Memorandum by Cranfield University Centre
for Resource Efficiency and Management
This response is submitted to the House of Lords
Science and Technology Sub-Committee inquiry into Waste Reduction
by the Centre for Resource Management and Efficiency at Cranfield
University. The Centre is an applied research-intensive unit offering
postgraduate programmes in waste and resources management, innovation
and design for sustainability and environmental management for
business. Our published research includes studies of waste flow
in regional economies, sustainable design and the impact of producer
responsibility on product design. Here, we restrict our comments
to the issues of waste reduction, the design mindset and materials
selection.
The relationship between products, people and waste
is a complex psychological one, described by social commentators
since the late 1950s.[1]
As we have become conditioned to seek value in ourselves as individuals
and in social groups through the purchases we make,[2]
we can expect any attempt to reposition this relationship to be
socially challenging.
WASTE REDUCTION
1. Waste reduction requires consideration
of materials flow. We need to adopt a mass balance approach[3]
to identify opportunities to achieve dematerialsation, ie to reduce
materials flow per unit of economic output as well as total materials
flow within an economy. A co-ordinated, twin-track approach of
sustainable design and production (reduced use of materials) coupled
with improved recycling and remanufacture (reduced discard of
materials), represents a sound forward strategy. We are only beginning
to learn how to co-ordinate these two components. However, Defra's
recent repositioning of its sustainable consumption and production
function alongside its waste evidence function is a valuable step
forward within Government. Understanding the influences on materials
selection and the design "mindset" are also critical.
2. The price of raw materials is the main
driver for waste reduction, but only where this is a significant
proportion of total product cost. The barriers to waste reduction
can be understood if we recognise that every product has multiple
owners in its life-cycle as it progresses through the value chain,
and that there is no single owner of the waste that it generates
in manufacture, use and disposal. The product lifecycle requires
a series of trade-offs where waste is a cost, paid at each stage.
Economic trade-offs for resources vary considerably, and a product's
value at any one stage of its value chain may still render high
levels of waste as affordable.
For example, the weight of automotive vehicle
structures has reduced progressively year on year, yet the total
weight of a vehicle has remained stable as increasing components
and functions add to the payload. Thus material and fuel efficiencies
may not necessarily be realised.[4]
Such "product lightweighting"[5]
is widely viewed as a better design strategy for the environment,
but can itself entail the use of new materials for which there
are no recycling systems.
3. The waste industry currently gains no
benefits from reducing waste. The sector is driven by volume and,
at present, landfill companies are capitalised by their remaining
void space. Further, waste companies are disconnected from the
manufacturing process. Although better design could reduce material
and fuel consumption, consumers have no metric for the material
and disposal costs of products and therefore cannot value any
improvements in performance against these in their purchasing
decisions. So, in the absence of integrated production and waste
management and readily available life cycle costs, product differentiation
is difficult for consumers to identify. A strategy of (i) better
design to encourage production of less waste at source; (ii) the
efficient use of materials and (iii) influencing lifestyles to
promote the value of functional products is required.
DESIGN MINDSET
4. While many designers are interested in
sustainable product development, there are limited opportunities
for experienced designers and engineers to rethink product development
processes that cross disciplinary boundaries. Designers are not
equally rewarded for understanding how to create value, and protect
the environment. Ecodesign is seen as contributing to product
and market enhancement, rather than as an essential function.
An improved understanding of life cycle thinking might support
informed decision making and behaviour. Cranfield University's
MSc in Innovation and Design for Sustainability, and our recent
£3.8 million HEFCE funded initiative in creative design are
attempts to foster interdisciplinary understanding by placing
designers alongside manufacturing, materials, environmental and
process specialists.
MATERIALS SELECTION
5. The principal factors that influence
the use of materials in production processes are material availability,
cost and customer demand, informalities such as habit and routine,
and the design and manufacturer's knowledge of the materials they
currently use. These factors are far more influential than the
prospect of waste reduction. Significant investment in these features
creates a reluctance to move away from established "successful
materials".
6. High volume functional products (eg lighting
assemblies; computers) with extended product lives are superseded
when fashions change or through product innovation. Consumers
in affluent nations rarely value extended life as a key product
attribute. If end-of-life costs are easily transferable to consumers
without an associated reduction in demand, changes to product
design are unlikely.[6]
Conversely, where these costs cannot be transferred, they must
be borne by the manufacturer and an environmental influence on
design may be possible. This can only be influential when the
true [total material] costs of raw materials are included in their
price. The tracking and auditing of waste/disposal costs for specific
items such as oil, tyres and aggregates can be influential in
revisiting wastes as resources eg as now being progressed through
the National Industrial Symbiosis Programme's work for specific
sectors.[7]
7. Today, many manufactured goods are not
offered in their own right but rather as part of a package that
includes service components. First, manufactured goods are provided
with closely aligned services, for example, finance, insurance,
maintenance warranties, repurchase clauses and service agreements.
Second, manufactured goods are supplied to customers as a vehicle
for accessing services. In this case, the sale of the good is
not the end point of the transaction, but only the beginning of
the relationship between the consumer and producer.
Examples of these services include "power
by the hour" from Rolls Royce and document handling services
from Xerox. Increasing consumption of the second category of services
as substitutes for goods in "business to business" and
"business to consumer" markets may provide opportunities
to promote sustainable resource use and achieve waste prevention.
Critically, within these arrangements, manufacturing firms gain
incentives to produce more durable goods to support service delivery.
However, not only should the design of the capital goods used
to support service delivery be considered, but also the overall
design of service itself so to ensure, for example, that emissions
to air from the transport component of service delivery do not
cancel out any improvements in resource efficiency that may be
attained from this approach.
1 Packard, V. (1960) The Waste Makers, Pelican
books, 320pp. Back
2
James, O. (2007) Affluenza, Vermilion Publ, 400pp. Back
3
Raffield, T, Herben, M, Billington, S, Longhurst, P and Pollard,
S. (2007) Coupling hidden flows and waste generation for enhanced
materials flow accounting. Comm Waste Res Manage 8 (1):
12-18 available at http://www.enviros.com/PDF/Raffield_couplinghiddenflows.pdf Back
4
Oakdene Hollins & Associates and Cranfield University (2007)
Product Lightweighting, Resource Efficiency KTN, www.resource-efficiency.org Back
5
James, O. (2007) Affluenza, Vermilion Publ, 400pp. Back
6
Gottberg, A, Morris, J, Pollard, S, Mark-Herbert, C & Cook,
M. (2006) Producer responsibility, waste minimisation and the
WEEE Directive: Case studies in eco-design from the European lighting
sector. Sci Tot Environ 359, 38-56. Back
7
http://www.nisp.org.uk/ Back
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