Tyre Waste And Associated Problems Environmental Sciences Essay

The landfilling of Surs occurs when no recovery methods are possible and when the Surs are in deficient status to be recycled. Landfilling of Surs is a hapless disposal solution as Surs are about wholly non-biodegradable due to the cross-linked gum elastic construction nowadays. If managed right, waste Surs do non present a important environmental or wellness menace. However, this is frequently non the instance, with illegal dumping and abuse. In fact, waste Surs are non classified as a jeopardy harmonizing to the EU ( Hylands & A ; Shulman, 2003 ) . Globally, Surs are disposed by dumping in landfill sites, either lawfully or illicitly. It is a consequence of the possible environmental jobs posed by Surs that the 1999 EU directive on landfill waste banned the disposal of whole Surs in landfill sites ( European Commission, 1999 ) .

The disposal of Surs in landfill sites creates instability in the shit as Surs tend to lift to the surface ( The Environment Agency, 1998 ) . This causes jobs for future usage of the landfill site as land renewal. The volume of the infinite a Sur takes up is chiefly air due to its natural construction ; 75 % of the volume is null infinite. This consequences in air being trapped when whole Surs are buried in landfill sites. Surs hence occupy a big volume in landfill sites and this infinite is better served for other waste stuff ( United States Fire Administration & A ; Federal Emergency Management Agency, 1998 ) . In order to cut down this volume, Surs are shredded before they are piled. Furthermore, as Surs have a high energy content, landfilling is a waste of this stored energy. Landfilling besides consequences in energy recovery non being possible as Surs are buried with other wastes in landfill sites. These factors have contributed to the forbiddance of whole Surs from landfill since 2003, with chopped Surs banned since 2006 ( European Commission, 1999 ) .

As a consequence of this prohibition, waste Surs are now stockpiled in monofill sites, which are particular sites merely for the disposal of Surs, either endlessly or until a usage can be found for them e.g. TDF, Pyrolysis etc. ( Rubber Manufacturers Association, 2009 ) . Monofill consequences in big sums of Surs piled together in one topographic point. An estimated 4 billion Surs are in landfilled, monofilled and stockpiled around the universe ( World Business Council for Sustainable Development, 2008 ) . Tyre piles show a important fire jeopardy. If big sums of tyres catch fire, a important environmental job arises. In the instance of whole Surs, big volumes of air are trapped and it becomes hard to cut off the supply of O. This, combined with the big surface country of a whole Sur, enables the Sur to go susceptible to combustion if a fire is initiated by an external input ( Integrated Waste Management Board, 2002 ) . Whole Surs are non easy to light as they are designed to be heat immune in operation and a temperature of over 350A°C must be maintained during combustion ( Federal Emergency Management Agency & A ; United States Fire Administration, 1998 ; Hylands & A ; Shulman, 2003 ) . Often, with whole Sur heap fires, the beginning of the fire is questionable and is normally the consequence of arsonist action or unnatural conditions conditions. Shredded Sur hemorrhoids have a lower hazard of catching fire as they have less air infinite and can be extinguished more easy. However, due to their much greater surface country and permeableness to air flow, chopped Surs frequently spontaneously combust, which is a major job ( Health and Safety Executive, 2012 ) .

These fires are a peculiar nuisance as they are hard to snuff out and besides produce a big sum of fume. The fume can be toxic as it is normally really heavy and oily ( Hylands & A ; Shulman, 2003 ) . When Surs burn, emanations such as polyaromatic hydrocarbons, C monoxide, sulfur dioxide, oxides of N and hydrochloric acid are produced ; most of which are pollutants ( US EPA, 1991 ) . In 1999, a Sur fire broke out in Westley, California due to a lightning work stoppage. The US Environmental Protection Agency took over 30 yearss to snuff out the fire and incurred costs of $ 3.5 million in the procedure. When tyres combust, they break down into oil, gas and metal ( US EPA, 2012c ) . It is estimated that the mean auto Sur produces two gallons of oil as a consequence of burning. Oil and gas are extremely combustible and hence AIDSs the fire, which is the ground why Sur fires are hard to snuff out. As a consequence of the fire, the oil and surface H2O can be absorbed into the land on which the Sur heap was situated. This can be a important pollutant as this overflow can pollute land H2O and pollute Wellss ( US EPA, 2012c ; Federal Emergency Management Agency & A ; United States Fire Administration, 1998 ) .

Whole Surs in out-of-door reserves present a possible human wellness jeopardy. Due to the form of the Surs, H2O can roll up and settle in them. In tropical states, standing H2O provides engendering evidences for mosquitoes, which are major bearers of diseases such as malaria ( US EPA & A ; OSWER, 2012b ) .

Harmonizing to Leff, McNamara & A ; Leff ( 2007 ) , monofill sites are specially built by unearthing an country and put ining an impermeable line drive and leachate aggregation system in order to forestall gathered H2O in the Surs from come ining the dirt and polluting the groundwater. The leachate H2O is directed to the nearest natural organic structure of H2O. However, for landfill sites, the Surs can come into direct contact with the dirt and leachates may come in the dirt ( Leff, McNamara & A ; Leff, 2007 ) . Research is presently being conducted to understand the consequence that these leachates may hold on groundwater. The chief concern is possible Zn leachates. The environmental impact of these substances is still unknown ( US EPA, 1991 ) .

These factors provide a instance for the reuse and recycle of ELTs instead than dumping in landfill and monofill sites. Globally, there is a push towards recycling, but some parts have greater installations for stuff and energy recovery than others. This means that some states still have big sums of Surs in landfill and reserves.

End-of-Life Uses

If beginning decrease steps are non possible and Numberss of Surs in reserves need to be reduced, assorted end-of-life utilizations can be considered for ELTs. These utilizations can be split into three chief countries ( Sienkiewicz, Kucinska-Lipka, Janik, et al. , 2012 ; World Business Council for Sustainable Development, 2008 ) :

Energy Recovery

Material Recovery


The per centum split of finishs of ELTs is shown below in Fig.6. It can be seen that the major method of recycling ELTs is through material recovery, as there are many possibilities to recycle ELTs via this method. It is of import to distinguish between material recovery and recycling ; material recovery requires the processing of the Sur before usage, whereas recycling is the usage of the whole Sur. There is frequently a important crossing over in the applications of stuffs from material recovery and recycling. For this ground, their applications will be considered together in the same subdivision.

Figure: Percentage portion of ELT finishs ( SIGNUS, 2010 )

Energy Recovery

Surs have a high sum of energy stored within them ; they have a calorific value of 31,400 kJ/kg ( Pipilikaki, Katsioti, Papageorgiou, et al. , 2005 ) . This is greater than that of coal, which allows ELTs to be considered as a beginning of fuel, in order to retrieve that energy. Table 4 shows a comparing of different fuels and their energies. It can besides be seen that tyres produce less CO2 emanations as a fuel than natural gas and coal.

Table: Energy content and CO2 emanations from fuels ( World Business Council for Sustainable Development, 2008 )


Energy ( Gigajoule/tonne )












Pet coke




Diesel oil




Natural gas








The usage of Surs as fuel is known as Tyre Derived Fuel ( TDF ) . TDF involves foremost tear uping the Surs and burning them in order to pull out their energy ( Sienkiewicz, Kucinska-Lipka, Janik, et al. , 2012 ) . TDF is used in a figure of industrial applications, for illustration in cement workss. The major applications for which TDF are used is shown in Fig.7.

Figure: Applications of TDF ( Rubber Manufacturers Association, 2009 )

The major usage of TDF used to be for cement kilns and in Europe, it remains an of import application ( Rubber Manufacturers Association, 2009 ; Pipilikaki, Katsioti, Papageorgiou, et al. , 2005 ) . In cement kilns, the Surs are used both as a whole and chopped and are normally co-combusted with coal ( Sienkiewicz, Kucinska-Lipka, Janik, et al. , 2012 ) . Using whole Surs is normally more good from an economic point of position as no pre-processing is required and in certain states, there are fiscal inducements to be gained by cement workss by utilizing whole Surs. However, within a whole Sur, there are stuffs such as steel and fabrics which do non fire good and can curtail the energy end product from burning. The Surs are burned at high temperatures of 1430C for long periods ( Pipilikaki, Katsioti, Papageorgiou, et al. , 2005 ) . The emanations produced from this procedure are minimum. Normally, in cement production, due to the big sums of Ca carbonate used, sulphur emanations from the combustion of coal are controlled. Using TDF, nevertheless, consequences in even lower sulfur emanations due the lower degrees of sulfur in Surs than coal ( Pipilikaki, Katsioti, Papageorgiou, et al. , 2005 ) . Globally, there is a thrust towards cut downing N oxide emanations ( NOx ) . In the US, federal and province Torahs force cement workss to cut down their NOx emanations. Using TDF helps to cut down these emanations ; hence, the usage of TDF is popular ( Rubber Manufacturers Association, 2009 ) . The ash, carbon black and steel from the combustion of the Surs are deposited in the kiln after firing and these merchandises can permanently bond with the cinder, which is the solid that forms the footing of cement. This does non impact the cement well, other than somewhat increased scene times ( Sienkiewicz, Kucinska-Lipka, Janik, et al. , 2012 ) . In fact, usually press ore is during the production procedure, but in this instance, the steel belts and beads can be used as a partial replacement. This reduces the cost, by cut downing the sum of Fe ore used. Using TDF is a cost effectual method of alternate fuel for cement kilns. ELTs can be obtained at low cost from reserves, which besides reduces the figure of stockpiled Surs ( Pipilikaki, Katsioti, Papageorgiou, et al. , 2005 ) .

Pulp and paper Millss are presently the major user of TDF in the US. Harmonizing to ( Rubber Manufacturers Association, 2009 ) , in 2007, “ there were 32 mush and paper factory boilers devouring 1066.9 1000 dozenss of bit Surs ” . This was about a 100 % addition from 2005. This was due to the lifting costs of energy. In mush and paper Millss, Surs are used in their chopped signifier, as french friess. The energy for these Millss is normally supplied via the combustion of wood waste. However, wood waste has changing belongingss, such as different wet contents and heat capacities. For this ground, the Millss use extra fuel beginnings to supplement the wood in order to guarantee dependability. TDF is used here due to its high heat capacity and low wet content ( US EPA, 2012a ) . In this application, it is of import that the TDF french friess are of good quality. This is because the size of the bit and the sum of residuary steel can greatly impact its public presentation. The optimum solution is with the smallest bit and lowest sum of steel as the steel can lodge to the furnace and impact its public presentation ( Blumenthal, 1996 ) . The usage of TDF is dependent on the cost of other fuels with regard to Surs.

TDF is besides used for industrial boilers and electric public-service corporation boilers. Some industrial workss use TDF as a auxiliary fuel beginning in chopped signifier. Here, the steel belts and beads must be removed before burning ; failure to make so can ensue in disposal jobs of the comburent ash ( US EPA, 2012a ) . TDF is besides used as fuel for electric public-service corporation boilers as a replacing for coal. TDF is preferred here due to its higher energy content and lower emanations. Specifically, TDF is burned in cyclone boilers, due to the fact that no alterations are required, therefore extinguishing start-up costs. Tyre french friess are used of size 1 ” ten 1 ” with metal removed, which means that there is a significant cost for the shredding and film editing of the whole Surs. However, in Stoker fired boilers, larger Sur pieces can be used which reduces the cost of pre-processing ( US EPA, 2012a ) .

In 1998, there were three dedicated tyre-to-energy workss in the US ( Rubber Manufacturers Association, 2009 ) , nevertheless in 2007, merely one works in Connecticut remains. This works uses 10-11 million Surs per twelvemonth. The ground for this lessening was attributed to the stoping of the Illinois Retail Rate Law, which had provided fiscal inducements for electricity coevals via alternate fuel beginnings ( Rubber Manufacturers Association, 2009 ) .

Harmonizing to the Rubber Manufacturers Association ( 2009 ) , the motive for utilizing TDF is about ever economical and tendencies depend on the cost of energy beginnings at that minute in clip. Due to lifting fuel costs, the usage of TDF in industry is going more prevailing. However, the environmental impact of TDF is still ill-defined. Governmental paperss frequently recommend the usage of TDF without adverting possible toxicity degrees. Studies conducted have indicated increased degrees of dioxins and furans in flue gases produced by workss utilizing TDF, as opposed to char. Dioxins and furans are toxic chemicals produced by firing Cl in the presence of hydrocarbons and O. Dioxins and furans are produced when TDF is burned as Surs contain Cl due the presence of man-made gum elastic. These chemicals present a serious wellness menace as they can do unwellnesss such as malignant neoplastic disease and bring on sexual wellness jobs. The World Health Organisation states that certain dioxin signifiers are considered to be extremely carcinogenic and even a really little measure can be unsafe. The Cl content of Surs is listed as being 0.149-0.150 % by weight harmonizing to the Rubber Manufacturers Association, which is greater than that of coal ( Energy Justice Network, 2012 ) . This indicates that there is a possible wellness hazard associated with the usage of TDF. Currently, research suggests that this hazard is low and manageable ( Kirk, 2000 ) , but as the usage of TDF additions, this decision may necessitate to be reassessed.

Material Recovery and Recycling

Globally, this is the chief signifier of ELT recycling, as there are many options available. Material recovery involves the processing of ELTs, either to recover material resources or to utilize the Surs in a new signifier. Material recovery can be split into regenerative procedures, such as pyrolysis, and material recycling. The different degrees of recovery are outlined in Fig. 10.

From this diagram, it can be seen that there degrees are split harmonizing to the sum of processing required ( Hylands & A ; Shulman, 2003 ) . Level 1 describes the “ devastation of the Sur construction ” , which involves the film editing of the ELTs and the associated applications in this signifier. Level 2 describes further polish of the Level 1 processing by dividing the elements of the Sur and farther decrease in size. This involves the shredding of the Surs into french friess and granulates. Level 3 categorises the stuff intervention processes to degrade the tyre stuff, with Level 4 depicting farther intervention procedures.

Figure: Degrees of consumer Sur recovery ( Hylands & A ; Shulman, 2003 )

Regenerative Procedures

Regenerative procedures can be described as procedures in which the Surs are chemically or thermally reacted to interrupt down the construction and composing so that the stuffs can be used for farther intents. These include pyrolysis, devulcanisation and gasification. Pyrolysis is the chief procedure presently being used, whereas the other procedures are either in development or are mostly unviable at present ( Yang, 1993 ; Sienkiewicz, Kucinska-Lipka, Janik, et al. , 2012 ) .

Pyrolysis is the procedure whereby a Sur is thermally degraded in the absence of O ( The Environment Agency, 1998 ) . The elastomers in the gum elastic decompose when they are heated to temperatures between 400 and 700C, with no O nowadays. This takes topographic point in pyrolytic furnaces which operate at different force per unit areas, depending on the type of furnace. A impersonal gas is used for the pyrolysis, normally nitrogen ( Sienkiewicz, Kucinska-Lipka, Janik, et al. , 2012 ) . From this procedure, merchandises of lower molecular weight are obtained, such as oils, gases and C, in the signifier of solid char ( Wojtowicz & A ; Serio, 1996 ) . The gases and oil possess around half of the entire pyrolytic merchandise weight. The entire merchandise composing of pyrolysis is shown in Table 5.

Table: Pyrolytic merchandise composing ( Appleton, Colder, Kingman, et al. , 2005 )

Primary Merchandises

wt %


Secondary Merchandises



Hydrogen, C monoxide, C dioxide, methane, C2H6, ethylene, propane, propylene, butane, butylene, pentane, pentene, sulphidric acid




Aromatics, methane seriess, olefines, ketones, aldehydes




15 % ash,

3-5 % of sulfur

Carbon Black, Activated Carbon

In China, a new pyrolysis engineering has been developed called “ Minute negative-pressure pyrolysis ” ( Li, Xu, Gao, et al. , 2010 ) . In this procedure, the Surs are shredded into 20mm granulates and delivered to the reactor, which is at 480-700A°C and 0.01-0.04 MPa. This procedure produces stuffs in three stages ; Gases, liquids and solids. In the gas stage, H, methane and C oxides are produced. Liquids such as H2O, pitch and pyrolytic oils and solids such as char, ash and metals are besides produced. The procedure is fuelled by the gas produced in the pyrolysis as it contains both the combustive gas and the gas merchandises, which are hard to divide. Any extra gas is deficient for sale as a resource so it is normally burned off ( Rubber Manufacturers Association, 2009 ) . The pyrolytic oil can be used as a fuel as it has similar energy content to diesel oil, but can non be used in its virgin signifier as it contains several contaminations. It is must be refined for usage as a fuel ( Rubber Manufacturers Association, 2009 ; Samolada & A ; Zabaniotou, 2012 ) . Conventional pyrolysis procedures frequently suffered many mechanical jobs in the 1980s when pyrolysis was foremost introduced. A microwave pyrolysis works is presently the method used, which produces no pollution or emanations apart from waste H2O ( Appleton, Colder, Kingman, et al. , 2005 ; Yatsun, Konovalov & A ; Konovalov, 2008 ) . The procedure map is for a microwave pyrolysis works is shown below.

Figure: Process schematic of pyrolysis ( Appleton, Colder, Kingman, et al. , 2005 )

The char produces contains low class C black, ash and “ other inorganic stuffs, such as Zn oxide, carbonates, and silicates ” ( Amari, Themelis & A ; Wernick, 1999 ) . The C produced is of really low quality and does non hold any important commercial value. In fact, there is difference as to whether the C is carbon black or char due to the extent of its low quality ( Rubber Manufacturers Association, 2009 ) . The limited applications for this merchandise are as a material filler or as a coloring agent for plastics ( Rubber Manufacturers Association, 2009 ) and even this is merely possible after extended polish. The char can besides be used for activated C as it is really porous, therefore holding a big surface country that can be used for chemical reactions and surface assimilation ( Warhurst, McConnachie & A ; Pollard, 1997 ) . Activated C has many applications, the most important one being in H2O intervention and filtration. The intervention of imbibing H2O is an of import application in developing states, where entree to imbibing H2O is more hard. Activated Cs are used in filtration systems as they have good porousness. Activated Cs are efficaciously used as a method of taking gustatory sensation and odour contaminations from imbibing H2O. Harmonizing to Warhurst, McConnachie & A ; Pollard ( 1997 ) , it can besides be used to take toxins, such as microcystins, chronic exposure to which can be a cause of liver malignant neoplastic disease. In another application, activated C is used in the extraction of gold due to its ability to adhere metal ions. For this ground, it is besides used in the intervention of metal-contaminated waste H2O, which is a job in parts of India and Africa. Activated Cs can besides be used in the nutrient industry to bleach sugar and take hapless gustatory sensation from vegetable oil ( Warhurst, McConnachie & A ; Pollard, 1997 ) .

The economic viability of ELT pyrolysis has been evaluated by Wojtowicz & A ; Serio ( 1996 ) . The illustration given is a works with a payback period of 3.3. old ages doing $ 1.50 per Sur. Till today, the pyrolysis of ELTs has non been a commercially successful procedure due the limited and low quality of the merchandise and high running costs ( Samolada & A ; Zabaniotou, 2012 ) . Particularly for the char produced, a important sum of polish and intervention must be undertaken in order to use the C for utile intents. The chief argument that waste direction companies have is the cost of pyrolysis with regard to burning of the Surs. A SWOT analysis was conducted by ( Samolada & A ; Zabaniotou, 2012 ) , which analysis the belongingss of pyrolysis.

Table: SWOT Analysis of Pyrolysis ( Samolada & A ; Zabaniotou, 2012 )



Reduced air emanations

High investing and operation costs

High efficiency and energy ego sufficiency

Limited merchandise application

Potential marketable merchandises

Lack in merchandise standardisation

About zero waste

Merely financially feasible in big graduated table workss

Handiness of support


Handiness of natural stuff


Compact nature of workss


Management and legislative system




Extensive research expertness

Public agnosticism

High value added procedure – natural stuffs from waste

Lack of environmental criterions and engineerings

Decrease of aggregation fee of ELTs

Unproved markets for terminal merchandises

Minimize exportation

Lack of consciousness at legislative degree

Develop a legislative system


Opportunities for support


Niche market


Increase energy independency


Research from Li, Xu, Gao, et Al. ( 2010 ) shows that in China, it is common for oil to be extracted from Surs in an illegal mode. This is normally seen in rural countries. The method for this procedure is really similar to pyrolysis, nevertheless, here the Surs are fed into a kiln at 500-600A°C and heated for 8-10 hours. Once the procedure is complete, low quality oil can be separated from the debauched Surs and can be sold illicitly as fuel. Further jobs arise due to the illegal dumping of the Sur residues, as this can do dirt and H2O pollution.

Another possible procedure is devulcanisation. This is the procedure of interrupting down the cross-linked gum elastic construction by partly or wholly interrupting the bonds between sulfur and natural gum elastic. This disadvantage of this procedure is that the gum elastic obtained from the procedure no longer possesses the belongingss of the gum elastic before vulcanization ; normally the viscousness of the gum elastic is reduced. There are several methods of finishing this procedure such as, thermomechanical, thermochemical, physical and biological ( Sienkiewicz, Kucinska-Lipka, Janik, et al. , 2012 ) .

There are chiefly three stairss in the devulcanisation. First, the ELTs are land into all right atoms. In the 2nd measure, the gum elastic is assorted with chemicals that soften the gum elastic and trip the reaction for interrupting the chemical bonds. The gum elastic is treated at 200-220A°C and 2.0-2.3 MPa for around 3 hours ( Li, Xu, Gao, et al. , 2010 ) . The procedure takes topographic point in a reactor, in which the reactive constituents are continuously assorted while being externally heated via a het oil jacket. Finally, the merchandises are refined and procedures are undertaken to take the unpleasant smell of the gum elastic ( Li, Xu, Gao, et al. , 2010 ) .

The gum elastic produced from this procedure can be used for doing new Surs ; nevertheless, the sulfur can non be wholly removed from the gum elastic. This makes it unsuitable for other intents such as the production of plastics ( Integrated Waste Management Board, 2002 ) . Although devulcanisation is the oldest and simplest signifier of material recovery for gum elastic, the range for recovery of ELTs is limited due to the low quality of the merchandise, high energy usage and high degree of pollution ( Li, Xu, Gao, et al. , 2010 ) . The cost of this procedure makes it an unviable option for the recovery of ELTs.

Another possible procedure that is still under research is gasification. This is the procedure whereby pure O, H or steam is assorted with oil produced from the burning of ELTs. This takes topographic point under high temperature force per unit area, which enables the production of a gas. This gas so be used as a fuel for steam turbines to bring forth electrical energy ( Integrated Waste Management Board, 2002 ) . The gas produced typically has a calorific value 10-15 % higher than coal. This procedure produces ash and metal waste which can be converted into a scoria, which can so be used for several applications. Current fiscal theoretical accounts suggest that this procedure could be economically feasible every bit long as standard energy monetary values continue to lift ( Peace, Petersen, Leary, et al. , 2006 ) .

Material Recovery Processes

This subdivision describes the processing of ELTs utilizing mechanical procedures and lineations their possible applications, of which civil technology is a major sector.

First, the assorted methods of mechanical processing must be described, such as the shredding and grinding of the Surs. The grinding of Surs opens up a really big market of applications. The major job faced by the shredding and grinding of Surs is the steel belts and bead and besides the fabric beds which need to be separated during the procedure ( US EPA, 1991 ) . The steel and fabrics obtained from these procedures can be used for several applications.

Shreding and Grinding Procedures

ELTs can be shredded into 50 mm french friess through the usage of a shredding machine. In this procedure, the steel and fabric constituents are non normally removed. However, big pieces of steel bead can be removed before tear uping in order to cut down harm to the machine. Shredding is a suited method of cut downing the volume of ELTs as the volume is typically reduced by 75 % . This procedure is comparatively clean with the lone emanations produced being all right dust atoms ( ETRMA & A ; ChemRisk LLC, 2009 ) .

The first major crunching procedure used is ambient crunching. In this procedure, the chopped 50mm french friess enter a granulator, which repeatedly grinds the french friess in order to obtain rubber granulates or crumb gum elastic. The granulator removes the metal constituents through the usage of magnetic belts ( Li, Xu, Gao, et al. , 2010 ) . The fabric fibers are removed by utilizing agitating screens and air current sifters ( ETRMA & A ; ChemRisk LLC, 2009 ) . This procedure occurs at ambient temperature, therefore the name ‘ambient crunching ‘ . The lower size bound for crumb gum elastic from this procedure is 0.3mm. This procedure produces a big sum of heat, which can oxidize the crumb gum elastic, hence, a chilling system is required ( Sienkiewicz, Kucinska-Lipka, Janik, et al. , 2012 ) . The conventional below shows the procedure map for ambient grinding. The size is given in mesh graduated table and inches. Sizes below 5000 micrometers are referred to in this manner, with the mesh figure increasing with diminishing size ( SIGMA-ALDRICH, 2012 ) .

Figure: Ambient crunching procedure map ( Sunthonpagasit & A ; Duffey, 2004 )

Cryogenic grinding is a similar grinding procedure. However, in this instance, the chopped Surs are cooled below the glass passage temperature of the gum elastic utilizing liquid N. Typical temperatures are around -80A°C, at which the gum elastic becomes really difficult and brickle. Due to this, the gum elastic is crushed into little granulates in a cock factory. These granulates can be every bit little as 75Aµm, which means a really all right pulverization is produced ( Sienkiewicz, Kucinska-Lipka, Janik, et al. , 2012 ) . This enables the speedy separation of the gum elastic, steel and fabric via similar procedures as in ambient grinding ( ETRMA & A ; ChemRisk LLC, 2009 ) . This means that a purer gum elastic is produced compared to ambient grinding. The gum elastic crumb produced from cryogenic grinding has a much smoother surface and less surface country than that produced from ambient grinding ( Jang, Yoo, Oh, et al. , 1998 ) . However, due to the freeze, the crumb gum elastic has higher humidness content in cryogenic grinding. Besides, the cost of the procedure is increased due to the usage of liquid N. This can be reduced by utilizing compressed air alternatively of liquid N ( Sienkiewicz, Kucinska-Lipka, Janik, et al. , 2012 ) .

Sienkiewicz, Kucinska-Lipka, Janik, et Al. ( 2012 ) besides provide information about other procedures include wet grinding and crunching with a H2O jet. Wet grinding is based on the ambient crunching procedure but a few alterations exist. The chopped gum elastic granulates are assorted with H2O to organize a suspension. This is so land utilizing particular stationary and traveling grindstones. The advantage of this procedure is the H2O cools the gum elastic and the grindstones, forestalling oxidization. Furthermore, it is possible to obtain a finer gum elastic crumb of size 10-20Aµm.

Water jet grinding is chiefly used to interrupt down the construction of truck Surs due to their big size and hardness. It is wasteful to utilize crunching machines to treat these Surs as it would necessitate a significant sum of energy. High force per unit area H2O jets are used ( 2000 saloon ) which strips off the gum elastic bed from the Sur, go forthing the steel belts and beads behind. This allows a really pure crumb gum elastic to be obtained. Other than the huge sums of H2O used, this method is a low energy method and does non bring forth any pollutants ( Sienkiewicz, Kucinska-Lipka, Janik, et al. , 2012 ) .

An option that can be considered before the processing of Surs is de-beading. This is the remotion of the steel bead from the Sur construction. This reduces the sum of metal that needs to be removed during processing and besides increases the flexibleness of the Sur. This is a manual procedure and is hence expensive and time-consuming. De-beading is good in applications in which whole Surs are used near to natural H2O beginnings as there is a hazard that the bead can fade out and pollute the H2O. This procedure besides enables material applications of the steal bead ( Hylands & A ; Shulman, 2003 ) .

Applications of cured stuffs and recycling of whole Surs

Crumb gum elastic and chopped Surs have several applications, many of which are in the civil technology and building sector. Crumb gum elastic is besides used to do new rubber consumer merchandises, nevertheless this is a minor market in comparing to the building market. Whole Surs are besides extensively used in a figure of building applications and are besides used as alternate stuffs for insularity and protection.

Civil Engineering Applications

There are a figure of countries in which crumb gum elastic, shredded Surs and whole Surs play a portion in civil technology and building. These include landfill technology, dirt and drainage systems, eroding control, unreal reefs, insularity and surfacing.

There are a figure of belongingss that shredded Surs possess that can be utile for technology applications. These are summarised in the tabular array below. Surs can by and large be used in topographic point of normal technology stuffs when the belongingss below are required and besides a lightweight option is desired.

Table: Technology belongingss of chopped Surs and associated applications ( Hylands & A ; Shulman, 2003 )


Possible Application

Low compacted dry denseness

Foundation filling

High thermic electric resistance

Insulating bed to forestall freeze

High hydraulic conduction

Drain, landfill drainage line drive, leach Fieldss

Low horizontal emphasis

Fill behind walls and span abutments

In landfill technology, the usage of Surs is permitted and good in a figure of state of affairss ( Angloenvironmental, 2006 ) . These are outlined in Fig.11. First, Surs can be used to supply a leachate aggregation bed under the landfill site. Leachates are substances which are produced from landfill waste and can be absorbed into the dirt under the landfill site. Normally sand, rock or crushed rock is used for this application ( Rubber Manufacturers Association, 2009 ; Hylands & A ; Shulman, 2003 ) . ELTs can be used as whole Surs or scintillas of assorted sizes for this application due to their high permeableness and porousness ( Hylands & A ; Shulman, 2003 ) .

Surs can besides be used to protect the geomembrane from rupturing. The geomembrane represents the boundary between the landfill site and the Earth. Due to their squeezability, Surs can absorb daze from impacts and hence are a suited stuff for this application ( Hylands & A ; Shulman, 2003 ) .

Chopped Surs can besides be combined with dirt to be used as the day-to-day screen for the landfill. This cover stuff must be spread across the surface on a day-to-day footing in order to cut down odour and motion of the waste. Surs are non needfully a suited stuff for this application ; nevertheless, Surs are used here due to their comparative low cost and copiousness. Surs have a high hydraulic conduction, which means that they are really permeable to H2O, which is non a desirable quality for day-to-day screen as it means that H2O can come in the waste during rainfall. Besides due to the antecedently mentioned combustibleness of Surs, a fire hazard is present when utilizing them in this application ( Rubber Manufacturers Association, 2009 ; Hylands & A ; Shulman, 2003 ) .

Other applications in landfill technology usage tyres as a filling stuff for covering beds and for protection of the gas drainage system ( Rubber Manufacturers Association, 2009 ; Hylands & A ; Shulman, 2003 ) .

Figure: ELT Applications in landfill technology ( Hylands & A ; Shulman, 2003 )

Another major country of civil technology that involves Surs is in building filling and dirt conditioning. Surs are frequently used in the building of retaining walls and span abutments as a backfill stuff. In add-on, Surs are used as make fulling for embankment building.

Embankments are structures that envelop a main road. These are chiefly soil buildings ; nevertheless, frequently the dirt is really soft and can do instability of the construction. For this ground shredded Surs are used every bit make fulling as they increase the strength of the dirt. Tyre scintillas are suited for this intent as they are comparatively lightweight and cheap. Compacted chopped Surs can be 60-90 % lighter than normal dirt ( Edincliler, Baykal & A ; Saygili, 2010 ) . This ensures that there is decreased force per unit area on the dirt. Their high hydraulic conduction is an advantage in this state of affairs as it allows H2O to run out through the dirt, which improves the structural stableness of the embankment as low pore force per unit area is maintained. The soil-tyre composing must be varied in order to obtain the optimal belongingss. Harmonizing to Edincliler, Baykal & A ; Saygili ( 2010 ) , the commixture ratio is dependent on the method used to treat the Surs ( Edincliler, Baykal & A ; Saygili, 2010 ) . The diagram below shows the fill in embankments. Surs are besides used as fill in retaining walls for the same grounds as discussed here.

Figure: Sur fill in embankments ( Hylands & A ; Shulman, 2003 )

Surs are besides used for drainage applications. Chopped Surs can be used in the building of infected drainage systems. By utilizing Surs as a backfill for the drain building, force per unit area due to weight is reduced and the capableness to hive away H2O is increased ( US EPA, 2012b ) .

In add-on, tyre french friess can be used as make fulling for surface H2O drains on route sides. Normally, crushed rock or similar stuffs are used for this application ; nevertheless, this can ensue in dust distributing onto the route, which is a jeopardy for vehicles. Shredded or chipped Surs can cut down the hazard of harm occurring and besides supply better drainage ( Hylands & A ; Shulman, 2003 ) .

Rubber crumbs can besides be used for the drainage bed in green roofs. Green roofs are buildings carried out in order to cut down the C footmark of edifices as they offer thermic stableness through the roof. The edifice so stays ice chest in summer and heater in winter. This is done by seting flora to organize a bed on the roof of edifices. The drainage bed allows a balance to be between air and H2O in the roof. Therefore it must be hold appropriate H2O drainage belongingss. Surs are a suited stuff due to the high hydraulic conduction of crumb gum elastic ( Vila, Perez, Sole , et al. , 2012 ; Perez, Vila, Rincon, et al. , 2012 ) .

Figure: Floating Breakwater made from Surs ( Burgess, 2012 )

There are a figure of utilizations for Surs in a marine technology scenario. First, Surs can be used for the building of eroding control systems. In this application, Surs are normally used in their whole signifier and are de-beaded to forestall taint of the H2O.

Floating groins are used to absorb beckon energy before the moving ridge hits land. This helps to cut down eroding of coastal shores. Surs are suited for this application because they provide really effectual damping of moving ridges. The Surs are joined together and placed perpendicular to the moving ridges in order to supply effectual baffling for the moving ridges ( Hylands & A ; Shulman, 2003 ) .

Surs are besides used to do bales which can be used as a structural constituent in an eroding protection wall. This enables protection against eroding and quiver. Whole Surs are used in the building of sea walls to forestall coastal eroding. Sea walls can be constructed by repairing whole Surs onto wooden stations with high strength wire. Whole Surs are impermeable and supply muffling against moving ridges and therefore are suited for this application ( Hylands & A ; Shulman, 2003 ) . Surs can besides be used without wooden stations to make a mattress which provides protection against moving ridges. It is argued that in these applications, Surs are used chiefly due to their comparative inexpensiveness as these buildings display a 20 % failure rate. This is besides a consequence of hapless design ( Nairn, 2004 ) .

Artificial reefs are constructions in the sea which are constructed from Surs. These allow the colonization by many marine species due to the null infinite in the Surs. The Surs are anchored to the ocean floor ( Baine, 2001 ) in order to ease this. Surs are used here due to their low cost and lastingness. Some concern has been raised by environmental administrations about possible leaching of compounds into the H2O. Zinc is one of the chief compounds prone to leaching from a Sur ; nevertheless, grounds suggests that leachates are minimum comparative to compounds already bing in the H2O ( Collins, 2002 ) .

The concluding major application of Surs in civil technology is in thermic insularity for roads. In northern climes, H2O in dirts under roads can stop dead in winter and are so released when dissolving occurs in spring. This can do frost snap of belowground pipes. Freezing of roads is besides a safety jeopardy for vehicles and automobilists. Surs are suited in this application due to their high thermic electric resistance and low weight ( Hylands & A ; Shulman, 2003 ) . Typically, a bed of 6-12 inches of chopped Surs is placed under the route to forestall freeze of H2O ( US EPA, 2012b ) .

Other Applications

Surs and steel beads can be used in the production of concrete and cement. Chopped tyres and crumb gum elastic are used as gum elastic sum in concrete. Introducing gum elastic into the concrete mixture increases its flexibleness. Using the modified concrete has several advantages ; noise pollution and care costs are reduced, while the lastingness and life of the surface is increased. Furthermore, due to the ductileness of gum elastic, this concrete has greater opposition to frost-related snap. However, rubberised concrete has weaker weariness strength than standard concrete and therefore a thicker bed is required in usage ( Bravo & A ; De Brito, 2012 ) . Adding gum elastic sum besides improves the workability of the concrete mixture if the content is below 40 % and crumb gum elastic is used instead than scintillas. The size of the sum plays a portion in finding the compressive strength of the concrete. Compressive strength is by and large reduced if gum elastic sum is used due to hapless coherency between the gum elastic and the cement matrix. This decrease can be every bit much as 50 % . However, by utilizing crumb gum elastic, the loss of compressive strength is reduced ( Bravo & A ; De Brito, 2012 ) . Due to these features, rubberised concrete can merely be used in a limited scope of state of affairss. Rubberised concrete can potentially be used when quiver damping is required ; for illustration, it can be used as structural foundations for revolving machinery. It can besides be used for impact resistive constructions, such as clang barriers ( Siddique & A ; Naik, 2004 ) .

Using the recycled steel beads in concrete can ensue in increased stamina of the concrete. This reduces the workability of the concrete mixture and the compressive strength of the concrete is still lower than normal concrete. The motive behind utilizing recycled Sur stuffs in concrete is related to the application and cost of stuffs. Recycled tyre stuffs are comparatively inexpensive ; nevertheless, possible benefits are minimum from their usage in concrete. Further research is required to obtain a greater apprehension of this application ( Papakonstantinou & A ; Tobolski, 2006 ) .

The usage of gum elastic sum with asphalt is referred to as gum elastic modified asphalt ( RMA ) . Asphalt is besides known as bitumen, which is a heavy, syrupy crude oil fraction. Asphalt is used for doing route surfaces and a specific application of RMA is in the readying of athleticss and recreational surfaces. In RMA production, crumb gum elastic is blended with the bitumen in a moisture or dry procedure ( Hylands & A ; Shulman, 2003 ) . Roads constructed utilizing RMA have some improved features. First, the overall quality of the route is increased, with improved thermic stableness and improved life. Thermal stableness means that there will be less fluctuation in the route features ( tyre clasp etc. ) with altering temperature. Furthermore, there is an addition in clash which can cut down skidding. In add-on, operational noise is reduced and there is less hazard of distortion and weariness snap due to the flexibleness of the gum elastic crumb ( Hylands & A ; Shulman, 2003 ; Sienkiewicz, Kucinska-Lipka, Janik, et al. , 2012 ) . If the route surface breaks up, the rubberised atoms are less likely to do harm to vehicles. The usage of RMA has been common in the US for over 50 old ages and in the EU, RMA route building is increasing ( Rubber Manufacturers Association, 2009 ) .

Sports and recreational surfaces are a major donee of RMA and crumb gum elastic. One method is utilizing a combination of crumb gum elastic with polyurethane to organize a dry mixture. The other method is utilizing a polymerised RMA, similar to that discussed above. The dry mixture is usually used in making unreal sod for athleticss Fieldss. The normal RMA mixture is normally used to make surfaces in resort areas ( Hylands & A ; Shulman, 2003 ) .

Using crumb gum elastic for unreal sod ( AT ) is an progressively popular application. In 2007, 4.5 % of entire US bit Sur was used in crumb gum elastic come uping for athleticss Fieldss. The of import consideration in AT is playing comfort of the surface, or playability. AT has increased playability over conventional surfaces as playing Fieldss have significant discrepancy in quality. Furthermore, AT has a greater life than standard surfaces, with over 2000 hours more playing clip per twelvemonth ( Simon, 2010 ) . AT is besides non affected by rainfall or any other inauspicious conditions conditions. Health hazards of AT have been on a regular basis questioned with respects to potential for hurts and toxicity. Some surveies have suggested that AT and grass Fieldss have really similar hurt rates and the nature of the hurts does non propose one surface is less safe than the other. However, the most recent developments in AT are potentially safer than grass playing Fieldss. Harmonizing to Meyers ( 2010 ) , FieldTurf, the latest embodiment of AT, is safer than conventional grass playing Fieldss. This is due to fewer cases of hurts over the 3 old ages of the survey. With regard to toxicity, in general, there is no existent wellness menace through the usage of gum elastic crumb on playing surfaces ( Connecticut Department of Environmental Protection, 2010 ) . However, it must be mentioned that stormwater overflow AT contains a degree of Zn contamination from crumb gum elastic that is above acceptable degrees. This should be remedied utilizing better drainage systems ( Connecticut Department of Environmental Protection, 2010 ) . In add-on, the consumption of gum elastic crumb is possible in the instance of little kids who use the surfaces. Besides, particulates could be unwittingly inhaled. However, the perceptual experience of a possible wellness hazard is much greater than the hazard itself. AT is really popular due to its low care qualities and therefore much reduced running costs. Although the installing costs of AT are greater, this will be regained due to the low running costs. In general, AT surfaces have several advantages over grass playing surfaces and their increased usage is due to this. The chief obstruction to their farther popularity is wrong public perceptual experience of wellness and safety ( Simon, 2010 ) .

Crumb gum elastic is besides used in the resort area market in a signifier of RMA. This is due to the ability of gum elastic to absorb daze ; hence, it is good for the safety of kids. The demand for this application is diminishing due to the fact that other stuffs are cheaper and have a shorter life than RMA ; therefore it is more profitable for providers to sell the lower quality stuffs ( Rubber Manufacturers Association, 2009 ) .

Crumb gum elastic can besides be moulded or extruded to bring forth assorted merchandises such as floor tiles, rug carpet pad and railroad slumberers. The crumb gum elastic is normally held together utilizing an adhesive. There is a immense potency for enlargement in this market due to the high lastingness and quality of the merchandises. It is sensible to anticipate an addition in the nature and figure of these types of merchandise in the hereafter ( Hylands & A ; Shulman, 2003 ; Shulman, 2009 ; Rubber Manufacturers Association, 2009 ) .

A really limited application is the usage of crumb gum elastic in the fabrication of new Surs. The usage of crumb gum elastic in this application is restricted to 5 % of the gum elastic for the Sur ; greater measures will ensue in damaging effects to the quality of the Sur. In fact, there are no technology benefits to be gained by recycling tyre gum elastic to bring forth new Surs ( Rubber Manufacturers Association, 2009 ) .


It is of import to now compare the assorted terminal of life utilizations described in this literature reappraisal. In add-on, the direction of used Surs around the universe will be discussed and evaluated. Finally, future applications will be suggested with betterments and farther actions for the direction of ELTs.

The reuse and retreading of Surs was shown as a feasible option for widening the life of Surs. The popularity of retreaded Surs in emerging economic systems, such as in India, is due to their lower cost than new Surs. The chief obstruction that faces their application in the major Western economic systems is the wrong negative perceptual experience that recaps are less safe than new Surs. In order to increase the popularity of recaps in these states, more instruction should be given to consumers in order to guarantee them that recaps are dependable. This could besides be done through inactive selling, for illustration by publishing pro-retreading newspaper or magazine articles. However, this is improbable to go on unless national authoritiess back up reworking to the full as it does non do economic sense for Sur makers and Sellerss to sell recaps alternatively of new Surs. It is besides utile to see the design of Surs to widen their life in order to cut down the sum of used Surs. In add-on, consumers should be more informed about how to utilize their Surs right in order to cut down wear and widen their service life. However, these steps have a significantly lower impact on the direction of used Surs than traditional recovery methods.

It can be seen that if the disposal of Surs via landfilling or stockpiling is prohibited, a figure of recovery options exist, which can bring forth a figure of utile natural resources. First, energy recovery methods were considered, specifically Tyre Derived Fuel ( TDF ) . TDF involves the burning of the Surs. Harmonizing to Sienkiewicz, Kucinska-Lipka, Janik, et Al. ( 2012 ) , 87-115 MJ/kg are required to bring forth a Sur. From burning of this Sur, merely 32 MJ/kg are recovered. The energy required to treat a Sur into crumb gum elastic is merely 1.8-4.3 MJ/kg. Although this energy demand for material recovery is little, with TDF, some energy can be recovered for new intents. Tyres represent a significant beginning of locked energy and hence present a inexpensive and plentiful supply of energy resources. Furthermore TDF is simple and easy to transport out as merely simple burning is required ; hence, no new installations are required for this to be possible. This is highly good in topographic points where stuff recovery installations do non be or are scarce. TDF can be used in several industrial kilns and can be used to consume reserves and take Surs from landfill sites. In add-on, there are about no emanations produced from TDF, which means that it can be a possible ‘green ‘ energy production method. Further research must be conducted into the usage and development of dedicated tyre-to-energy workss as this can be a future method of energy recovery.

Material recovery is an country in which there are many possible applications. This was split into regenerative procedures and stuff recycling processes. Regenerative procedure included pyrolysis, devulcanisation and gasification. These procedures involve the chemical dislocation of the Sur to bring forth stuffs that can be used in other applications. There are many drawbacks to utilizing these procedures. First, the merchandises obtained are of hapless quality and necessitate farther intervention and refinement to be used. Regenerative procedures are besides really expensive as the workss have high installing and running costs. However, gasification is an country with possible ; it combines oil obtained from pyrolysis with other gases to bring forth a high energy gas. This can be used as a fuel beginning in future, in concurrence with pyrolysis and TDF to obtain maximal energy from Surs. Other regenerative procedures require farther research before they can go financially feasible on a big graduated table.

However, material recycling nowadayss a wealth of chances in footings of resource recovery. The decrease of ELTs to little granules and scintillas can enable their application in a figure of civil technology state of affairss. Surs are used chiefly as make fulling stuff for earth building or wall building. ELTs are an ideal stuff for these applications as they can be obtained cheaply and have good opposition to thermal alteration, emphasis and impact. As mentioned earlier, the energy required to treat these Surs is minimum compared to the energy required to bring forth a Sur. Crumb gum elastic has a figure of applications which were described in this literature reappraisal. The chief applications were for unreal sod, concrete production and rubberised consumer merchandises, such as colloidal suspensions for places.

In comparing, material recovery provides more applications for resource recovery than energy recovery at a lower energy and fiscal cost. The per centum of the original energy recovered in TDF is less than 40 % . If material recovery techniques are impracticable or the installations do non be, so TDF is a good option for cut downing the sum of Surs in reserves. In states with a hapless recovery substructure, focal point should be placed on first implementing energy recovery methods and at the same time or later constructing material recovery workss. The primary end should be to extinguish Surs from landfill and reserves every bit far as possible.

The direction systems in topographic point play a important function in the recovery rates of ELTs. The theoretical account in the EU is one that functions efficaciously and therefore this part has the highest recovery rate globally. The chief ground for this is the Producer Responsibility direction system. This system involves holding Torahs in topographic point which oblige Sur manufacturers and Sellerss to pull off ELTs. A legal model is the most effectual method in obtaining a high recovery rate ; without specific Torahs, manufacturers and Sellerss would hold no involvement in the direction of used Surs as this is non a profitable scenario.

Improvements in direction construction must be seen in states such as India and China as many used Surs are produced, but presently, recovery is minimum. Implementing a Producer Responsibility system would ensue in greater actions being taken in order to recycle Surs efficaciously. In add-on, specialist direction organic structures must be established so that Surs are non assorted in with other wastes ; from this literature reappraisal it is more appropriate to see used Surs to be a resource than waste.


In decision, there are a assortment of options available for the farther use of used Surs. First, used Surs can be retreaded or reused. If this is non possible, they are either stockpiled in monofill sites until a usage is found for them. These ELTs have several applications which have been sorted into two classs: energy recovery and material recovery. Energy recovery involves the burning of ELTs in order to bring forth energy. Material recovery describes processes which allow new stuffs to be obtained from the chemical debasement of ELTs, which can be used for a broad array of applications. In general, both paths have their benefits, but material recovery has such a big figure of utilizations that can be completed with a comparatively low sum of energy compared to the energy required to bring forth a Sur. Energy recovery merely regains less than 40 % of the original energy and therefore is non as cost effectual as material recovery. In general, the literature has shown that ELTs should now be seen as a ‘useful waste ‘ , or a resource, which can be used in several utile applications.

The direction of Surs is an built-in variable in the recovery rate of ELTs. The recovery rate is 96 % in the EU ( Sienkiewicz, Kucinska-Lipka, Janik, et al. , 2012 ) , which is a consequence of a well-structured and implemented direction system. The direction system that appears to be the most effectual is the Producer Responsibility theoretical account, where jurisprudence states that Sur manufacturers and Sellerss should pull off used Surs. The hapless recovery rates in other states, such as India and China, are a consequence of a deficiency of recycling substructure and direction system. This literature reexamine recommends that similar systems to the EU should be adopted by these states and enforced in a thorough mode in order to ease effectual ELT recovery.


Recommendations are provided for the betterment of resource recovery from ELTs.

Material recovery is a far more extended application for ELTs than energy recovery ; hence, more investing should take topographic point into the development of stuff processing installations for the long term.

If this is non possible, Surs should be combusted for usage as TDF in order to cut down reserves rapidly and repossess energy.

States without a structured used tyre direction system should strictly follow the Producer Responsibility theoretical account, which is successfully implemented in the EU.