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Making the most of industrial wastes:
strengthening resource security of
valuable metals for clean growth in the UK
Industrial wastes have the potential to
contribute towards the UK’s ambition for clean
growth. This policy note will highlight where
policy intervention can promote circular
economy approaches in industrial waste
management.
Overarching
recommendation
The UK Government should aim to develop
integrated policies that unlock the potential of
resource recovery to contribute to clean
growth, create social benefits and maintain
environmental protection. The current
regulatory framework for industrial wastes was
not designed with the circular economy in mind.
In order to design policy and regulation that
enables the potential for resource recovery
from such wastes, better collaboration between
policy makers, industry and academia is
essential.
§In order to work towards the aims set out in the
Industrial and Clean Growth strategies the UK
needs to reduce its reliance on finite resources
and those from politically sensitive areas. The
UK government has committed to clean growth
and decarbonisation of the energy system,
requiring development and growth of the green
technology sector . The Industrial and Clean
1,2
Growth strategies aim to see the UK maximise
capabilities in the design, development and
manufacture of electric vehicles, offshore wind
and batteries. These technologies require
supplies of metals including lithium, rare-earth
metals, vanadium, cobalt – many of which we
currently 100% import . Also the global output of
3
these critical metals is concentrated in only a
number of countries; for instance, China
produces 90% of rare earth metals and over 50%
of cobalt is produced in Congo . This has given
4
rise to concerns over the potential for resource
nationalism restricting supply of crucial
materials .
5Extraction of metal resources from
industrial wastes in the UK can contribute to a
more secure and sustainable source of these
valuable materials6(Table 1).
§A shift to renewable energy will be associated
with a shift from one non-renewable resource
(fossil fuels) to another (metals and minerals) .
7
In addition to less common metals highlighted
above, low carbon infrastructure will require large
quantities of materials such as iron, copper, zinc
and aluminium. The negative environmental and
social impacts of acquiring the materials required
for clean growth infrastructure must be
minimised in order to realise the benefits of a
transition to low carbon technologies. Strategies
for this include designing products and
infrastructure for reuse and recycling, and
ensuring that metals already in the supply chain
(e.g. in electronic goods) are recycled .
8The
recovery of metals from industrial wastes
Why resource recovery
from industrial wastes?
§Waste materials from the extractive and
manufacturing sectors have been described as
‘anthropogenic ores’ reflecting their potential
supply of valuable metals. These include wastes
from refining steel and aluminium, and metal mining
industries.
§Resource recovery from wastes can result in social,
environmental and economic wins particularly when
using low cost, low environmental impact
technologies.
§Maximising resource recovery from these
anthropogenic ores will improve the UK’s resource
security. Resources from wastes can contribute to
the supply of valuable metals and materials needed
for clean growth, many of which are currently 100%
imported.
§Metals are essential for the production of wind
turbines, batteries, solar panels and a multitude of
electronics. These resources must be obtained
sustainably if the objectives of clean growth are to
be realised.
§Increased efficiency in the use of resources,
including recovery from wastes, can contribute
towards reductions in the use of raw materials from
finite sources.
§Reducing raw resource extraction will minimise the
associated negative environmental impacts and
carbon emissions.
§The growing focus on resource efficiency and the
development of increasingly coherent plans across
Government is welcomed, but policy and regulation
must adapt to facilitate the strategic economic
benefits of resource recovery as well as providing
environmental protection.
Resource recovery for clean growth
Recovered metals for constructing
low-carbon infrastructures including
lithium, copper, zinc, and tin
Recovered metals essential for clean
technologies including vanadium,
cobaltrare earth elements and
Historical Mine
Workings
Acidic waters
Toxic Metals
Mine Waste
Alkaline waters
Toxic Metals
Industrial Wastes
from Incineration,
Steel and Aluminium
Production
Currently require
long-term
management
and containment
provides an additional supply of metals from UK
sources, reducing demand on raw material use.
§A move to circular economy approaches could
result in job creation in the historic industrial
areas of the UK where unemployment is
currently high9. Resource recovery from
industrial wastes could promote the development
of new recovery businesses, as well as stimulating
innovation in industrial areas of the North East10
and Wales . There is an additional benefit in the
11
proximity of current and historical industrial
wastes to the green technology industries that
require the extracted metals. The Clean Growth
strategy highlights the North East region for
wind turbine production and the West Midlands
for development of electric batteries . Both
2
these regions have a legacy of industrial wastes
containing the valuable metals required in the
clean industries of the future.
§Resource recovery has benefits across
environmental and social domains, primarily
driven by reductions in the use of raw
resources12. The use of primary resources has
negative environmental and social impacts, and
there is a growing recognition that this should be
factored into the cost of materials and goods in
order for a circular economy to be realised .
13
There is a need to stimulate the secondary
resources market in order to encourage
investment and growth of the sector. This could
be through internalising the real societal and
environmental costs of primary extraction into
the costs of materials. Many government
departments currently focus solely on economic
metrics , this needs to be replaced by new
14
modelling approaches that integrate values
across social, environmental, economic and
technical domains if we are to transition to a
circular economy.
Table 1: The potential contribution of a number of UK wastes to the annual UK import of metals. The % contributions presented
in this table are based on estimates from RRfW publications where the assumptions regarding recovery efficiency and
11,15
concentrations of metals are described. Import data for metals is based on 2014 figures and does not account for how the
4
import of materials is likely to change as demand for certain metals increases.
*Data is based on a study of only 14 sites of the 8000 disused sites estimated across England and Wales alone11
**There are promising prospects for lithium extraction from certain mine wastes (for instance china clay wastes in the SW England)
although estimates of potential reserves are not currently available.
*** Market values calculated based on metal prices and exchange rate for 12 Apr 2018. Prices taken from London Metal Exchange
(cobalt, copper, tin, lead), Infomine.com (Ferro vanadium) and Metalary.com (lithium).
Metal
UK Waste Vanadium Cobalt Lithium Copper Tin Lead
Steel slag 49% 0.8%
(annual production)
Steel slag 638% 11%(legacy waste)
Fly ash 11%(annual production)
Fly ash 132%(legacy waste)
Mine tailings * ** 2.78% 1.82% 1.34%(legacy waste)
Market value of 100% £4.2 £293.5 £9.3 £98.2 £64.5 £219.2
annual import (million £)***
The development of technologies and infrastructure
for reducing carbon emissions associated with our
energy systems is key component of the UK (and
global) ambition for clean growth. Technologies
such as solar farms, wind turbines and electric
vehicles have a high demand for metals and
materials. These resources must be obtained
sustainably if the objectives of clean growth are to
be realised. Metals required include:
Vanadium: emerging metal in the production of
long-lived batteries for commercial energy storage
and a key component in the production of light-
weight steel (for use in wind turbines and electric
cars).
Lithium: in high demand for batteries required for
electric cars, home energy storage as well as
personal electronics.
Rare Earth Metals: metals required for technologies
including solar panels, wind turbines, batteries and
energy-saving light bulbs. Although not technically
rare, supply of these elements is controlled by only a
handful of other countries.
Metals for clean growth
Opportunities for
resource recovery from
industrial wastes
§Resource extraction from industrial residues can
provide simultaneous economic, social and
environmental benefits. Environmental and
social benefits occur both upstream due to the
replacement of raw material extraction and
downstream through the remediation of wastes
which otherwise can pose risk to environment and
human health . Many of the metals targeted for
12,15
recovery are hazardous and can leach into the
aquatic environment or carry as dust into the
atmosphere. UK regulations protect
environmental and human health, which result in
the need for long-term management of wastes
such as steel slag and mine tailings. Despite
protective regulation, chronic pollution is
associated with industrial wastes in the UK .
11,16
The longevity of such pollution risks can result in
issues with responsibility for management when
companies close or ownership changes .
10
Adoption of resource recovery techniques can
accelerate the decontamination of industrial
wastes and provide a revenue stream to
industry, along with contributing to reductions
in the UK reliance on primary resources.
Resource Recovery
from Waste programme
'Resource Recovery from Waste' is an academic
research programme funded by the Natural
Environment Research Council, Economic and Social
Research Council and DEFRA, and envisions a
circular economy in which waste and resource
management contribute to clean growth, human
well-being and a resilient environment.
The programme develops technologies to exploit
the resource potential of industrial wastes.
Research projects spanned a number of different
waste streams including the recovery of metals
from wastes resulting from steel and aluminium
production, and metal mines. These industries
have a legacy of waste material for which
environmental protection measures are required for
decades.
§There is potential to extract valuable metals in
significant quantities from industrial wastes,
including those from steel making, aluminium
production and incineration .
6,15 (Table 1) In the UK
there are considerable quantities of historical
wastes produced through decades of industrial
activity, as well as ongoing production of steel
wastes and increased production of incinerator
ash from energy from waste facilities. These
industrial wastes represent a stockpile for future
resource recovery.
§Resource recovery techniques can incentivise
environmental remediation by off-setting the
cost with the metals recovered .
11 Mine wastes do
not hold the answer to securing a long-term
supply of more commonly used metals (copper,
lead and tin) (Table 1); recycling has more impact
here. However, where mine wastes are resulting in
environmental contamination, resource recovery
techniques can accelerate remediation processes;
the cost of which can be off-set by the value of the
metals recovered .
11 Resource extraction from
mine wastes has been a focus of projects across
the RRfW programme.
§Some mine wastes are sources of metals that
are now extremely valuable for modern
technology. For instance, there is potential for
lithium extraction of china clay wastes and from
historic tin mines in South West England.
The programme is developing technologies that
minimise physical disturbance of these wastes and
utilise low-impact, low-cost and low-energy
techniques to maximise the environmental and
social benefits of resource recovery.
Technologies under development in the programme
include:
§Using more environmentally-friendly approaches
to dissolving metals from wastes. This leads to
the formation of metal-rich solutions (leachates)
from which metals can be recovered.
§The use of bacteria, engineered materials
(nanomaterials) and ion-exchange resins to
selectively adsorb metals from leachates
produced.
For more information visit: www.rrfw.org.uk
§To promote a circular economy, the current
regulatory framework for industrial waste
needs to be redesigned. Regulation relating to
the industrial wastes discussed in this policy note
focusses primarily on environmental and public
health protection. There is a need to extend the
focus to supporting the opportunities offered by
resource recovery . For example, for steel
10
production the EU directive on Integrated
Pollution Prevention and Control requires
facilities to have permits specifying emission
limits, monitoring regime and Best Available
Techniques. Whilst these environmental controls
are essential, the recognised Best Available
Technique for steel slag residue in the UK
revolves around safe handling, storage and
preparation for bulk reuse, with no option for
resource recovery .
10 Discussions are needed to
determine where current UK regulation around
end-of-waste for materials are limiting
opportunities for resource recovery (the EU
Circular economy package already highlights the
need for streamlining provisions on by-products
and end-of-waste status ). Such discussions will
17
require consultation between policy makers,
regulators, relevant industries and researchers in
order to identify opportunities and barriers to
implementation of emerging technology .
13
§Assessing the full life cycle impacts of resource
acquisition is complex but essential for
determining which technologies and
approaches are appropriate for the situation6,18.
This approach allows for a better understanding
of the potential negative impacts and positive
benefits resulting from decisions around
resource acquisition and use. For example,
historical mine waste sites in the UK can have
cultural and environmental importance, including
providing rare natural habitats, leisure and
educational services . These factors should be
11
balanced against the potential social value of
obtaining a resource from within the UK, the
benefits for local employment and reduced
reliance on primary resources from politically
sensitive countries.
Implications for policy and regulation
§There is a need to promote the development of
local, circular supply chains through industrial
symbiosis. In the UK there is the opportunity to
develop networks linking industrial waste
producers with end users for the recovered
valuable metals – an example of industrial
symbiosis . Industrial symbiosis is most
19
successfully established when policy and
regulation supports the investment needed to
build relationships . This is highlighted by the
10
success of the National Industrial Symbiosis
Programme (NISP) in delivering significant
financial, social (including employment), resource
and environmental benefits in return for public
investment . The UK took a lead in industrial
20
symbiosis in the early 2000’s, however since
funding of NISP ceased in 2014 the UK has fallen
behind compared to other countries where the
principals have been adopted and supported by
policy. The role of government in promoting
industrial symbiosis should be considered in
the development of the ‘Resources and Waste
strategy’ .
21
§The recovery of resources from wastes needs
to be incentivised through the creation of
markets that account for the economic,
technical, social and environmental value of a
resource. Accounting for values across these
multiple dimensions, instead of a focus on
economic benefit alone, is necessary to drive a
move away from primary resource use.
Frameworks are being developed for the
exploration of the effects of recovery decisions
on the creation and destruction of economic,
technical, social and environmental values along
whole supply chains of materials, components
and products . This approach can assist decision
18
makers in assessing overall sustainability
performance of existing and emerging supply
chains. Such tools are essential for developing
arguments around choices in resource recovery
from waste that can be integrated into
sustainability assessments and decision-making
processes . The definition of value in global
22
economic systems is being questioned with
proposals for alternative models of taxation and
metrics that encompass social and
environmental costs and benefits .
23 The UK
‘Resources and Waste strategy’ is an
opportunity to embrace this changing culture
and incorporate metrics for measuring value
across multiple domains into decision making.
References
1. Department for Business, Energy and Industrial Strategy. .Industrial Strategy: building a Britain fit for the future
2. Department for Business, Energy and Industrial Strategy. .Clean Growth Strategy
3. Naden et al, 2012. . Security of supply of mineral resources (SOS minerals).Science and Implementation Plan
Natural Environment Research Council.
4. BGS Minerals UK: . Webpage accessed: 09/02/2018.Commodities and statistics
5. House of Commons Science and Technology Committee, 2011. Report on oral and written evidence on
Strategically Important Metals.
6. Sapsford et al, 2017. In situ resource recovery from waste repositories: Exploring the potential for mobilisation
and capture of metals from anthropogenic ores. Journal of Sustainable Metallurgy, , pp. 375-392.3
7. Vidal et al, 2013. . Nature Geoscience, , 894-8966Metals for a low carbon society
8. European Commission. (2015). .Factsheet on the production phase of the circular economy
9. Morgan and Mitchell, 2015. Employment and the circular economy: Job creation in a more resource efficient
Britain. WRAP and Green Alliance
10. Deutz et al, 2017. Resource recovery and remediation of highly alkaline residues. A political-industrial ecology
approach to building a circular economy. Geoforum, , pp. 336-34485
11. Crane et al, 2017. Physicochemical composition of wastes and co-located environmental designations at
legacy mine sites in the south west of England and Wales: Implications for their resource potential. Resources,
Conservation and Recycling, , pp 117-134.123
12. Ng et al, 2016. . Resources, Conservation andA multilevel sustainability analysis of zinc recovery from wastes
Recycling, , pp. 88-105.113
13. Velenturf and Purnell, 2017. Resource recovery from waste: Restoring the balance between resource scarcity
and waste overload. Sustainability, , pp 1603-1620.9
14. Velenturf et al. Co-producing a vision and approach for the transition towards a circular economy: Perspectives
from government partners. Preprints 2018.
15. Gomes et al, 2016. Alkaline residues and the environment: A review of impacts, management practices and
opportunities. Journal of Cleaner Production, , pp. 3571-3582112
16. Riley and Mayes, 2015. EnvironmentalLong-term evolution of highly alkaline steel slag drainage waters.
Monitoring and Assessment, , pp. 1-16187
17. European Commission. (2016). .Briefing on Closing the loop: New circular economy package
18. Iacovidou et al, 2017. A pathway to circular economy: developing a conceptual framework for complex value
assessment of resources recovered from waste. Journal of Cleaner Production, , pp. 1279-1288.168
19. Deutz, 2014. . In Salomone R, Saija, G. (Eds)Food for thought: Seeking the essence of industrial symbiosis
Pathways for Environmental Sustainability: Methodologies and Experiences. Springer, Switzerland. Pp. 3-11
20. UK Government Office for Science Report, 2017. From Waste to Resource Productivity: Evidence and case
studies, pp. 182
21. Velenturf, 2017. . Regional Studies, Regional Science, ,4Initiating resource partnerships for industrial symbiosis
117-124
22. Millward-Hopkins et al, 2018. Fully integrated modelling for sustainability assessment of resource recovery
from waste. Science of the Total Environment, , pp. 613-624612
23. The Ex'tax project, et al. (2016). .New era. New plan. Europe. A fiscal strategy for an inclusive, circular economy
This policy note was written by Rachel Marshall, Anne Velenturf and Juliet Jopson as part of a Policy Impact
project funded by the Natural Environment Research Council for the Resource Recovery from Waste
programme (grant code CVORR NE/L014149/1). We are grateful for the input from RRfW researchers and all
feedback received including from DEFRA, POST, WRAP, and the EA.
Resource Recovery from Waste
University of Leeds, Leeds LS2 9JT.
Web: https://rrfw.org.uk/
Twitter @RRfW6
LinkedIn Resource Recovery from Waste
ResearchGate Resource Recovery from Waste