1 Introduction

Plastics production has increased to a global value of 311 million tonnes (MT) since the 1930s, with a growth rate of about 4% [1]. However, plastic usage is necessary for everyday living, and without it, modern markets and shopping can become much intricate [1, 2]. Plastics are used daily in packaging wide assorted goods, drinks, food for easier transportation, footwear, clothing, telecommunications, transport, among other things [3]. This has resulted in large-scale production with its durability, lightweight, low manufacturing costs displacing the use of unconventional materials like ceramics, metals, woods, among other things [3]. The large-scale production and proliferation of plastics have become a global concern due to their polluting effects [4]. They are primarily unrecycled and end up either in the natural environment or landfills [1]. Some of these plastics also end up in marine habitats, tourist sites, freshwater, and natural terrestrial [3]. Due to their extensive disposal level in the marine or ocean, aquatic lives have been distorted, leading to their near extinction [3]. Reports indicate that about 700 aquatic lives, including seabirds, marine animals, fishes, among other things, could go extinct due to their incessant injuries by plastic waste [2]. This has been attributed to the entanglement, suffocation, infection, drowning, starvation, and ingestion of plastic waste [2].

Also, the burning of plastics in landfills and various homes unabatedly has increased global anthropogenic carbon footprints [3]. Africa is now the second most polluted continent in the world, with over 500 shipping containers of waste being imported every month [3]. The data available on 33 African countries indicate that the continent had imported about 172 Mt of plastic waste and polymers between 1990 and 2017, valued at $US 285 billion [4]. As compared to other African countries, Tunisia (7%), Morocco (9.6%), Algeria (11.3%), South Africa (11.7%), Nigeria (17%), and Egypt (18.7%) had the largest share of the importation [4]. In South Africa, for example, 90,000 tonnes to 250,000 tonnes of plastic entering the sea each year [3]. It is further estimated that the importation of plastics to the continent would likely double in the next five years, contributing to the rise in world’s temperature significantly [4]. World’s temperature is also projected to increase from 1.5 to 3 °C with a corresponding impact on food insecurity, water supply, inequality, and poverty [5].

Although plastic waste has been a bane on the environment, humans, aquatic animals, and increasing climatic conditions, its benefits cannot be overlooked. It is essential to argue that the material is highly resistant, lightweight, versatile, and cheap [3]. Thus, it gives a valuable position in providing several environmental benefits critical in reducing food waste and maintaining food safety and quality [6]. The trade-offs between plastics and a complete ban on plastic could be intricate and lead to a negative knock-on effect on the environment [6]. It is against this backdrop that this paper explores two eco-friendly techniques to transform plastic waste into valuable products in a sustainable environment.

Extant literature has explored eco-friendly techniques to transform plastic waste into valuable products in a sustainable environment; however, there is limited literature in the African context. First, ASCE, Elsevier, Google Scholar, and Web of Science were some databases that were employed to search for peer-reviewed publications, and the researchers selected publications written in English. Some of the keywords used were ‘production’, eco-friendly techniques’, ‘plastic’, and ‘plastic waste’. The Boolean operators including ‘AND’ and ‘OR’ were also used in the search. The timeframe of these publications was set to 2002 to 2021 to include recent papers for the publication and the relevant papers selected. The backward and forward snowballing which means using citations within publications and finding citations were also adopted.

The next section is as follows. Section 2 explores eco-friendly techniques to transform plastic waste into valuable products in a sustainable environment. Section 3 addresses the challenges and benefits of producing liquid fuels from plastic waste. Section 4 concludes the study with recommendations for future research.

2 Eco-friendly techniques to transform waste into valuable products in a sustainable environment

To comprehend the eco-friendly techniques to transform waste into valuable products in a sustainable environment, it is essential to understand the different plastics, waste management chain, and distribution components. This is pivotal in understanding the nature of the problem and executing the best mediations for decreasing plastic waste. Millions of plastics that can be recycled or reuse end up being improperly discarded [1]. The global production of plastics was only 2 million tonnes in the 1980s, but there has been an abysmal increase in plastic production, resulting in about 381 million tonnes of plastic production in 2015 [6]. This implies that the world has produced over 7.82 billion tonnes of plastic waste cumulatively from 1950 to 2015 [7]. In the 1980s, 100% of the plastic waste generation was totally discarded without being incinerated or recycled [6]. As technology advanced, several methods were discovered in properly disposing of these waste products [8]. By 2015, 55% of plastic waste was still being discarded, 25.50% incinerated, and only 19.50% recycled [6].

In Africa, the total production of plastic waste was estimated at 15.9 Mt, with 8 African countries playing critical roles in its production, with the highest productions from Nigeria (2.3 Mt), Egypt (4.0 Mt), and South Africa (9.0 Mt) [9]. For instance, South Africa began production of plastic in the 1970s and polypropylene in 1991 at an average of 120,000 t a year [10]. The average production then rose to 220,000 t at the end of 2001 [4]. Among the widely produced plastics, polyolefins, in other words, polyvinyl chloride (PVC), polypropylene (PP), polypropylene (PP), polystyrene (PS), low-density polyethene (LPDE), and high-density polyethene (HDPE) accounts for 50% of the overall plastic production [2]. These plastics have a broad spectrum of additives, including thermal stabilisers, slip compounds, antistatic agents, lubricants pigments, heat and light stabilisers, acid scavengers, antioxidants, flame retardants, and plasticisers [4]. Some of these additives have been classified as endocrine-disrupting chemicals [EDCs, e.g. Diethylhexylphthalate (DEHP) or bisphenol A], while others have been classified as toxic [11]. Some have also been noted as persistent organic pollutants (POPs), including short-chain chlorinated paraffin (SCCPs); hexabromocyclododecane (HBCD); hexabromobiphenyls (HBB); flame retardants polybrominated diphenyl ethers (PBDEs); fluorinated tensides, eg. Perfluorooctanoic acid (PFOA) [4].

Polyethene (LDPE and HDPE) has contributed to 7 Mt of waste polymers over the last decade because it is used for producing sachets [11]. For instance, in Ghana, 150,000 sachets are produced a day by larger companies, while 45,000 sachets are produced a day from small-scale sachet water companies [12]. Further, over 40 plastic manufacturing companies were set up by the close of 2006, producing approximately 26,000t of plastic [12], resulting in agricultural pollution in the country [13]. Also, in Nigeria, excessive littering in the country has been attributed to the country’s excessive production of sachet water [14]. Over 60 million sachets are consumed daily, while Lagos alone accounts for 1500 sachet water factories [14] with little to no deposit return policies on the sachets produced. The current production and importation of plastic waste are likely to negatively affect the continent if recycling channels are fully adopted and operationalised.

Further, the usage time of plastic distribution includes a noteworthy test of sustainability because of the short life utilisation of these plastic applications [6]. The most widely used application of plastic is in the packaging sector, which accounts for about 146 million tonnes of plastic production and usage [7]. This suggests that a dominant fraction of plastic use has less than a month life span and mostly ends up in streams, freshwater bodies, and the marine [1]. Presently, the predominant application of plastic waste is that 30.8% are sent to the landfill, 29.7% are being recycled, and 39.5% is energy recovery [2]. Particularly in Africa, there are hardly energy or thermal recovery from plastic waste, including cement kilns and incinerators, and almost all the plastic wastes end up at the dumping sites [4]. Even though there has been a massive reduction in sending plastic waste to landfills in developed countries, the situation is far from satisfactory and even worse in most developing countries, especially Africa.

The unconventional approach of processing plastic waste at incineration and landfill sites is no longer sustainable [5]. This is due to the high emissions of toxic gases, including carbon dioxide (CO2), into the atmosphere, thereby increasing global temperatures and climatic conditions [6]. As such, there has been intense pressure from climate change agencies like the United Nations Framework Convention for Climate Change (UNFCCC) and the Paris Agreement to find innovative ways of recycling these plastic wastes [7]. Various methods have been identified, including the conversion of polyolefin waste into a broad spectrum of valuable products lie clean fuels, naphtha (a combination of hydrocarbons), polymers, among other things. The potency of this innovative technology has the impetus to shrink the use of plastic waste globally while increasing the profits of recycling companies. The current urbanisation worldwide, especially in the global south where there is limited development, plastic waste could be used to construct roads, developing real estates, among others. This reduces the pressure on cement production, which currently also contributes to 10% of the world’s atmospheric carbon print [6]. Again, waste-pickers have played pivotal roles over the years to reduce plastic waste in the environment [15]. Waste pickers are self-employed, small-scale individuals commonly found in the city’s informal economy [16]. Waste is obtained for personal use or to sell to buy-back centers and/or higher-level dealers [17]. About 2% of the global population earns a living by gathering, sorting, using, and/or selling salvageable waste [15]. For instance, roughly 37,000 South Africans earn a living from picking plastic waste [17], having an impact in reducing plastic waste in the environment.

The world is faced with the rapid expansion of cities, with the most happening in the global south, especially in African countries [18]. The urbanisation of these cities into megacities is inexplicable with corresponding population explosion, and migration traffic keeps building up in those areas [19]. For example, in areas like Lagos, Mumbai, etc., several reports of massive traffic build-up sometimes last for several hours [18]. These developing megacities and urban centres are faced with huge levels of plastic pollution, with various governments failing to implement stringent measures to curb such situations [19]. In effect, there have been several reports of negative impact on the economies of these cities as well as countries [20]. Despite these challenges, the government cannot totally ban plastic due to its environmental benefits and the trade-offs between plastics and a complete ban of plastic, leading to a negative knock-on effect on the environment [6]. As such, plastic waste could be utilised to construct roads to expand road infrastructure in these centres as urbanisation is inevitable.

The application of plastic waste has also been considered in the construction of roads and road surfacing globally, especially in the global south, where road infrastructure is limited [18]. These materials are used to prevent a double tragedy of limited asphalt roads and limited resources (like sand, gravels, among others) in road construction [21]. Utilising polymer-modified bitumen to achieve better asphalt roads has also been considered for a long time [18]. Thus, while increasing the construction of roads around the world with plastic waste, the rampant use of natural materials, including sand and gravel for asphalt roads which are exhaustive, is also reduced [20]. Waste plastics of various forms have been used as modifiers in pavement materials [21]. According to statistics, three types of waste plastics were most commonly used by researchers: PET, PE, and PP [22,23,24,25,26]. Thus, PET, PE, and PP have been found to have excellent binding properties and softens when subjected to heat between 100 and 160 °C [18, 22]. Extant literature indicated that the melting temperatures of PP, PET and HDPE were 135 °C, 160 °C, and 165 °C, respectively [18,19,20,21,22,23]. Particularly PET absorbs some oil and releases a low molecular weight fraction (5 to 10% by weight) into bitumen which increases the velocity of bitumen-plastic composite (BPM) [25]. This makes it highly blendable with bitumen for the construction of roads [23]. On the other hand, heating plastic waste above 270 °C tends to decompose, and 750 °C tends to release noxious gases [22].

The strength of asphalt to withstand shearing deformation is measured in viscosity [21, 22]. If the viscosity is too high, the binder may struggle to flow to cover the aggregates [21]. Thus modifying and controlling the viscosity of polymer-based asphalt is also important [22]. The viscosity of virgin binders is generally increased when waste plastics are added. When HDPE and PP are added, however, viscosity reduces until the HDPE and PP concentrations exceed 2.5% [18]. This may be demonstrated by the thixotropic effect, and the thixotropic effect of polymer modified asphalt may be attributed to the reversible structure breakdown that is typical in polymer modified bitumen multiphase systems [18]. The physical and chemical qualities of recycled materials are closely related to their properties [21]. The porous mortar covering on the floor, for example, gives Recycled Concrete Aggregates (RCAs) their high absorbency and low abrasion resistance [23]. As a result, thoroughly comprehending the physical and chemical characteristics of recycled products would aid in developing disposal procedures and the analysis of test results. When it comes to waste polymer components, the interfacial character and blend properties are also crucial. The surface state of polymers is significantly altered by electron irradiation and trans-polyoctenamer (TOR), and understanding polymers in terms of molecular structure and functional groups are important [25].

Research again shows that combining PP and BPM are less susceptible to temperatures and fatigue, improved pavement performance, and better rutting resistance when used for road construction than other forms of plastic wastes [22]. Also, bitumen could be blended with polymer-coated aggregate for better stripping value and higher Marshall Value, which is also more suitable for road construction [23]. For instance, plastic waste like thermocole, cups, films, and disposed carry bags have been used to construct about 1500 km of roads in Maharashtra, India, which has been able to withstand high temperatures, rain, and heavy traffic [20]. For every tonne of waste plastic used in the construction of one km road, it is estimated that about 3 tonnes/km of carbon emissions are reduced in the atmosphere in India [20]. Also, plastic waste is being used in countries like South Africa, Ethiopia, the Netherlands, the United States, Australia, and the UK to construct roads [19]. The UK government also announced a £23 million investment in plastic roads in eight local authorities [19]. NelPlast Ghana Limited also makes pavements from plastic waste approved by the Ministry of Environment, Science, Technology, and Innovation in Ghana [18]. As depicted in Fig. 1 is a pavement block made of plastic waste in Ghana.

Fig. 1
figure 1

(Source: Quartz Africa)

Pavement block made of plastic waste

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Urbanisation has further resulted in an unprecedented rate of housing deficit globally and, therefore, the need for affordable housing units [27]. The cause has been attributed to several factors, including; the high rising cost of housing units against income, high demand against supply, population growth, and scarcity of land, among others [28]. Plastic waste has been considered as a better alternative for the construction of housing units [29]. Most of the extant research has been conducted in most developing countries with high population growth rate [27, 29]. Population growth has become acute and quite natural in recent times, leading to urbanisation. This has pushed urban centres into sub-urban centres and mostly leading to improper settlements or slums [27]. A considerable amount of plastic waste is generated every day in these areas, having negative repercussions on municipal development [30]. The rampant growth in these urban centres has been attributed to land unavailability and huge housing costs in urban centres, thereby pushing these settlements into sub-urban areas resulting in improper settlements [30].

Real estate developers have purchased further land in urban centres to build luxurious buildings for the bourgeoisie and high-income earners in society [29]. This leads to a knock-off effect on the low-income earners forced into peri-urban centres and subsequently into slums [27]. With massive levels of pollution mostly attributed to improper plastic waste disposal, municipal and government policies are centred on reducing plastic waste in these areas [28]. Thus various recycling policies, especially where sorting of plastic waste is evident, these waste are converted into concrete blocks, asphalt for paving roads, among others [31]. Bricks used for housing units consist of 70% plastic waste which offers an absolute strength as opposed to laterite stones and requires less water than stone [31]. This also offers an opportunity to limit water usage in times of water crisis to increase the elasticity of water supply for domestic purposes. With the current exorbitant cost of housing units globally, the use of plastic waste for affordable housing units offers 48% cheaper prices than laterite housing units [27] (Fig. 2).

Fig. 2
figure 2

Source: (African Globe)

Affordable Housing unit made of pet bottles and plastic waste in Nigeria [82]

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Figure 3 shows the proposed process for the valorisation of plastic waste into affordable housing units. Firstly, plastic waste hubs must be identified and subsequently collected. Some of these sites include landfills, rivers, oceans, among others. The next process is for the collected waste to be sorted out into PP, LPDE, HPDE, and polyethene. Some of these plastic waste have better stripping value and higher Marshall Value which could bind easily with bitumen and polymer-coated aggregate. Also, some of these plastic waste are less susceptible to temperatures and fatigue with improved performances and better rutting resistance, especially PP. After these plastics are sorted out, the next stage is to valorise the plastic into building blocks. These valorised plastics are then transported to construction sites for constructing affordable housing units.

Fig. 3
figure 3

Proposed process of valorisation of plastic waste into affordable housing units

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2.1 Plastic waste valorisation into fuels

Plastic waste valorisation into fuels is essential in reducing plastic pollution globally [32]. Several alternatives to valorising plastic waste have been suggested, right from primary routes of directly recycling to quaternary routes of valorising plastics to energy [33]. The process entails converting polyolefin into valuable products, including clean fuels, naphtha (a combination of hydrocarbons), and polymers [34]. A wide range of strategies adopted include (i) gasification of plastic waste, which deals with the production of gaseous streams for energy or synthesis, (ii) pyrolysis for the production of H2 or specific pyrolysis processes, and (iii) integration of plastic derived products or plastics into refinery units [2]. There are also other forms of recycling plastic waste, but due to their inefficient nature, when there are complexities, they fail to utilise the forms or types of plastics [33]. These include the primary recycling of plastic solid waste (PSW) and mechanical recycling [34].

Mechanical recycling of plastics occurs when plastic manufacturing companies recover PSW through mechanical means, which can be done for single polymers like PS, PP, and PE [35]. The contaminated and intricate the waste is that the less it could be recycled via the mechanical process, which is most ubiquitous in African countries than in developed nations [36]. This recycling method is more ubiquitous in most African countries than in developed countries [34] compared to the chemical processes. Since the chemical process has eluded most governments in reducing recycling waste, this paper discusses them as the most efficient ways to be considered by various governments on the continent to curb the high rate of plastic pollution [37, 38]. Again, there are little to no deposit policies on the continent, and therefore this process can be considered as a more efficient way to reduce plastic waste in the environment [39]. Chemical recycling [37, 38, 40, 41] plays a major role in transiting circular economies and compounds like hydrocarbons and closed-loop recycling materials [40, 41]. These systems allow for the elimination of toxic substances and, as a result, the management of difficult waste streams [38]. Chemical producers must commit to using raw materials from secondary sources to create safe, cost-effective, and viable chemical recycling supply chains [38].

Extant literature conducted on pyrolysis of plastics shows that there are four main strategies of producing fuels from plastic waste, including H2 production [42,43,44,45,46,47], gasification aimed at producing gaseous steam for synthesis or energy [48,49,50,51,52,53], integrating plastic wastes or plastic-derived products in refinery units [54,55,56], and developing specific pyrolysis process [57,58,59,60,61,62,63,64,65,66]. Based on these plethoras of literature, the findings showed that the pyrolysis process yielded a larger volume of liquid oil, of up to 80 wt% and with a moderate temperature of 500°C.

Many researchers choose pyrolysis because it can yield a large volume of liquid oil, up to 80 wt%, at a moderate temperature of 500 °C. The liquid oil produced can be used in various applications, including diesel engines, boilers, and furnaces, without further treatment or upgrading [64]. There are different compositions for plastics, which are usually stated in terms of their proximate analysis [2]. Proximate analysis is a method for determining the chemical properties of a plastic compound using four specific elements, including ash content, volatile matter, fixed carbon and moisture content, fixed carbon [63]. Findings show that the main factors that affect the liquid oil yield in the pyrolysis process are ash content and volatile matter [62]. Thus, the research showed that high volatile matter favored liquid oil production, while high ash content reduced liquid oil production, increasing gaseous yield and char formation as a result [61,62,63,64,65]. The volatile matter content of all plastics was found to be very high, while the ash content was found to be very low [62]. These properties mean that plastics have a high propensity for pyrolysis to contain significant amounts of liquid oil [61, 63, 65].

Using a fixed-bed reactor at 500 °C, liquid oil is generated using PET in the pyrolysis process [67, 68]. In this experiment, the heating rate was 10 C/min, and the sweeping gas was nitrogen gas. The liquid oil yield was found to be lower than the gaseous product. The liquid oil yielded was 23.1 wt%, while the gaseous substance yielded 76.9%, leaving no stable trace. The low liquid yield revealed that PET has a comparatively low volatile content of about 86.83%, compared to other plastics with volatile contents of over 90% [67]. Unfortunately, the gas chromatography results–mass spectroscopy (GC–MS) study revealed that 49.93% of the oil contained benzoic acid. In another study, the liquid oil obtained was slightly higher than the previous study, with a liquid yield of 39.89 wt%, a gaseous yield of 52.13 wt%, and a solid residue of 8.98 wt% [69]. Therefore liquid oils obtained from PET ranges between 23–40 wt% and gaseous yield between 52–77 wt% [70].

HDPE also produces high levels of oil during pyrolysis at different operating parameters [61]. HDPE was refined into liquid oil using a pyrolysis temperature of 300–400 C and a heating rate of 5–10 C/min, with nitrogen gas as the fluidizing medium [71]. According to the experiment, the largest cumulative conversion of HDPE occurred at 350 C, with a liquid yield of 80.88 wt%. The solid residue was very high at 300 °C with 33.05 wt%, but it was reduced to 0.54 wt% at the maximum temperature of 400 °C. Another experiment using a semi-batch reactor at a higher temperature range of 400–550 °C yielded liquid oil of 79.08wt% and gaseous product of 24.75 wt% at 550 C, while wax dominated the product fraction at temperatures of 500–550 °C. Pyrolysis yielded a dark brownish oil with no visible trace and a boiling point of 82 to 352 °C. This indicated that the oil contained various oil components, such as diesel, kerosene, and gasoline, which suited the properties of conventional petroleum. The sulfur content of the HDPE pyrolytic oil was very low at 0.019%, making it environmentally friendly. Marcilla et al. [72] used a batch reactor to study HDPE pyrolysis at 550 °C and yielded liquid oil of 84.7 wt% and a gaseous product of 16.3 wt%. But when Mastral et al. [73] increased the temperature to 650 °C in the fluidized bed reactor, it was discovered that 68.5 wt% liquid oil was produced and 31.5 wt% gaseous substance was produced. This suggests that when temperatures are increased above 550 °C, oil yields decrease.

Experiments have also been conducted on LDPE pyrolysis in a fixed-bed reactor at 500 °C and a heat rate of 10 °C/m [74]. It lasted for 20 min, and nitrogen was used as the fluidizing gas. It was discovered that a high liquid yield of 95 wt% was achieved with a low gas yield and no char. Marcilla et al. [72] also achieved a high liquid oil yield of 93.1 wt% when it was carried out in a batch reactor at 550 °C, but with a lower heating rate of 5 C/min. Again, at lower temperatures of 430 °C, Sharuddin et al. [61] obtained an oil yield of 75.6 wt% and Aguado et al. [75] with an oil yield of 74.7 wt%. In another experiment, the pressure in the batch reactor was decreased to between 0.8 and 4.3 MPa in the pyrolysis process with temperature at 450 °C, and the results showed an oil yield of 89.5% liquid oil, 10wt% gaseous, and 0.5 wt% char [76]. This suggests that pressure has an effect on the pyrolysis of oil products.

PP pyrolysis was carried out in a micro steel reactor at temperatures ranging from 250 to 400 °C which yielded liquid oil of 69.82 wt% occurring at 300 °C and a cumulative conversion of 98.66% [71]. The rise in temperature to 400 °C only decreased overall substance conversion to 94.3% and increased solid residue from 1.34 to 5.7 wt% [71], implying that coke formation took over at higher temperatures. However, PP pyrolysis was investigated at a higher temperature of 380 °C in another experiment [61]. They discovered a higher liquid yield of 80.1 wt%, 6.6 wt% gaseous residue, and 13.3 wt% solid residue. When temperatures was increased further by Fakhrhoseini and Dastanian [70] a higher liquid yield of around 82.12 wt% was obtained but increasing temperatures above 500 °C only decreased the liquid yield obtained [77]. This was seen in the experiment of Demirbas [77], who obtained liquid oil at carried out 48.8 wt%, 49.6 wt% gaseous yield, and 1.6 wt% char at an intense temperature of 740 °C.

PS pyrolysis was carried out in a batch pressurized autoclave reactor at 300–500 °C for one hour at a heat rate of 10 C/min and an experimental pressure of 0.31 MPa to 1.6 MPa [76]. It was discovered that at the optimum temperature of 425 °C, PS pyrolysis provided a very high liquid oil yield of about 97.0 wt%, and just 2.5 wt% of the gas was extracted at its limit. Another trial, which used a fluidized bed reactor at a temperature of 450–700 °C, showed a high yield of liquid oil product [78]. At 600 °C, the maximum liquid oil yielded was 98.7wt%. At a lower temperature of 450 °C, the liquid oil produced was still considered high, at 97.6 wt%, with a difference of 1.1 wt%. When energy conservation was a top priority, a lower temperature was preferred because it would save cost on energy. According to a study conducted, when the PS pyrolysis was run at 581 °C in a batch reactor, the liquid oil was decreased to 89.5 wt% [76]. As a result, running the PS pyrolysis at temperatures higher than 500 °C is not recommended to maximize liquid oil yield.

In most African countries where plastic waste is not separated right from production, distribution to consumption creates heterogeneous resins making separation and recycling plastic waste difficult. Therefore, there is the need to also assess past literature on mixed plastics and the level of oil or fuel they produce. Pyrolysis of mixed plastic waste obtained from German homes, which contains roughly 75% PE, PP, and 25% PS was used for the experiment [79]. Following the addition of chlorine, a small PVC volume of 1wt% was discovered. The experiment was then carried out in a fluidized bed reactor at a temperature of 730 °C, yielding 48.4 wt% liquid oil. The amount of liquid oil obtained was very close to that obtained by Demirbas [77] in pyrolysis of PPs, PE and PS mixture collected from landfill, which was about 46.6 wt%. The solid and yields, respectively, were estimated to be 2.2 wt% and 35 wt%. The residual PVC in the material resulted in 4 ppm chlorine in the oil, which resulted from the remaining PVC, but the detection of 4 ppm chlorine in oil does not distort the quality of fuels since the maximum amount of chlorine found is fuels are mostly around 10 ppm. In a bubbling fluidized bed reactor, pyrolysis of mixed plastics containing 24wt% PP, 30 wt% HDPE, and 75 wt% LDPE was also investigated at high temperatures of 650 °C and 730 °C [80]. The findings revealed a higher liquid oil content of 48wt% at temperatures below 650 °C. Heavy fractions such as carbon black, wax, and heavy oil made up 52% of the oil fraction. At temperatures of 730 °C, however, 70% of the light fraction of liquid found in the pyrolysis oil was formed, with 44 wt% suggesting a lighter hydrocarbon liquid and gaseous with higher temperatures. From these findings on the valorisation of plastics into fuels, mixed plastics produced lower levels of liquid oil or fuels as compared to single plastics.

For optimum utilisation of these processes, the value chain of plastic waste needs to be segregated into homogeneous plastics to achieve efficient processing of the recycled plastic waste from the production stage to the consumption stage. This would ensure that plastics are separated, monitored, and sorted to produce suitable feeds. Apart from the pyrolysis of plastic wastes into liquid or wax products, it can also generate hydrocarbon-rich gases depending on the conditions, feed, and a heating value of 25–45 MJ/kg [57] appropriate for energy recovery. These hydrocarbons from liquid and wax products make them ideal raw materials for the refinery. Although the product's scalability is minimal compared to crude oil, its conceptual proof of serving as raw materials for the refinery is validated.

3 Benefits and challenges of producing liquid fuels from plastic waste

Pyrolysis, unlike recycling, does not pollute water and is called a green technology because the gaseous pyrolysis byproduct has sufficient calorific value to be reused to offset the pyrolysis plant's total energy demand [76]. Since it does not require an expensive sorting waste, handling is also much simpler and more versatile than traditional recycling methods [70]. The process adds value and increases the revenue of refinery units and companies involved in the valorisation of plastic waste into liquid fuels [74, 81]. Also, plastic waste dissolves in the solvent, increasing its bulk density, reducing the amount of plastic waste prior to the process [57]. Separation of mixed plastic into separate parts is thought to be critical since pyrolysis of single types of plastic is frequently stated to be higher than that of mixed plastic [78,79,80]. Therefore, using selective dissolution makes it possible to divide mixed plastic waste into its constituent parts. This is likely since some plastics can only melt in specific solvents at specific temperatures, which is alternative to manually separating plastic waste, which requires more time than mechanical separation (for instance, certain HDPE bottles with plastic labels or caps) are made of LDPE) [77, 80].

A challenge identified is that the valorisation process produces liquid fuels on a smaller scale and requires intricate post-processing to meet commercial fuel requirements. The previous experiments suggest that the valorisation of plastic waste requires highly skilled personnel and high levels of technologies in ensuring a cleaner waste polymer. Thus, catalyst poising may occur without these necessary factors, which could be highly poisonous to the environment. Again, the findings suggest that the composition in the feed and the variable quality is a challenge in producing liquid fuels from plastic waste. Thus, other plastics like large amounts of PVC and other inorganics could affect the composition feed and the quality of fuels produced. As earlier noted, the chlorine substance of more than 10 ppm falls below the required level of chlorine in fuels and even in petrochemical fuels, and as such, with a large amount of PVC in the composition feed could reduce the quality of the fuel produced. Onwudili et al. [76] also identified that plastic waste requires pretreatment before being used in feeds to produce fuels or oils. The high volatile nature of these plastics requires dissolution to ensure that the volarisation process is done at a higher safety measure [78, 79]. The kinetic models and reaction data are inadequate due to limited research on them leading to several problems during the design of reactors [74, 75, 77,78,79,80].

4 Conclusion and recommendations

In conclusion, the paper explored eco-friendly techniques to transform plastic waste into valuable products in a sustainable environment. The trade-offs of using plastic waste for road construction and as a component in cementitious composites were discussed. Further, the challenges and benefits of producing liquid fuels from plastic waste were also addressed. It was discovered that the conversion of polyolefin waste into a broad spectrum of valuable products lie clean fuels, naphtha (a combination of hydrocarbons), polymers, among other things. Thus the potency of this innovative technology has the impetus to reduce plastic waste on the African continent and increase the profits of refinery and recycling companies. It was also found that hand pickers play a major role in reducing plastics in Africa and provides an income-generating job for waste pickers. More so, the current urbanization level in Africa with high traffic congestions offers government and real estate developers to construct roads and buildings cementitious products made of plastic waste. Again it was observed that mixed plastics produced lower levels of liquid oils or fuels as compared to single plastics. Although the product’s scalability is minimal compared to crude oil, its conceptual proof of serving as raw materials for the refinery is validated. Therefore, recycling plastic waste to liquid end-products was a sustainable way of helping the environment with beneficial economic impact on the African continent.

The study recommends the following:

  • There is a need for governments in Africa to implement policies on deposits of plastics at designated centres.

  • Considering the rate of plastic waste importation on the continent, there is the need to impose huge taxes on imported plastic waste to reduce its proliferation.

  • There is a need to ban single-use of plastics on the continent.

  • Implement novel technologies in recycling waste into reusable products and fuels.

  • Affordable housing units should be constructed with plastic waste to reduce the housing deficit and reduce the enormous financial burden in providing these facilities by the government.

  • Valorisation of fuels produces smaller-scale fuels compared to crude oils and therefore there is the need to integrate plastic waste polyolefins in refinery units to produce larger amounts of fuels.