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Circular Economy. Is it Enough?

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  • Loughborough University, London

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Circular Economy:
Is it enough?
Dr. Sharon Prendeville
Chris Sanders
Jude Sherry
Filipa Costa
March 11, 2014
029 2064 7034
info@edcw.org
www.edcw.org
2
Circular Economy: Is it enough? 1
1.Introduction
2. Dening the Circular
Economy
3. Comparing Ecodesign and
the Circular Economy
4. Challenges to Closing the
Loop
5. Alternatives to the
Circular Economy
6. Conclusion
References
Contents Page 3
Page 3
Page 5
Page 8
Page 11
Page 12
Page 13
Images produced by Richard Harlow
Circular Economy: Is it enough?
2
Ecodesign is a strategic design
management process that
considers the full life-cycle
environmental impacts of
packaging, products, processes,
services, organisations and
systems. It can identify layers of
waste and layers of value.
3
1. Introduction
Recently, the concept of the circular
economy has gained traction in industry
and policy as a pathway to deliver



While not a new concept clearly its
widespread appeal has never been
greater. This is because industry at
large recognises the need to transition
from a linear take-make-dispose
model of production and consumption.
A key driver for this is increasing
awareness of resource scarcity, risks
to business competitiveness and the
potential impact this may have in
the long-term. In a recent UK based
survey of 435 companies in total
72% indicated that they are looking
to engage with waste management
providers to collaborate and implement
closed loop systems (Edie, 2013).
Purported incentives and cost reductions
seen through circular economics are

gains claimed through implementation
of closed loop manufacturing systems.
One report commissioned by the Ellen
McArthur Foundation (2013) found that
adopting a circular economy approach
could save European manufacturers
$630bn a year by 2025. As global
demand for sustainable solutions reaches

unparalleled prospects for industry.
This brief position paper discusses the
importance of an ecodesign perspective
within a circular economy. Firstly,
we set out the main similarities and

circular economics. Following this we
discuss key challenges in implementing
circular economy principles within

alternatives to the circular economy

for long-term environmental
protection and social wellbeing.
2. Circular Economy or
Closing the Loop?

between the concepts of circular
economy and closed loop manufacturing

academic and grey literature.

how both concepts involve the reverse

remanufacturing, repair, recovery,
recycling and reuse. And this is widely
accepted.

economic growth, promote renewable
energy, the notion of ‘restoration’
and the ‘replenishing’ of resources.
Importantly, the concept of closed loop


Ecodesign Centre’s view of the circular
economy as a broader agenda than that
of closing the loop.
However, though broader, it is not
entirely clear how a circular economy
approach could restore or replenish
natural resources. It is true that
circularity can reduce the need for raw
Circular Economy: Is it enough? 4
Ecodesign is a strategic
design management
process that considers
the full life-cycle
environmental impacts of
packaging, products,
processes, services,
organisations and
systems. It can identify
layers of waste and layers
of value.
Circular Economy: Is it enough?
4
material extraction thus alleviating
stress on the natural environment. But

Finally, it is essential to recognise that
circular economics and closed loop
approaches advocate for material and

Figure 1. Closed Loop Production System (adapted from the OECD, 2009)
environmental impact reduction. It is
also essential to recognise that there
are environmental impacts resulting
from product life cycle stages other than
raw material extraction (this includes
environmental impacts of recycling
processes). In Section 2 we discuss the
role of ecodesign in bridging this gap.

3. Comparing Ecodesign
and the Circular Economy
This section introduces ecodesign and
the strategic and operational alliances
between ecodesign and the circular

these concepts begin to diverge.
Ecodesign is a strategic design
management approach to reducing
environmental impacts across the
Circular Economy: Is it enough?
5
whole product life cycle. The European

into account all of the environmental
impacts of a product right from the
earliest stage of design. In particular,
this avoids uncoordinated product
planning (for example, eliminating a
toxic substance should not lead to higher
energy consumption, which on balance
could have a negative impact on the
environment.” Traditionally, ecodesign

evolved to include services and systems
(see Sherwin and Evans, 2000).

Ecodesign strategies (such as design for
recycling, design for disassembly) can
facilitate closed loop remanufacturing
while also making ecodesign products
suited to servicing, leasing and hiring
options.
This means that like the circular
economy model, ecodesign often
requires business model innovation
to realise value invested earlier in the
design stage.
Circular Economy: Is it enough?
6
Operational Synergies
The practical relationship between
ecodesign and the circular economy
is acknowledged (e.g. Besch 2005).
Importantly, a large body of literature on
ecodesign practices exists including case
studies, ecodesign methods, strategies
and a substantial number of ecodesign
tools. This existing body of practical

support the implementation of a circular
economy.
Circular Economy: Is it enough? 7 8
Strategic Overlaps
There are strategic alliances between
ecodesign and the circular economy.

an operational concept, whereas in
our experience ecodesign requires
strategic decision-making. This is
because business model redesign and
cross-sector collaboration are required
to fully implement and therefore

Similarly, the core aim of the circular
economy is to extract ‘the maximum
value from material while in use, then
recovering and regenerating’ waste
requiring a rethink on how to design
products including product systems and
businesses.
Importantly, this overlap sees
both concepts promote business
model innovation, reverse
logistics, intersectoral cascades
and cross-sector collaboration.
Combined, these aspects require
fundamental changes in industrial
infrastructure, which is a key barrier
to implementation of ecodesign and
circular systems.
Diering Approaches
Ecodesign is central to closed
loop manufacturing and product
designers are at the forefront of
its implementation. While product
designers play a central role, there are

involves. Some authors are proponents

In contrast, McDonough and Braungart
(2007) have explicitly criticised resource

techniques. Rather, through their Cradle
to Cradle design protocol (C2C) they

with long-term growth and economic
prosperity. With the assumption that
growth is good, the framework advocates
for consumption, based on short-term
product life spans. It promotes new

which seek to design and manufacture
within closed-loop cycles. Products and
product parts are made up of biological
or technical nutrient materials, which
are recovered and reutilised within their
respective biosphere or technosphere
(McDonough and Braungart 2007). Other

basis for ‘biological’ nutrients and their

Reijnders 2008).
In addition, MBDC have also criticised


toxicity aspects of products. Instead,
they propose material toxicity testing
as a preferable approach.Ideally, a
combination of both approaches is
desirable.
Ecodesign needs to be informed
by LCA results to allow design
practitioners and other stakeholders
to take action. In terms of material
toxicity testing, Ecodesign Centre
proposes that material formulators
should undertake material toxicity
testing (rather than individual
Circular Economy: Is it enough?
8
Figure 2 - Relationship between
Ecodesign and Circular Economy
companies undertaking Cradle to Cradle

basis). Taking a twofold approach would

across the product life cycle.
Fundamental Distinctions
It has long been stated that 80% of a
product’s environmental impacts are
determined at the design phase (Graedel
and Allenby, 1995). As previously
discussed, Table 1 illustrates how circular



prioritise total environmental impact
reduction*. For example, Sherwin and
Evans (2000) state ecodesign is ‘the
design of a product, service or system
with the aim of minimising the overall
impact on the environment’. This
distinction is important because resource

have environmentally negative rebound

According to McKinsey (2011) circular
economics means ‘meeting current
demand/consumption needs’ (see
Table 1). In contrast, we believe society
over consumes. Design has the power
to fundamentally change, for the
better, how society behaves and how

ecodesign methods question and assess
the validity of the product need, right

method).
4. Challenges to Closing
the Loop
The literature discusses a number of
challenges or barriers to achieving the
circular economy. Here, we discuss these
challenges according to three groups:
challenges related to practical issues
Design has the power to
fundamentally change,
for the better, how
society behaves and how
people consume.
of implementation such as technical,
economic and infrastructure problems;
challenges to do with behavioral change;

Ecodesign Centre perceive within the
circular economy model.
Practical issues surrounding the circular
economy are frequently cited and many
of these are also relevant to ecodesign.

practical problems. This is followed by
a discussion of issues that are more

economy.
4.1 Practical Issues
Supply chain management,
Logistics, Pricing and
Investments
Each of the possible routes for
maintaining materials in a closed system
has its own problems. For example,
companies struggle to implement
functioning distribution networks that
bring products from locations scattered
nationally or internationally to a central
depot. In addition, few regions have
the infrastructure in place to collect
unwanted products. These issues are
exacerbated by a limited ability to
predict quantities of returned products.
Furthermore, there is often poor market
demand for reused and remanufactured
products, in part related to consumer
perceptions of these products, their
quality and functionality. Other

binding contracts that may constrain
improvements to business operations,
Intellectual Property (IP) rights which
restrict information sharing along the
supply chain and issues around the
legalities of selling remanufactured
products (Kuo 2011; Souza 2012;
Vanegas et al. 2011).
In addition, the economic viability
and environmental impact reduction
through schemes to promote reuse
and remanufacturing (such as ‘product
take-back’) are dependent on a number
of factors. Most importantly, product
designs need to be durable enough to
withstand remanufacturing and multiple
cycles of use and Original Equipment
Manufacturers (OEM) need to be willing
or incentivised to take the product back

and service models are suited to non-
energy consuming products during the



impacts). Products also need to be
manufactured with standardised
materials to generate high value and
pure recyclate thus incentivising product
take-back (Kuik et al. 2012; Grant &
Banomyong 2010). Some businesses
may have also already invested large
amounts of money in machinery and
infrastructure for their production
processes, making required changes
uneconomical. Others may struggle
to raise initial investment funds to
implement improvements.
Businesses also need appropriate

remanufactured products. This is an
active and complex area of academic

al., 2009; Shi et al., 2011). One particular
Circular Economy: Is it enough?
9 10


http://www.ecodesigncentreorg/en/resources/

best-practice
issue is known as the ‘cannibalisation’


life products from a business, switch
to a lower price remanufactured one
(purchased from the same business), and

risk scenario.
Recycling and Externalities
Economic, infrastructure and technical

of recycling for some materials. For
example, although technically possible,

perform closed loop recycling for some
types of plastic due to the mixing of
contaminants such as ink and metals
in the recyclate (Hopewell et al., 2009).
Therefore, plastics are often down cycled
into products that require a lower quality
material. There are also challenges for
the recovery and recycling of metals.

currently exist for metals such as
aluminium and steel, the recovery rates
for other metals such as Rare Earths are
much lower (Ecodesign Centre Critical

recovery of these metals include very
low quantities in products, making it


of one metal type versus another in the
recovery process (Hagelüken & Meskers,
2009). A major challenge is ensuring that
metals from waste products enter into
the correct recycling pathways. Currently
a large quantity of end-of-life products
are traded abroad and processed

the environment and human health.
Andersen (2007) suggests that the
circular economy cannot recycle
materials in perpetuity, noting that
beyond a certain point recycling will


related to a problem with the true cost
of goods and services where the external
costs to the environment or ‘externalities’
are not included. This results in
goods and services being priced very
cheaply, making recycling and reuse
of materials uneconomical while virgin
material supplies are still plentiful.
This phenomenon prevails despite the
environmental impacts associated with
their production.
For these reasons ecodesign prioritises
long life durable products that can be

with limited additional process. This is
particularly important because easily
disassembled products with high
amounts of recycled content (therefore
suited to recycling) can often have
compromised durability (Prendeville
2014).
Behavior Change Issues and
Overconsumption
Achieving a circular economy requires
action from and communication
between a variety of stakeholders
including politicians, business managers,
investors, research scientists, designers
and everyday consumers. Changing
current modes of production and
consumption requires behavior change
Circular Economy: Is it enough?
10

at: http://ecodesigncentre.org/en/resources/

amongst these groups. A large amount
of research has been undertaken on
pro-environmental behavior change

One major challenge is altering peoples’
habits to avoid activities that are
unsustainable (Kollmuss & Agyeman,
2002). On a business level, change also
requires leadership from owners and
managers.
Of particular concern in the literature,
linked both to general consumers
and businesses, is the occurrence of



have been shown to lead to increases
in consumption, known as the Jevons
Paradox, and therefore greater
cumulative environmental impacts
(Polimeni et al., 2009) . Discussing these
phenomena with an economist uncovers



are gained. Therefore, focusing solely

products, threatens the sustainability of
the circular economy.
More Fundamental Challenges
to the Circular Economy
There are also limitations to recycling
and growth of the economy based on
material use that can be understood
from the second law of thermodynamics
(Ayres, 1998). This law recognises that
entropy (a measure of disorder) in an
isolated system always increases until
it reaches a state of thermodynamic
equilibrium (maximum entropy). If the
economy is considered as a closed
thermodynamic system , then materials
cannot be cycled continuously without
inputs of energy external to the system.
In the short-term limits to economic
growth based on thermodynamics
will not be an issue. Supplies of many
materials currently remain plentiful.
However, rapid economic growth that
is decoupled from environmental
degradation may be limited by the
environmental damage caused by mining
materials and an inability to source clean,
renewable energy at competitive prices.
In the longer-term thermodynamic limits
may mean that the circular economy
alone will not be a solution for a truly
sustainable society.
5. Alternatives to the
Circular Economy
There are other economic models that
have been suggested that are less
supportive of economic growth, due to
the limitations described above. But also
because there is evidence to suggest
that beyond a certain point economic
growth based on material use does little
to increase human well being (Jackson,
2009). Perhaps the most frequently cited
alternative model is the steady state
economy, where the size of the economy
is stable. For a steady state economy to
be achieved the throughput of materials
in an economy would need to remain
fairly constant, as would population.
A limit would then have to be set on
resource inputs to allow for a level of
economic activity that ensures good
Circular Economy: Is it enough?
11 12
1.Earth is a closed system but not an isolated system; energy inputs
can come from the Sun
living standards for the population while
maintaining the natural environment.

measures may then allow for continuous
improvements in quality of life to be
made.
The other commonly cited suggestion
is sustainable degrowth. As the name
implies, this model aims for planned
degrowth of the economy to ensure
society lives within environmental limits.

from the steady state economy, some
commentators see the end route of
sustainable degrowth as a steady state
economy (Kerschner, 2010).
Moving towards a steady state economy
or achieving sustainable de-growth both
represent major challenges for society.
One of the largest barriers for either is
the fact that population would have to
remain constant or decrease. Currently
population is predicted to rise, reaching
around 9 billon people by 2050 (United

how resource inputs into the economy
could be limited and controlled on a
global scale and is important to note
that many countries still need economic
growth to lift them out of poverty.
Despite these challenges, a steady state
economy has long been suggested as the
endpoint of development of an economy
(Kerschner, 2010). Although it may be

should perhaps be a goal to strive
towards. The circular economy could be
used as a route to achieve this. Despite
it being a concept that is supportive of
economic growth, a circular economy
implemented using ecodesign principles
will allow for better quality of life while
reducing environmental degradation.
These changes may make it easier to
achieve a steady state economy in the
future, while being less at odds with
political and economic systems of the
present.
6. Conclusion
This brief paper discusses the circular
economy model from the perspective of
ecodesign. In doing so, Ecodesign Centre
sets out important issues that need to
be addressed to ensure environmental
and social sustainability within a circular
economy model.

to industry, coupled with advocating
for continual economic growth and
consumption, poses long- term risks
to the environment and to society. And
therefore risks the sustainability of the
circular economy.
The proven success of the circular
economy model is its ability to awaken
and mobilise industry. It is clear that the
circular economy is instrumental to drive
forward necessary societal changes in
modes of production and consumption.
With greater alignment of environmental

unparalleled opportunity for societal
transition.
Circular Economy: Is it enough?
12
There is evidence to
suggest that beyond a
certain point economic
growth, based on
material use, does little
to increase human well
being (Jackson, 2009).
References
Andersen, M.S., 2007. An introductory
note on the environmental economics
of the circular economy. Sustainability

Ayres, R., 1999. The second law, the
fourth law, recycling and limits to
growth. Ecological Economics, 29(3),

linkinghub.elsevier.com/retrieve/pii/
S0921800998000986.
Besch, K., 2005. Product-service

opportunities on the European market.
Journal of Cleaner Production, 13(10-

Braungart, M., McDonough, W. &
Bollinger, A., 2007. Cradle-to-cradle
design: creating healthy emissions - a

and system design. Journal of Cleaner

Chi Kuo, T., 2011. The study of
production and inventory policy of
manufacturing/remanufacturing
environment in a closed-loop
supply chain. International Journal
of Sustainable Engineering, 4(4),

Dobbs, R. et al., 2011. Resource
Revolution: Meeting the world’s energy,
materials, food, and water needs,
Edie, 2013. Closing the loop: risk or
reward?,
Ellen MacArthur Foundation, 2013.
Towards the Circular Economy:
Economics and business rationale for an
accelerated transition,
European Commission, 2012. Ecodesign
your Future: How Ecodesign can
help the environment by making
products smarter, Available at: http://
ec.europa.eu/enterprise/policies/

brochure_ecodesign_en.pdf.
Feng, F. et al., 2013. Evaluation of

Circular Economy with Intuitionistic

& R. Dou, eds. The 19th International
Conference on Industrial Engineering
and Engineering Management SE -
36. Springer Berlin Heidelberg, pp.

org/10.1007/978-3-642-38391-5_36.
Graedel, T.E. & Allenby, B.R., 1995.

Prentice Hall.
Grant, D.B. & Banomyong, R., 2010.
Design of Closed-loop supply chain and
product recovery management for fast-
moving consumer goods: The case of a
single use camera. Journal of Marketing,

Hagelüken, C. & Meskers, C., 2009.
Technology challenges to recover
precious and special metals from
complex products,
Hislop, H. & Hill, J., 2011. Reinventing the
wheel A circular economy,
14
13 Circular Economy: Is it enough?
Hopewell, J., Dvorak, R. & Kosior, E.,
2009. Plastics recycling: challenges and
opportunities. Philosophical transactions

B, Biological sciences, 364(1526),

pubmedcentral.nih.gov/articlerender.fc
gi?artid=2873020&tool=pmcentrez&re
ndertype=abstract [Accessed December
15, 2013].
Jackson, T., 2009. Prosperity without
growth? The transition to a sustainable
economy.,
Kerschner, C., 2010. Economic de-growth
vs. steady-state economy. Journal of

Available at: http://linkinghub.elsevier.
com/retrieve/pii/S0959652609003473
[Accessed December 12, 2013].
Kollmuss, A. & Agyeman, J., 2002.
Mind the Gap : why do people act
environmentally and what are the
barriers to pro-environmental behaviour.
Environmental Education Research, 8(3),

Kuik, S.S., Nagalingam, S. V. & Amer,
Y., 2012. A Framework of Product
Recovery to Improve Sustainability in
Manufacturing. Advances in Mechanical
Engineering, 2(1).

2009. Pricing used products for
remanufacturing. European Journal
of Operational Research, 193(2),

linkinghub.elsevier.com/retrieve/
pii/S0377221707011289 [Accessed
February 24, 2014].

environmental behaviour: existing
evidence and policy implications.
Environmental Science & Policy, 11(5),

linkinghub.elsevier.com/retrieve/
pii/S1462901108000312 [Accessed
December 30, 2013].
Organisation for Economic Co-operation
and Development, 2009. Sustainable
Manufacturing and Eco-Innovation:
Framework, Practices and Measurement,
Available at: http://www.oecd.org/sti/
inno/43423689.pdf.
Polimeni, J.M. et al., 2009. The Myth of




electronic waste management system
in Spain. Journal of Cleaner Production,

linkinghub.elsevier.com/retrieve/pii/
S0959652611004781 [Accessed April 9,
2012].

wastes consisting of biological nutrients
good or healthy? Journal of Cleaner

Available at: http://www.sciencedirect.
com/science/article/B6VFX-4S4J6J0-

6b08 [Accessed May 18, 2010].
14 Circular Economy: Is it enough?
Sarkis, J., 2001. Manufacturing’s
role in corporate environmental
sustainability - Concerns for the
new millennium. International
Journal of Operations & Production

Available at: http://www.emeraldinsight.
com/10.1108/01443570110390390.
Sherwin, C. & Evans, S., 2000. Ecodesign

International Symposium on Electronics

Shi, J., Zhang, G. & Sha, J., 2011. Optimal
production and pricing policy for a closed
loop system. Resources, Conservation

Available at: http://linkinghub.elsevier.
com/retrieve/pii/S0921344910001382
[Accessed February 24, 2014].

Chains: A critical Review, and Future
Research. Decision Sciences, 44(1).

pro-environmental behaviour: An
integrative review and research agenda.
Journal of Environmental Psychology,

linkinghub.elsevier.com/retrieve/
pii/S0272494408000959 [Accessed
December 11, 2013].
Umeda, Y. et al., 2012. Toward integrated
product and process life cycle planning—
An environmental perspective. CIRP
Annals - Manufacturing Technology.
Available at: http://linkinghub.elsevier.
com/retrieve/pii/S000785061200203X
[Accessed July 2, 2012].

2300,
Vanegas, P. et al., 2011. Information
exchange requirements for cradle to
cradle implementation in an industrial


Cycle Sustainability Management. Berlin.
15 Circular Economy: Is it enough? 16
Circular Economy: Is it enough? 16
We make ecodesign happen
through developing and
delivering collaborative multi-
sectoral ecodesign projects.
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... (1) In terms of eco-design, Prendeville et al. (2014) have demonstrated that this stage plays a central role in CE to enhance its advantages (primarily focusing on resource utilization), as eco-design is designed to reduce all environmental impacts in the product life cycle. Since eco-design takes into account all the environmental impacts of a product since the early stages, it has the potential to improve the CE approach by facilitating the use of materials and resources (Prendeville et al., 2014;Geissdoerfer et al., 2017). ...
... (1) In terms of eco-design, Prendeville et al. (2014) have demonstrated that this stage plays a central role in CE to enhance its advantages (primarily focusing on resource utilization), as eco-design is designed to reduce all environmental impacts in the product life cycle. Since eco-design takes into account all the environmental impacts of a product since the early stages, it has the potential to improve the CE approach by facilitating the use of materials and resources (Prendeville et al., 2014;Geissdoerfer et al., 2017). ...
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... In addition, Sebastian [77] argues that the inadequacy of BIM's design to incorporate such cutting-edge technology makes it impossible to apply it for projects of this type due to poor coordination and preparation of contract procedures. Since BIM implementation must be included in the contract from the outset, it is not acceptable if a project is not appropriately coordinated and the processes are not well stated [78]. As a result of the necessary tweaks before BIM can be widely implemented, several companies have avoided it. ...
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... Companies can minimize emissions and other environmental damages through the principle of reuse, while they can diffuse reuse principles through remanufacturing products, increasing user demand to purchase reused and remanufactured products. Furthermore, the companies should produce durable goods unless they are not suitable for multiple cycles, while there is a necessity to market reused products [47,63]. ...
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... This existing body of practical ecodesign knowledge is beneficial to support the implementation of a circular economy. According to Prendeville (2014) ecodesign strategies (such as design for recycling, design for disassembly) can facilitate closed loop remanufacturing while also making ecodesign products suited to servicing, leasing and hiring options. This means that like the circular economy model, ecodesign often requires business model innovation to realise value invested earlier in the design stage (Fig.4). ...
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The literature on blockchain technology and circular economy is at a nascent stage, with only initial limited and superficial recognition of the possible role blockchain may have in supporting circular economy laws and policies. This paper contributes to this emerging area by exploring the regulatory opportunities and challenges for adoption of blockchain for circular waste management. In particular, through a mixed methods approach combining empirical and doctrinal research, this paper presents initial findings on: (1) the current role of blockchain within the legal landscape on circular economies; (2) the regulatory barriers of blockchain application to circular economies; and (3) opportunities of blockchain in supporting regulatory mechanisms promoting circularity.
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Product recovery operation is widely recognised and practiced as an ecological alternative for end-of-life products processing that promotes the utilisation of returned products, components and materials. 6R (reduce, reuse, recycle, recover, remanufacture, redesign) incorporation is a proactive practice that primarily focuses on the improvement of product, process and system levels along supply chains and makes the returned product economically and environmentally viable. However, conventional product returns policy and strategy that has its limitation on measureable criteria for product recovery operations. In this paper, a framework of supply chain process of returns management is proposed to describe the dynamics of product recovery operations within multiple product lifecycle stages from pre-manufacturing, manufacturing, use and post-use. Future research should concentrate on sustainable manufacturing activities to improve sustainability of supply chain networks .
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