Issues facing the recycling industry
6.1
The previous chapter highlighted the implications of the lack of domestic
demand for recycled content, particularly given China's recent decision to ban
the importation of 24 types of material.
6.2
Other reasons attributed to the challenges the recycling industry face,
however, relate to the collection, sorting, and processing of materials. This
chapter examines issues related to the approach taken to collecting materials
as well as the infrastructure for sorting and processing. The issue of
stockpiling is also discussed, as are particular issues related to specific
types of recyclable material, including glass, mattresses and tyres.
Implications of collection methods for recycling
6.3
Submitters emphasised that the collection method is a major component in
ensuring the high quality of recyclable products and in ensuring viable markets
for recyclable materials. In particular, the quality and quantity of material
collected and diverted to recycling is affected by:
-
differing collection methodologies utilised in in recycling
programs, both within and between states; and
-
policy settings.[1]
6.4
The variability of recycling yields was highlighted by Re.Group, which
submitted that:
Analysis of household recycling
yields across all NSW Council areas, using 2011–12 data published by the NSW
EPA, demonstrates the scale of variance in the quantity of material collected
for recycling in this one jurisdiction. Across NSW, the average yield is about
250kg/household/year. However, there are more than 40 councils with yields
above 300kg/household, and more than 10 with yields above 400kg/household/year.[2]
6.5
Re.Group also provided an example of the differences in the quality of
recycling feedstock collected in New South Wales, measured in terms of
contamination by items that are not able to recycled at a specific facility. It
submitted:
We have some council clients where 'yellow bin' recycling
feedstock consistently has less than 10% contamination, and other clients where
contamination levels are up to 20%. Contamination management is a key factor in
the cost of operating a recycling facility...[3]
Collection methods
6.6
In its submission, the Western Australian Local Government Association (WALGA)
outlined the different types of programs which can contribute to the collection
and recovery of recyclable material. These programs include the provision of
multiple bins to encourage source separation of waste, organics and recycling
at the household level; container deposit schemes which improve the quality of
both eligible materials and what remains in kerbside programs; and product
stewardship schemes such as DrumMuster and MobileMuster which promote the use
of specific collection infrastructure.[4]
6.7
The committee received evidence about the collection methods in place
throughout Australia. For example, the Lake Macquarie Council submitted that
'fortnightly collection of a mobile recycling bin has proven to be the most
effective in terms of yield, presentation rates, ratepayer satisfaction, safety
and cost effectiveness'. It stated that as a result, this model for recycling
has been 'widely adopted across Australia'. The Council also noted that the
addition of fortnightly garden or weekly food and garden waste kerbside
collection services has also proven effective.[5]
6.8
It was particularly noted that the kerbside regimes (up to three bins)
in New South Wales, Victoria, Australian Capital Territory and South Australia
result in greater diversion from landfill of both household recyclables (paper,
cardboard, glass, aluminium, plastics and steel) and green waste. The Waste
Management Association of Australia (WMAA) explained that a number of jurisdictions
also provide assistance in diverting food waste from landfill towards the green
waste.[6]
6.9
The South Australian Government, which was recognised by the Australian
National Waste Report 2016 as having the highest resource recovery rate in
Australia, highlighted the success of its kerbside recycling collection system
which diverts 47.8 per cent of kerbside collected material away from
landfill. It submitted that an investment of $7.25 million has provided
householders with access to easy to use, two and three bin systems.[7]
6.10
The Northern Adelaide Waste Management Authority (NAWMA) submitted that
a three bin system should be mandatory in all metropolitan areas. NAWMA also
suggested that governments should not preclude or prevent collection systems
that may divert more recyclables from landfill. It highlighted that in South Australia
it is mandated that municipal solid waste must be collected weekly while 'other
jurisdictions have shown step changes in recycling rates from a weekly food and
garden organics service, and fortnightly residual waste' collection.[8]
6.11
Local Government New South Wales (LGNSW) also noted that the collection
methods of kerbside recycling chosen by local councils is influenced by both
the market value of recyclates, and community expectations and behaviour. It
noted that in New South Wales:
Some NSW councils source separate materials, such as paper
and cardboard, as a higher quality recyclate has more market value. Other
councils have mixed waste and recycling collections that are processed at
advance waste treatment centres as diverting recyclable
materials from the general waste stream has proved challenging in some
communities.[9]
6.12
Container deposit schemes (CDS) can also increase the rate of container
recycling and increase source separation. They also have the additional benefit
of reducing litter. Under a CDS, a refund is provided for eligible empty
containers that are returned to a designated collection point. The longest
running CDS in Australia is in place in South Australia. Other jurisdictions
with CDS in place, or where schemes are being developed, are New South Wales,
Queensland, Western Australia, the Australian Capital Territory and the
Northern Territory.
6.13
A number of submitters highlighted the benefits of CDS. For example, the
Western Australian Local Government Association (WALGA) submitted that:
There is documented evidence that a CDS improves
the quality of both eligible materials and what remains in the kerbside system. Furthermore, the provision of handling fees can encourage operators
and community groups
to participate
in the waste
management industry and develop markets for collected material.[10]
6.14
Implications for the glass industry associated with CDS are discussed
later in this chapter.
Issues with existing approaches to
kerbside collection
6.15
The Victorian Waste Management Association (VWMA) submitted that collection
methods have developed to provide the simplest and most efficient mechanism for
households, and have reduced manual handling exposure for the industry. It
noted that 'infrastructure is now all geared to handle comingled recycling'.
The VWMA concluded that 'separation at source (i.e. by the householder)
requires significantly more resources and space and reduces the economics of
the activity'.[11]
6.16
However, a number of submitters highlighted that the separation of
materials at the source results in higher yield recycling programs. Maitland
City Council submitted that 'the collection of comingled materials will always
be of lower quality than the collection of source separated clean recyclables'.[12]
Similarly, the Waste Management Association of Australia (WMAA) submitted that
'by source separating different waste streams, and providing accessible
collection systems, there is an increased ability to recover materials which
can be potentially recycled into other products'.[13]
The Western Australian Government likewise submitted that:
The State Government and the Waste
Authority strongly support source separation rather
than mixed waste processing as a preferred means to
achieving higher recovery. Source separation generates more homogenous waste
streams which are easier to recover and represent
a higher value
to the recycling sector.[14]
6.17
The South Australian Government was also supportive of source separation
at the household level, and submitted that:
Source separation at the point of generation (i.e. household)
generally results in a much higher quality recyclable material than a single
bin system for all household wastes that relies on downstream processing
technology to subsequently separate out various materials. Collection is undertaken
using compaction vehicles that in the case of recyclables can result in further
contamination due to glass breakage that embeds in other recyclables such as
paper / cardboard.[15]
6.18
Mr Jeffrey Angel, Director, Total Environment Centre/Boomerang Alliance,
told the committee that 'source separation in a genuine sense is the opposite
to co-mingled'. Mr Angel stated:
...we do have red and yellow and green bins, where ostensibly
there is some general separation. But, as we've seen in the yellow co-mingled
recycling bin, that degrades the material value of the paper and metal and
plastic. Not only that, but in placing it both in the bin and in the garbage
truck, where things are then compressed, the glass breaks and infiltrates the
paper. That also makes the paper either useless or of low value.[16]
6.19
Visy similarly submitted that accurate at-home segregation is
'inconsistent at best' and that the causes of this include reduced size waste
bins, differing council guidelines, volumes of waste to be disposed, and the
level of householder education. Visy explained that the failure to segregate
materials 'may doom tonnes of other recyclable items to waste' as contaminant
items can confuse sorting machinery in MRFs or elude hand sorting, thus risking
'contaminating an entire load'.[17]
6.20
SKM Recycling suggested that the provision of smaller general waste bins
by councils 'may also be contributing to an increase in the quantum of
non-recyclable (waste) materials ending up in recycling bins'.[18]
6.21
The Australian Capital Territory (ACT) Government argued that
'government interventions to achieve a greater level of upstream sorting can
greatly impact on the quality and quantity of materials recovered for
recycling'. It highlighted that in the ACT when construction and demolition
(C&D) waste is sorted onsite, virtually all of the material can be
recovered and the gate fees for the sorted material at C&D MRFs can fall to
under $20 per tonne. Companies that deliver unsorted C&D waste to MRFs are
charged over $130 per tonne and only 75–85 per cent of the material
is recovered.[19]
6.22
The ACT Government also noted that office waste, if not sorted onsite is
often collected with other commercial waste such as food waste and as a result
is considered contaminated and sent to landfill. The ACT Government highlighted
that the cost to send such waste to landfill or to Advanced Waste Treatment
(AWT) facilities for processing is much higher than sending it to facilities
for sorted material. The ACT Government submitted that this
demonstrates that state and territory governments can set requirements for
waste management which achieve positive outcomes for recycling. It submitted
that:
The ACT has been successful at increasing recycling from
C&I [commercial and industrial] businesses via its Actsmart program. However,
at present this only reaches around 6 percent of eligible businesses. A case
may exist for further Government interventions to achieve higher adoption
levels.[20]
6.23
Kerbside collection also has particular implications for the glass
recycling, which are discussed later in this chapter.
Need to educate households and
provide incentives
6.24
Submitters also noted that significant community engagement and
education are required to increase the quantity and quality of recycling
collected. WMAA stated that:
Having a well-informed community that has easy access to
collection systems such as those described above definitely assists with source
separation of waste into the respective streams, and can therefore improve the
quality of what is collected and recovered. This also has the additional
benefit of improving the remanufacturing process, by assisting to reduce costs
associated with contamination.[21]
6.25
In addition to the need for appropriate infrastructure for the
collection and processing of material to be in place, the WALGA submitted that
'the chances of recovering good, high quantity material' can be increased
through the use of:
-
a well-funded communication and engagement program; and
-
sufficient motivation to undertake waste diversion
activities—motivation can be intrinsic (value based), related to incentive
(cash), or a wish to avoid a negative consequence (regulation).[22]
6.26
The VWMA submitted that 'the complexity of materials and the different
materials collected by council recycling can be confusing to residents,
especially to renters who have less ownership of recycling than longer term
residents'.[23]
6.27
As previously noted, source separation is critical to ensuring that
recycling processes are efficient and effective. SKM Recycling submitted that
'the presence of non-recyclable materials in SKM's feedstock reduces the
efficiency of SKM's materials recovery processes'. It attributed poor kerbside
sorting practices 'partly to a lack of community awareness as to what can, and
what can't be recycled in the kerbside recycling bin'. SKM Recycling suggested
that the Australian Government should provide funding to support community
education programs to encourage sound recycling practices.[24]
6.28
Visy also supported the implementation of 'strong education practices to
promote better at-home recyclables segregation'. It stated that:
...there are householders that simply do not comply with
Council recycling guidelines and those who practice "wish-cycling".
Wish-cycling is the phenomenon of tossing anything and everything that could
possibly, maybe, sort of be recycled into the recycling bin.[25]
6.29
It was also argued that the ability to export recycled materials to
China has resulted in a policy and education focus on the quantity rather than
the quality of recycling which has led to the contamination of recycling
streams. Mr Harry Wilson, President, Waste contractors and Recyclers
Association of New South Wales (WCRA), told the committee that:
As an industry we pulled off
the advertising and the education of the ratepayers over the last five or 10
years because of the acceptability of this product into China. I think that was
a bad mistake by the whole industry. That has to come back on and we need to
tell the public that some of these products aren't recyclable and get them out
of the stream so that we're not handling non-acceptable items. I think we can
do better in that area, and that's federally.[26]
6.30
The Ipswich City Council noted that levels of contamination in its
recycling program had increased over the past five years and attributed the increase
to education programs in its jurisdiction becoming lax. Councillor Andrew
Antoniolli, the then Mayor of Ispwich City Council, told the committee that the
council has focused, and continues to focus, on educating children in local
schools, but noted that 'different age groups have different understandings of
recycling, and particularly the older age group sometimes get somewhat
confused'.[27]
6.31
Councillor Antoniolli also noted that the area has a diverse cultural
community and 'some cultures aren't as familiar with recycling as others'. Councillor
Antoniolli told the committee that the council had recently released a 'bin
app' which advises residents on bin collection schedules and the correct bin to
utilise, but that 'the up-take rate of the app' has not been as high as the
council would prefer. Councillor Antoniolli acknowledged that council may have
placed too much emphasis on the app and that in the future, there must be an
'advanced education scheme' implemented.[28]
6.32
LGNSW submitted that as each council responds to the unique needs of
their community, a range of practices and collection methods are utilised. This
can also lead to challenges in educating householders on what items can be
recycled, and the correct method for disposal.[29]
6.33
Similarly, Mr Peter Shmigel, Australian Council of Recycling, told the
committee that the level of investment in recycling varies from council to
council. Mr Shmigel stated:
The reality is that from
council to council you find very different levels of investment, effort in contamination
reduction and in education of the community. Some rely entirely on their
contractors and some do it themselves. It's a totally disparate approach in the
same way that it's disparate around which bins there are. I think that a
concerted effort can get you come gains right away.[30]
6.34
The South Australian Government noted that investment in the Recycle
Right household education program has assisted in addressing the issue of
householders placing incorrect items in kerbside recycling bins.[31]
The Adelaide Hills Region Waste Management Authority (AHRWMA) also highlighted
the importance of education in achieving positive outcomes in recycling, and
the need for such programs to be funded. It submitted that:
Advice and understanding of what can/cannot be recycled has
the ability to significantly impact consumer behaviour and decisions regarding
waste – for example takeaway coffee cups. When consumers became aware that
takeaway coffee cups potentially could not be recycled through kerbside
recycling bins there was a quick change in behaviour to use reusable cups. This
matter also raises the importance of education in the effort to reduce waste to
landfill.[32]
6.35
Re.Group, which operates a number of recycling facilities, and accepts
feedstock from a range of local councils and commercial operators submitted
that 'there are significant differences in the quantity and quality of material
collected for recycling in different parts of Australia'. It attributed these
differences to 'the lack of a consistent national approach to education and
promotion of resource recovery activities'. Re.Group advocated for the
development of a nationally consistent education program, based on existing
programs which have been proven to be successful. It submitted:
Community engagement and education is a critical factor for
increasing the quantity and quality of recycling collected. Given that this
education is often left to individual councils or contractors, the messaging is
often inconsistent and less effective than could be possible through a more
coordinated national approach. There are excellent examples of recycling
education programs that have been developed in specific parts of Australia,
which could be readily replicated and rolled out across a much larger audience.[33]
6.36
The City of Gold Coast (CoGC) submitted that it has been offering
'financial incentives to residential customers' to encourage the use of green
waste bins to reduce the volume of green and food wastes entering landfill. It
submitted that this has proven successful with up to 20 per cent of CoGC
households becoming customers over four years. The CoGC also noted that 'at a
future tipping point, incentives lose their impact and disincentives such as
higher disposal fees have more influence, e.g. green waste disposal charge
increases make a green waste collection service a more viable option. The CoGC
stated that the introduction of mandatory collections will maximise the
quantity of organics collected but that there will be an inevitable increase in
contamination from disengaged residents.[34]
6.37
The South Australian Government submitted that state governments should
consider implementing variable rate pricing to provide a 'more direct market
based price signal and economic incentive for behavioural change towards
resource recovery'. Variable rate pricing would charge householders for the
disposal of waste in a similar manner to other utilities such as water and
electricity. This would be in accordance with two guiding principles of
environmental policy, namely the polluter pays principle and the shared
responsibility concept.[35]
6.38
The South Australian Government suggested that variable rate pricing
would increase the transparency of the price differential between recycling and
landfill disposal. It submitted that an effective variable rate system should
be built on three pillars—identification (for waste generator accountability),
measurement (of waste and/or services provided), and unit pricing (charging
according to service provided). The South Australian Government suggested that
such systems can take various forms. It stated:
A variable rate pricing system can take various forms such as
weighing the amount of waste in collection bins or using pre-paid bags, tags or
stickers or prescribed sizes of waste bins. Technical specifications depend on
the specific situation in the collection area, provisions made in legislation
and other waste policy. While they operate differently from one another, these
systems share one defining characteristic - person/business who throws away
more, pay more.[36]
Issues related to particular types of recyclates
6.39
The following sections will outline the evidence raised in relation to
the collection, sorting and recycling of particular types of recyclates which
pose unique challenges to the recycling industry. This includes: glass,
mattresses, and tyres.
Glass
6.40
Submitters noted that the glass recycling sector is facing significant
challenges including that:
-
commodity prices are non-existent with some councils paying to
have glass recovered;[37]
-
glass is being stockpiled as there are limited established
markets for recycled glass;[38]
-
there is progressive closure of glass furnaces by glass
re-manufacturers; and
-
there is a decline in investment for glass manufacturing.[39]
6.41
Glass is currently recovered through kerbside recycling and CDS.
However, the committee received evidence indicating that both collection
methods present issues for glass recycling.
Kerbside collection
6.42
While there are high levels of recycling of glass through kerbside
systems, submitters pointed to problems with kerbside recycling. For example,
Visy submitted that glass recycling has posed a challenge to the industry for a
number of years. It stated:
The sorting, cleaning and re-manufacture of glass received
from the kerbside recycling stream has posed serious challenges to the
recycling industry over many years. Glass is a significant portion of the
kerbside recycling bin, making up circa 35% of the volume. Therefore of the
total 3 million tonnes per annum collected from kerbside bins, approximately
1 million tonnes is glass.[40]
6.43
Owens-Illinois explained that current kerbside collections systems
result in 'a significant level of small glass fragments and contaminants'
that cannot be used in recycled glass manufacturing. It stated that co-mingled
recycling collection combined with high compaction rates breaks glass into
small fragments that cannot be extracted, and contaminates other recyclable
materials.[41]
6.44
Mr Nicholas Harford, Equilibrium, told the committee that glass products
collected in kerbside recycling:
...get broken at multiple points. When the bin gets picked up
it gets thrown into the truck pretty hard, depending on the style of the truck.
As the truck gets fuller, most trucks compact within the truck, so that creates
breakage as well. When the truck gets to the material-recovery facility the
material is dumped onto a cement floor, so you get more breakage. It's usually
picked up in an excavator if it hasn't been dumped straight into a loading bay
of some sort, so it gets picked up and dumped again. All through these phases
it gets broken. I would explain as well that over the years a lot of bottles
have got lighter and thinner, which is a good thing because it uses less
material and energy in its manufacture. But it breaks more easily.[42]
6.45
In addition, Owens-Illinois explained that for operational, quality and
safety reasons, glass must be colour sorted and contaminants such as metal,
stone, ceramics, and a range of glass types (e.g. Pyrex glassware, drinking
glasses, and medical and laboratory glass) must be removed prior to processing.[43]
6.46
Owens-Illinois stated that despite these challenges, it has been able to
maintain an average of 250,000 tonnes of post-consumer cullet, and recycle
content has increased from 23 per cent to 39 per cent over the past 15 years.
It attributed this success to a willingness to invest in technology to process
recycled glass, and manufacture new containers with an increasing recycled
content. Owens-Illinois highlighted the investment in technology such as
optical sorting and x-ray technology to colour sort small particles of glass
and remove contaminates. It stated that 'such technology is expensive and its
commercial viability relies heavily on high volumes of glass collected through
co-mingled kerbside collection'.[44]
Container deposit schemes
6.47
Given the issues kerbside collection presents for glass recycling, the
introduction of CDS (also referred to as container deposit legislation, or CDL)
creates an alternative stream of glass collection, diverting material from kerbside
collection systems. Some submitters highlighted the benefits of CDS for glass
recycling, including that it reduces glass contamination of co-mingled
recycling, and yields higher quality recyclates. Other submitters, however,
argued that the introduction of CDS pose a number of challenges to glass
recycling in Australia. This section explores these issues.
6.48
The South Australian Government, which has had CDL since 1977, submitted
that its scheme results in reduced glass in kerbside recycling, which has reduced
glass breakage in compaction vehicles and led to higher quality recyclables.[45]
The scheme has also increased the quality of recovered materials due to a
greater level of separation according to container type. It submitted that
there are 120 depots across the state where deposits can be redeemed.[46]
Similarly, Councillor John Woodward, City of West Torrens (South Australia)
submitted that:
Container Deposit Levy (CDL) in South Australia has proved
effective in reducing waste, increasing recycling and importantly, creating a
high quality glass for recycling. The CDL allows the glass to be sorted into
different colours at source, which increases the quality and value of the
material for recycling. There is a strong argument for making the CDL a
national scheme and increasing the deposit to 20c per item.[47]
6.49
It was submitted that in addition to improving recycling outcomes and
reducing waste, container deposit schemes provide a buffer against changes in
commodity prices or changes in the recycling regulatory environment. For
example, Mr Ritchie, MRA Consulting, told the committee that:
...container deposit schemes are worth somewhere between $190
and $300 a tonne in additional revenue to that MRF-council combined entity—and,
yes, there's a whole debate happening about where that is apportioned and
allocated—but CDS in New South Wales at least offers a buffer to China National
Sword that perhaps other states don't have. It's half as much again in terms of
value to the MRFs.
6.50
Owens-Illinois told the committee that, globally, it has supported
'non-discriminatory' CDS when the scheme helps 'deliver high volumes of good
quality and cost effective cullet'. Owens-Illinois emphasised that its support
'is very much market specific and our support for CDL is typically in markets
that have limited recycling infrastructure and where existing recycling
outcomes are poor'.[48]
However, in considering the introduction of schemes in both New South Wales and
Queensland, Owens-Illinois expressed a preference for a 'centralised container
deposit scheme'. The benefits of a single, national approach are further
discussed in Chapter 7.
6.51
The implications of new schemes being introduced in states such as
New South Wales and Queensland attracted significant comment. The Local
Government Association of Queensland, in considering the impact of the upcoming
introduction of a CDS in Queensland in July 2018, submitted that:
The introduction of a Container Refund Scheme (CRS) in
Queensland on 1 July 2018 will provide significant resource recovery opportunities
and challenges across the State. In particular, CRS glass collected through a
container refund point is not subject to compaction making it capable of being
sorted and as such a more valuable commodity. However, comingled glass
collected outside South East Queensland (SEQ) through a local government
kerbside collection would have greater transport costs and would be least
desirable compared with CRS and SEQ glass.[49]
6.52
The Brisbane City Council submitted that glass containers in kerbside
recycling bins currently represent approximately $12.5 million in council
revenue. It submitted that when the Queensland Government implements the
Container Refund Scheme from 1 July 2018, it is expected that these containers
will not remain in the kerbside system as 'community groups and charities will
all operate as collection and refund points, thereby diverting these funds into
community groups'. The Brisbane City Council also submitted that 'the cost of
the scheme (external to local government) will far outweigh any benefits
gained'.[50]
6.53
Similarly, Visy, in considering the introduction of CDL in Queensland
and New South Wales submitted that such schemes:
...may further exacerbate the glass challenges, as the
unintended consequence could be that, after glass containers are removed for
redemption, the glass remaining in the kerbside bin could be too poor in
quality to be re-used and can only be sent to landfill.[51]
6.54
It was also argued that, although the roll-out of CDS will marginally
increase the recovery of some recyclable materials, it may exacerbate the
market failures in the glass sand and glass bottles arenas.[52]
Mr Spedding, NWRIC, also stated that if there is not a market for the glass
fines[53]
resulting from kerbside collection, then it is likely that stockpiling will
occur.[54]
6.55
Mr Vaughan Levitzke, Chief Executive Officer, Green Industries SA, told
the committee that the implementation of new CDS in Australia has largely been
driven by the community, and noted that the beverage industry has long opposed
the introduction of such schemes. Mr Levitzke stated:
It's probably community pressure, but also NGOs have played a
strong role, particularly in New South Wales. Also I think the beverage
industry probably didn't do itself a great service in terms of the way it
fought container deposits over many, many years. Many of those arguments didn't
hold water—no pun intended![55]
Suggestions for change
6.56
To address challenges for glass recycling associated with kerbside
collection, Owens‑Illinois advocated for the introduction of kerbside glass-only
collection systems. Owens‑Illinois considered this would achieve 'the
single greatest improvement to glass recycling'. It stated that:
Current Beneficiation
Facilities using feedstock from the current kerbside collection system yield
between 30% to 60% glass recoveries. Glass only kerbside collections will
significantly increase the glass recovery to at least 90%.[56]
6.57
Owens-Illinois anticipates that the introduction of glass only
collections would result in the glass delivered to cullet beneficiation plants
under both kerbside collection and CDS being of similar quality. This, in turn,
would 'allow for less capital intensive facilities, reducing the cost of
recycling in the future'.[57]
6.58
In addition to making changes to the ways in which glass is collected
and processed, it was suggested that a range of other policies should also be
implemented. These include:
-
taxes or levies should be applied to virgin aggregates to provide
a level playing field for recycled glass;[58]
and
-
the use of recycled products in new materials, for example,
requirements to utilise a minimum proportion/amount of recycled glass in
aggregate and roadbuilding materials should be mandated.[59]
Mattresses
6.59
In excess of two million mattresses are sold every year. 1.6 to 1.8
million mattresses are disposed of with more than half of these going to
landfill (about 900,000 cubic metres per year of landfill). Other mattresses
are reused, stockpiled or illegally dumped.[60]
It should be noted that with the appropriate collection and processing systems,
mattress are '(almost) fully recoverable'.[61]
6.60
The WMAA noted the importance of source separation and appropriate
collection systems in achieving high recovery rates. It stated that
'mattresses...cannot be recovered from landfill, however where Councils create
separate collection systems, the potential for these to be recycled is greatly
improved'.[62]
6.61
It was also noted that a product stewardship scheme for mattresses is
currently being discussed. Councils supported the inclusions of mattresses in
the scheme so that as much of the material can be recovered and to keep bulky
items out of landfill.[63]
Tyres
6.62
In 2015–16, Australia generated more than 56 million EPUs (equivalent
passenger units) of end-of-life tyres, which equates to roughly two EPUs per
person. By weight, this equates to around 450,000 tonnes of waste material.
This waste material is:
-
recycled domestically (e.g. road construction, tile adhesives) –
10 per cent;
-
exported as tyre-derived fuel – 27 per cent; and
-
sent to landfill, stockpiles, illegally dumped or exported, or
buried in mine sites – 63 per cent.[64]
6.63
Mr Robert Kelman, Executive Officer, Australian Tyre Recyclers
Association (ATRA), told the committee that the greatest barrier to the
sustainable use of used tyres in Australia is the export of whole baled tyres.
Mr Kelman stated that:
There are three principal reasons why we believe that process
is unsustainable. The first is that those tyres carry water, and the World
Health Organization identified that tyres moving around the globe are the biggest
cause of the transportation of mosquito borne diseases that there is, so we
move dengue fever, malaria and other quite dangerous diseases around the world
in tyres because they're black and contained and they sustain water—the perfect
incubator for mosquito larvae. The second reason is that they go to
unsustainable outcomes like dirty pyrolysis operations in Malaysia or India.
The third is that it massively diminishes the ability of the industry in
Australia to develop, because you can buy a baler for $15,000, get a truck and
undercut a legitimate industry when you go to the retailers and collect their
tyres. So it keeps the industry at a very low level.[65]
6.64
ATRA noted the lack of regulation in relation to tyres in Queensland and
WA has allowed rogue operators to undercut legitimate businesses, and to
stockpile or dump waste products. ATRA went on to note that Queensland and
Tasmania have large stockpiles of tyres, with Tasmania having around 1.2
million tyres in stockpiles—the largest in Australia.[66]
6.65
Mr Kelman, ATRA, told the committee that:
The modus operandi, which we've seen again in Queensland, is
that you lease an industrial site, pay maybe a few months in advance to an
unsuspecting landlord, pile the tyres up—and we've got a couple of sites in
Queensland which have over a million tyres each—and then walk away. Or, as I
say, they may mysteriously somehow catch fire. And that means that you're not
spending any money in shredding that material, containerising it and exporting
it. My members pay about $1,100 per 40-foot container to export tyre derived
fuel, so the $2 is the endpoint of their income. If you've got a model where
you can simply stockpile those tyres, you're making quite a lot of money.[67]
6.66
Mr Kelman, ATRA, also noted that eventually illegally stockpiled tyres
'have to be paid for by government to get rid of them'. Mr Kelman highlighted
that the Victorian EPA was forced to fund the removal of a large stockpile of
tyres in Stawell. Mr Kelman stated:
Stawell was the largest stockpile of used tyres in
Australia...Stawell became a massive community issue every year. Every fire
season, they allocated a crew to the site to remain in position on those really
hot, dangerous days in case it did go up because of the enormity of the impact
that that would have. The government eventually spent the several million
dollars to contract one of my members to collect the material, process and
export it and deal with that community opposition.[68]
6.67
A number of submitters noted that, in an attempt to manage end-of-life
tyres, a voluntary, industry-led product stewardship scheme was introduced in
2014. The scheme—Tyre Stewardship Australia (TSA) is administered by tyre
importers in Australia and is supported by a levy imposed on tyre importers,
vehicle manufacturers and miners of a minimum of $0.25 per EPU imported into
Australia.[69]
The Australian Competition and Consumer Commission (ACCC), which has granted
authorisation for the scheme to operate,[70]
has published the following summary of the purpose of the TSA and how the
scheme operates:
The Scheme is an accreditation program that aims to reduce
the amount of end of life tyres (EOLTs) entering the environment via landfill,
illegal dumping or undesirable export, while increasing the recycling rate of
EOLTs...Broadly, the Scheme requires participants to adhere to a series of
general and specific commitments to ensure the environmentally sound use of
EOLTs, to deal only with other accredited participants of the Scheme and to
report data to TSA regularly. The Scheme also imposes a $0.25 tyre levy on
tyres that its participants import into Australia.[71]
6.68
Mr Harford, Equilibrium, told the committee that the bulk of tyre
retailers in Australia now use a Tyre Stewardship Australia accredited member
for the recycling of tyres. Mr Harford explained:
Under the Tyre Stewardship Australia scheme, 25c per
equivalent passenger unit is now charged on every tyre that is sold in
Australia and that goes to Tyre Stewardship Australia to do research and
development. It's a coercive action, and the ACCC has acknowledged it as
such, in that anyone who wants to be a member of Tyre Stewardship Australia can
only use Tyre Stewardship Australia members for any of its activities.
Therefore, the bulk of the retailers of tyres in Australia, passenger tyres in
particular, now have to use a Tyre Stewardship accredited member for their
collection and recycling. As I noted, we actually do audits for Tyre
Stewardship Australia for the recyclers. So those recyclers have to meet a very
high standard and they have to prove that the tyres that they collect in
recycle are actually going to an environmentally responsible end market at the
end of the day. It brings a greater level of accountability and transparency to
those operators and reduces the chance of rogue operators in the tyre space.
While it doesn't fund them directly, it does provide that kind of market force.[72]
6.69
Tyrecycle, however, argued that the TSA has not had the desired impact
on addressing illegal landfilling and dumping because of the voluntary nature
of the scheme.[73]
6.70
The committee was advised that New South Wales is addressing the problem
of tyres with a tracking regime for all end-of-life tyres. Tyrecycle stated
that there is minimal risk of tyres avoiding this system and being illegally
disposed of.[74]
Mr Kelman, ATRA, described the New South Wales tyre regulatory regime as
'leading the way'. Mr Kelman noted that recently, a number of New South Wales
retailers were fined for failing to comply with regulatory requirements.[75]
6.71
Finally, Mr Spedding, NWRIC, suggested that innovative solutions could
be utilised for the recycling of tyres such as a 'pyrolysis process' where
tyres are heated to produce oil, carbon black and metal. The oil can then be
reprocessed and used by vehicles 'within days'.[76]
Stockpiling
6.72
Stockpiling, or the practice of storing large quantities of collected
recyclable material was raised as an issue by a number of submitters. In
particular, the environmental and health risks associated with stockpiled
material were noted. Some submitters called for stockpiling to be made illegal,
while others argued that stockpiling is a commercial necessity for the recycling
industry and which should be managed rather than made illegal.
6.73
Mr Alex Serpo, National Secretary, NWRIC, told the committee that
stockpiles are 'a major concern'. Mr Serpo noted that beyond market conditions,
other causes of stockpiling include:
...rogue operators who will just
collect material, like construction material, put it somewhere and then close
down their company. They're what we call phoenix companies.[77]
6.74
Other submitters stated that the causes of stockpiling include market
forces and commercial gain, transportation and geographic distances, limited
interest from recyclers to commercially service remote communities, and a lack
of appropriate infrastructure available.[78] Stockpiling can also occur
when councils store material prior to collection and removal offsite by
appropriate recyclers.[79]
6.75
Mr Max Spedding, NWRIC, noted the danger associated with stockpiling
combustible material and stated that despite the implementation of safety
measures such as heat sensors, spacing of stockpiles, and fire barriers between
stockpiles and buildings, there have been a number of serious fires. Mr
Spedding described the risk as 'high' when combustible material is stockpiled.[80]
6.76
Submitters commented that, although stockpiling can become problematic,
there are also commercial needs which make stockpiling necessary. For example,
the South Australian Government commented that in regulating stockpiling, there
is a need to balance the genuine need of many businesses and local governments
to undertake some degree of stockpiling (for example, for reasonably
anticipated sales) against excessive stockpiling that can create environmental,
abandonment or unfair competition risks.[81]
Mr Max Spedding, NWRIC, explained that:
The difficulty is that recycling markets are not static. They
rise and fall quite dramatically. When they fall, you accumulate stock, but,
when the market recovers, it needs stock to be able to supply it; otherwise,
you miss out and the market's not reliable. Stockpiling is an inevitable part
of recycling, so a facility needs to have enough space. If it does stockpile
materials, it needs to be done in a proper manner, with the necessary security,
spacing et cetera.[82]
6.77
The Victorian Waste Management Association (VWMA) submitted that
'stockpiles are a necessary part of recycling to ensure constant supply for
processing'. It explained that the 'just in time' business model does not work
in the recycling industry. VWMA also noted that since the 2017 fire at the SKM
Recycling facility at Coolaroo, Victoria, the Victorian EPA and fire services
have enacted guidelines to prescribe storage requirements.[83]
6.78
Similarly, LGNSW submitted that the NSW EPA sets limits on the stockpiling
of waste products to prevent negative environmental consequences. It noted
that there is a view amongst some of its member councils that for some inert
and low risk recyclable materials, it may be desirable to allow stockpiling to
account for fluctuations in the market.[84]
6.79
Mr Serpo, NWRIC, told the committee that industry has proposed a number
of solutions to manage stockpiling including audits, enforcement action and
reporting tools. Mr Serpo stated:
In regard to stockpiles, industry has put forward a number of
solutions. One of them is mass balance reporting, a regulatory tool used
extensively in New South Wales and in South Australia, which basically says
what goes in should come out. Also, we've asked for audits of stockpiles. But
we also think enforcement is important, and that's to shut down the companies
which aren't acting ethically and, in some cases, are acting illegally and just
getting rid of waste in any way they can.[85]
6.80
However, ResourceCo submitted that stockpiling should be made illegal in
all jurisdictions. It argued that where there is no market for a material, it
should be diverted to landfill and levies paid. Operators should not be allowed
to stockpile material for a 'rainy day' with no market in sight as a way of
avoiding a waste levy.[86]
Infrastructure for processing recyclable material
6.81
Submitters highlighted the importance of investment in infrastructure
for the collection and processing of recycled material and diverting waste from
landfill. This infrastructure is needed both to enable regions to participate
in recycling programs and to reduce contamination rates. For example, the South
Australian Government submitted that:
More than $17 million in recycling infrastructure grants has
been provided towards over 150 projects across South Australia. In
metropolitan areas this has supported recycling infrastructure targeting
plastics, organics, mixed waste and e-waste. Funding in regional areas has
supported upgraded and new transfer stations using state-of-the-art
technologies and sorting equipment....in 2002-03, South Australia was diverting
approximately 61% of material from landfill. With the above investment, this
has increased significantly to 81.5% in 2015-16 and total resource recovery
tonnages have nearly doubled. Waste to landfill has reduced by 29% this period.[87]
6.82
The Shire of Exmouth highlighted the need for infrastructure to enable
recycling in regional areas. The Shire explained that 'as an isolated regional
area not on a standard transport route there are challenges with being able to
participate and support a recycling program'. It submitted that the cost of
transporting recyclables the necessary 1200 kilometres to a recycling
collection point negates any income produced by collecting the material, and
therefore recycling becomes 'unsustainable'. As such, it supported initiatives
which recycle and reuse material within the town but highlighted the need for
funding and research into opportunities for small scale recycling initiatives
that create products which can be used within the local area.[88]
6.83
The Shire of Exmouth also stated that certain regional areas could
be identified as 'recycling nodes' to collect and receive material from other
non-metropolitan areas. It submitted:
These nodes scattered throughout the state could be areas identified
as potential locations to receive and process recyclable goods outside of the
metro areas. They could then be supported to build the infrastructure to take
and/or process the recyclables.[89]
6.84
The committee received evidence that to reduce the contamination rate of
recyclable materials, investment in material recovery facilities (MRFs) is
required. Reducing contamination rates reduces the amount of product being sent
to landfill, supports domestic markets for product, and ensures that material meets
international regulatory requirements for the export to countries such as
China. Mr Stuart Garbutt, Director, Operations, Re.Group, told the committee
that in order to upgrade material recovery facilities (MRFs) funding of between
$5 million and $30 million would be required. Mr Garbutt explained:
A brand-new 10,000 to 15,000
tonne MRF is $5 million to $6 million; the 100,000 to 200,000 tonne MRFs are
$25 million to $30 million. I believe the one in Melbourne is reported to be
somewhere in the vicinity of $40 million to $50 million. I would dare say that
these newer MRFs probably don't need as much capital as some of these older
regional MRFs. You would be probably looking at packages of $1 million to $2
million in regional areas, $3 million to $5 million in the cities.[90]
6.85
Mr Garbutt, Re.Group, also noted that upgrades are a relatively
short-term project with an implementation period of between four and eight
months.[91]
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