
Hence, scenario 2 appeared to be the most
economically feasible options where 1 liter of used oil per
vehicle serviced is collected for processing. A limitation
to this study is technological advancement in engine oil
formulation that provides for longer engine oil drain
intervals in vehicles. Although the equation presented is
unable to link the number of barrels of oil required to a
specific year, it holds true for any number of vehicles,
therefore if a different model for the vehicle growth were
used the equation would still provide a value for the
economic benefit.
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5. CONCLUSIONS A successful used oil re-refining program is
imperative in view of the increasing demands of
petroleum products to power industrial machines and
internal combustion engines. Towards this end,
government assistance will be needed in making positive
societal impact for used oil re-refining program. The
result of this study elucidate economic benefits from used
oil re-refining in terms of reduction of imported
lubricating oil, conservation of oil resource, employment
generation, provide eco-friendly disposal of hazardous
waste and revenue generation. The result of this study
indicated the need to improve the present used oil
collection rates as a way of stimulating investment in used
oil re-refining in the country.
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APPENDIX 1
APPENDIX 2