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The term 'carbon footprint' has become tremendously popular over the last few years and is now in widespread use across the media – at least in the United Kingdom. With climate change high up on the political and corporate agenda, carbon footprint calculations are in demand. Numerous approaches have been proposed to provide estimates, ranging from basic online calculators to sophisticated life-cycle-analysis or input-output based methods and tools. Despite its ubiquitous use however, there is an apparent lack of academic definitions of what exactly a 'carbon footprint' is meant to be. The scientific literature is surprisingly void of clarifications, despite the fact that countless studies in energy and ecological economics that could have claimed to measure a 'carbon footprint' have been published over decades. This commentary explores the apparent discrepancy between public and academic use of the term 'carbon footprint' and suggests a scientific definition based on commonly accepted accounting principles and modelling approaches. It addresses methodological questions such as system boundaries, completeness, comprehensiveness, units, and robustness of the indicator.
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ISAUK Research Report 07-01 0
A Definition of ‘Carbon Footprint’
ISAUK Research Report
Thomas Wiedmann and Jan Minx
ISAUK Research Report 07-01
This report has now been published as a book chapter (suggested citation):
Wiedmann, T. and Minx, J. (2008). A Definition of 'Carbon Footprint'. In: C. C. Pertsova, Ecological
Economics Research Trends: Chapter 1, pp. 1-11, Nova Science Publishers, Hauppauge NY, USA.
© June 2007
ISAUK Research & Consulting
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ISAUK Research Report 07-01
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A Definition of 'Carbon Footprint'
Thomas Wiedmann1)*) and Jan Minx2)
1) ISAUK Research & Consulting, Durham, DH7 7FB, UK (
2) Stockholm Environment Institute, University of York, Heslington, York, YO10 5DD, UK (
*) Corresponding author. Email:
The term ‘carbon footprint’ has become tremendously popular over the last few years and is now in
widespread use across the media at least in the United Kingdom. With climate change high up on the
political and corporate agenda, carbon footprint calculations are in strong demand. Numerous approaches
have been proposed to provide estimates, ranging from basic online calculators to sophisticated life-cycle-
analysis or input-output-based methods and tools. Despite its ubiquitous use however, there is an apparent
lack of academic definitions of what exactly a ‘carbon footprint’ is meant to be. The scientific literature is
surprisingly void of clarifications, despite the fact that countless studies in energy and ecological economics
that could have claimed to measure a ‘carbon footprint’ have been published over decades.
This report explores the apparent discrepancy between public and academic use of the term ‘carbon
footprint’ and suggests a scientific definition based on commonly accepted accounting principles and
modelling approaches. It addresses methodological question such as system boundaries, completeness,
comprehensiveness, units and robustness of the indicator.
carbon footprint, ecological footprint, indirect carbon emissions, indicators, environmental accounting,
input-output analysis, life-cycle analysis, hybrid analysis
ISAUK Research Report 07-01
‘Carbon footprint’ has become a widely used term
and concept in the public debate on responsibility
and abatement action against the threat of global
climate change. It had a tremendous increase in
public appearance over the last few months and
years and is now a buzzword widely used across
the media, the government and in the business
But what exactly is a ‘carbon footprint’? Despite its
ubiquitous appearance there seems to be no clear
definition of this term and there is still some
confusion what it actually means and measures
and what unit is to be used. While the term itself is
rooted in the language of Ecological Footprinting
(Wackernagel 1996), the common baseline is that
the carbon footprint stands for a certain amount of
gaseous emissions that are relevant to climate
change and associated with human production or
consumption activities. But this is almost where
the commonality ends. There is no consensus on
how to measure or quantify a carbon footprint. The
spectrum of definitions ranges from direct CO2
emissions to full life-cycle greenhouse gas
emissions and not even the units of measurement
are clear.
Questions that need to be asked are: Should the
carbon footprint include just carbon dioxide (CO2)
emissions or other greenhouse gas emissions as
well, e.g. methane? Should it be restricted to
carbon-based gases or can it include substances
that don’t have carbon in their molecule, e.g. N2O,
another powerful greenhouse gas? One could even
go as far as asking whether the carbon footprint
should be restricted to substances with a
greenhouse warming potential at all. After all,
there are gaseous emissions such as carbon
monoxide (CO) that are based on carbon and
relevant to the environment and health. What's
more, CO can be converted into CO2through
chemical processes in the atmosphere. Also,
should the measure include all sources of
emissions, including those that do not stem from
fossil fuels, e.g. CO2emissions from soils?
A very central question is whether the carbon
footprint needs to include indirect emissions
embodied in upstream production processes or
whether it is sufficient to look at just the direct, on-
site emissions of the product, process or person
under consideration. In other words, should the
carbon footprint reflect all life-cycle impacts of
goods and services used? If yes, where should the
boundary be drawn and how can these impacts be
Finally, the term ‘footprint’ seems to suggest a
measurement (expression) in area-based units.
After all, a linguistically close relative, the
‘Ecological Footprint’ is expressed (measured) in
hectares or 'global hectares'. This question,
however, has even more far-reaching implications
as it goes down to the very decision whether the
carbon footprint should be a mere ‘pressure’
indicator expressing (just) the amount of carbon
emissions (measured e.g. in tonnes) or whether it
should indicate a (mid-point) impact, quantified in
tonnes of CO2equivalents (t CO2-eq.) if the impact
is global warming potential, or in an area-based
unit if the impact is ‘land appropriation’.
Many of these questions have been discussed in
the disciplines of ecological economics and life-
cycle assessment for many years and therefore
some answers are at hand. So far, however, they
have not been applied to the term carbon footprint
and thus a clear definition is currently missing.
This report addresses the questions above and
attempts a clarification. We provide a literature
overview, propose a working definition of the
term 'carbon footprint' and discuss methodological
A brief literature review
A literature search in June 2007 for the term
"carbon footprint" (i.e. where these two words
stand next to each other in this order) in all
scientific journals and all search fields covered by
Scopus1and ScienceDirect2for the years 1960 to
1Scopus ( is currently the largest
abstract and citation database of peer-reviewed
ISAUK Research Report 07-01
2007 yielded 42 hits; 3 from the year 2005, 8 from
2006 and 31 from 2007. Most articles deal with the
question of how much carbon dioxide emissions
can be attributed to a certain product, company or
organisation, although none of them provides an
research literature. Scopus is updated daily and
covers 30 million abstracts of 15,000 peer-reviewed
journals from more than 4,000 publishers ensuring a
broad interdisciplinary coverage.
2ScienceDirect ( contains over
25% of the world's science, technology and medicine
full text and bibliographic information, including a
journal collection of over 2,000 titles as well as online
reference works, handbooks and book series.
unambiguous definition of the term carbon
In most cases 'carbon footprint' is used as a generic
synonym for emissions of carbon dioxide or
greenhouse gases expressed in CO2equivalents.
Some articles, however, discuss the implications of
precise wording. Geoffrey Hammond writes
(Hammond 2007): "…The property that is often
referred to as a carbon footprint is actually a
'carbon weight' of kilograms or tonnes per person
or activity." Hammond argues "…that those who
favour precision in such matters should perhaps
campaign for it to be called 'carbon weight', or
some similar term."
Table 1: Definitions of 'carbon footprint' from the grey literature
Source Definition
BP (2007) "The carbon footprint is the amount of carbon dioxide emitted due to your daily
activities from washing a load of laundry to driving a carload of kids to school."
British Sky
(Sky) (Patel 2006)
The carbon footprint was calculated by "measuring the CO2equivalent emissions from
its premises, company-owned vehicles, business travel and waste to landfill." (Patel
Carbon Trust
"… a methodology to estimate the total emission of greenhouse gases (GHG) in carbon
equivalents from a product across its life cycle from the production of raw material
used in its manufacture, to disposal of the finished product (excluding in-use
"… a technique for identifying and measuring the individual greenhouse gas emissions
from each activity within a supply chain process step and the framework for
attributing these to each output product (we [The Carbon Trust] will refer to this as the
product’s ‘carbon footprint’)." (CarbonTrust 2007, p.4)
Energetics (2007) "… the full extent of direct and indirect CO2emissions caused by your business
ETAP (2007)
"…the ‘Carbon Footprint’ is a measure of the impact human activities have on the
environment in terms of the amount of greenhouse gases produced, measured in
tonnes of carbon dioxide."
Global Footprint
Network (2007)
"The demand on biocapacity required to sequester (through photosynthesis) the
carbon dioxide (CO2) emissions from fossil fuel combustion." (GFN 2007; see also text)
Grub & Ellis
"A carbon footprint is a measure of the amount of carbon dioxide emitted through the
combustion of fossil fuels. In the case of a business organization, it is the amount of
CO2emitted either directly or indirectly as a result of its everyday operations. It also
might reflect the fossil energy represented in a product or commodity reaching
Office of Science
and Technology
(POST 2006)
"A ‘carbon footprint’ is the total amount of CO2and other greenhouse gases, emitted
over the full life cycle of a process or product. It is expressed as grams of CO2
equivalent per kilowatt hour of generation (gCO2eq/kWh), which accounts for the
different global warming effects of other greenhouse gases."
ISAUK Research Report 07-01
Haven (2007) mentions the carbon footprint
analysis of an office chair as a "life-cycle
assessment which took into account materials,
manufacture, transport, use and disposal at every
stage of development." 3This hints at a more
comprehensive approach, rarely described in other
articles. However, there is no definition or
methodological description. Eckel (2007) points out
that the "Assessment of a business' carbon
footprint is not just calculating energy
consumption but also with increasing every scrap
of data from every aspect of the business
practices." Again, no clear scope of analysis is
While academia has largely neglected the
definition issue, consultancies, businesses, NGOs
and government have moved forward themselves
and provided their own definitions. In the grey
literature is a plethora of descriptions, some of
which are presented in Table 1.
In the UK, the Carbon Trust 4has aimed at
developing a more common understanding what a
carbon footprint of a product is and circulated a
draft methodology for consultation (Carbon Trust
2007, see definition in Table 1). It is emphasised
that only input, output and unit processes which
are directly associated with the product should be
included, whilst some of the indirect emissions
e.g. from workers commuting to the factory are
not factored in.
Life-cycle thinking can be found in many other
documents and seem to have developed into one
characteristic of carbon footprint estimates. A
standardisation process has been initiated by the
Carbon Trust and Defra aimed at developing a
Publicly Available Specification (PAS) for LCA
methodology used by the Carbon Trust to measure
3Note that a carbon footprint of a product derived in
such a way cannot just be added to the carbon
footprint of an office using this chair as this would
lead to double counting. Furthermore, double (or
multiple) counting would occur if companies
involved in the life cycle chain of the chair
(manufacturing, transport, disposal) reported their
full emissions (see e.g. Hammerschlag and Barbour
2003, Lenzen 2007 and Lenzen et al. 2007).
4The Carbon Trust is a private company set up by the
UK government "to accelerate the transition to a low
carbon economy."
the embodied greenhouse gases in products
(DEFRA 2007). Below, we discuss the pro's and
con's of various methodologies.
The Global Footprint Network, an organisation
that compiles 'National Footprint Accounts' on an
annual basis (Wackernagel et al. 2005) sees the
carbon footprint as a part of the Ecological
Footprint. Carbon footprint is interpreted as a
synonym for the 'fossil fuel footprint' or the
demand on 'CO2area' or 'CO2land'. The latter one
is defined as "The demand on biocapacity required
to sequester (through photosynthesis) the carbon
dioxide (CO2) emissions from fossil fuel
combustion. [It] includes the biocapacity,
typically that of unharvested forests, needed to
absorb that fraction of fossil CO2that is not
absorbed by the ocean." However, while
individual documents have used such a land-
based definition, for example the Scottish Climate
Change Strategy (see Scottish Executive 2006), it
has not changed the common understanding of the
carbon footprint as a measure of carbon dioxide
emissions or carbon dioxide equivalents in the
A definition of 'carbon footprint'
We propose the following definition of the term
'carbon footprint':
"The carbon footprint is a measure of the
exclusive total amount of carbon dioxide
emissions that is directly and indirectly caused
by an activity or is accumulated over the life
stages of a product."
This includes activities of individuals, populations,
governments, companies, organisations, processes,
industry sectors etc. Products include goods and
services. In any case, all direct (on-site, internal)
and indirect emissions (off-site, external,
embodied, upstream, downstream) need to be
taken into account.
The definition provides some answers to the
questions posed at the beginning. We include only
CO2in the analysis, being well aware that there are
other substances with greenhouse warming
ISAUK Research Report 07-01
potential. However, many of those are either not
based on carbon or are more difficult to quantify
because of data availability. Methane could easily
be included, but what information is gained from a
partially aggregated indicator, that includes just
two of a number of relevant greenhouse gases? A
comprehensive greenhouse gas indicator should
include all these gases and could for example be
termed 'climate footprint'. In the case of 'carbon
footprint' we opt for the most practical and clear
solution and include only CO2.
The definition also refrains from expressing the
carbon footprint as an area-based indicator. The
'total amount' of CO2is physically measured in
mass units (kg, t, etc) and thus no conversion to an
area unit (ha, m2, km2, etc) takes place. The
conversion into a land area would have to be
based on a variety of different assumptions and
increases the uncertainties and errors associated
with a particular footprint estimate (see e.g.
Lenzen 2006). For this reason accountants usually
try to avoid unnecessary conversions and attempt
to express any phenomenon in the most
appropriate measurement unit (e.g. Keuning 1994;
Stahmer 2000). Following this rationale a land-
based measure does not seem appropriate and we
prefer the more accurate representation in tonnes
of carbon dioxide.
Whilst it is important for the concept of 'carbon
footprint' to be all-encompassing and to include all
possible causes that give rise to carbon emissions,
it is equally important to make clear what this
includes. The correct measurement of carbon
footprints gains a particular importance and
precariousness when it comes to carbon offsetting.
It is obvious that a clear definition of scope and
boundaries is essential when projects to reduce or
sequester CO2emissions are sponsored. When
accounting for indirect emissions, methodologies
need to be applied that avoid under-counting as
well as double-counting of emissions, therefore the
word 'exclusive' in the definition.5Furthermore, a
full life-cycle assessment of products means that all
the stages of this life cycle need to be evaluated
correctly (with “full” meaning “untruncated”). In
the following section we discuss the
methodological implications of these requirements.
5Compare with the discussion of 'shared reponsibility'
as outlined by Lenzen et al. (2007).
Methodological issues
The task of calculating carbon footprints can be
approached methodologically from two different
directions: bottom-up, based on Process Analysis
(PA) or top-down, based on Environmental Input-
Output (EIO) analysis. Both methodologies need to
deal with the challenges outlined above and strive
to capture the full life cycle impacts, i.e. inform a
full Life Cycle Analysis/Assessment (LCA). Here,
only a brief impression of some of their main
merits and drawbacks can be provided.
Process analysis (PA) is a bottom-up method,
which has been developed to understand the
environmental impacts of individual products
from cradle to grave. The bottom-up nature of PA-
LCAs (process-based LCAs) means that they suffer
from a system boundary problem - only on-site,
most first-order, and some second-order impacts
are considered (Lenzen 2001). If PA-LCAs are used
for deriving carbon footprint estimates, a strong
emphasis therefore needs to be given to the
identification of appropriate system boundaries,
which minimise this truncation error. PA-based
LCAs run into further difficulties once carbon
footprints for larger entities such as government,
households or particular industrial sectors have to
be established. Even though estimates can be
derived by extrapolating information contained in
life-cycle databases, results will get increasingly
patchy as these procedures usually require the
assumption that a subset of individual products
are representative for a larger product grouping
and the use of information from different
databases, which are usually not consistent (see
e.g. Tukker and Jansen 2006).
Environmental input-output (EIO) analysis
provides an alternative top-down approach to
carbon footprinting (see e.g. Wiedmann et al.
2006). Input-output tables are economic accounts
providing a picture of all economic activities at the
meso (sector) level. In combination with consistent
environmental account data they can be used to
establish carbon footprint estimates in a
comprehensive and robust way taking into
account all higher order impacts and setting the
whole economic system as boundary. However,
this completeness comes at the expense of detail.
The suitability of environmental input-output
ISAUK Research Report 07-01
analysis to assess micro systems such as products
or processes is limited, as it assumes homogeneity
of prices, outputs and their carbon emissions at the
sector level. Although sectors can be disaggregated
for further analysis, bringing it closer to a micro
system, this possibility is limited, at least on a
larger scale. A big advantage of input-output
based approaches, however, is a much smaller
requirement of time and manpower once the
model is in place.
The best option for a detailed, yet comprehensive
and robust analysis is to combine the strength of
both methods by using a hybrid approach (Bullard
et al. 1978, Suh et al. 2004, Heijungs and Suh 2006),
where the PA and input-output methodologies are
integrated. Such an approach allows to preserve
the detail and accuracy of bottom-up approaches
in lower order stages, while higher-order
requirements are covered by the input-output part
of the model. Such a Hybrid-EIO-LCA method,
embedding process systems inside input-output
tables, is the current state-of-the art in ecological
economic modelling (Heijungs and Suh 2002,
Heijungs et al. 2006, Heijungs and Suh 2006). The
literature is just emerging and few practitioners so
far have acquired the skills to carry out such a
hybrid assessment. However, rapid progress and
much improved models can be expected over the
next few years.
The method of choice will often depend on the
purpose of the enquiry and the availability of data
and resources. It can be said that environmental
input-output analysis is superior for the
establishment of carbon footprints in macro and
meso systems. In this context a carbon footprint of
industrial sectors, individual businesses, larger
product groups, households, government, the
average citizen or an average member of a
particular socio-economic group can easily be
performed by input-output analysis (e.g. Foran et
al. 2005, SEI et al. 2006, Wiedmann et al. 2007).
Process analysis has clear advantages for looking
at micro systems: a particular process, an
individual product or a relatively small group of
individual products.
Practical examples
To date carbon footprints have been established for
countries and sub-national regions (SEI and WWF
2007), institutions such as schools (GAP et al.
2006), products (Carbon Trust 2006), businesses
and investment funds (Trucost 2006).
In this section we present two practical examples
of a carbon footprint analysis that adhere to the
definition suggested above. Both analyses were
undertaken by researchers of the Stockholm
Environment Institute at the University of York,
employing an input-output based approach.
The 'UK Schools Carbon Footprint Scoping Study'
(GAP et al. 2006) estimates that all schools in the
United Kingdom had a carbon footprint of 9.2
million tonnes of carbon dioxide in 2001, equating
to 1.3% of total UK emissions. Only around 26% of
this total carbon footprint can be attributed to on-
site emissions from the heating of premises,
whereas the other three quarters are from indirect
emission sources, such as electricity (22%), school
transport (14%), other transport (6%), chemicals
(5%), furniture (5%), paper (4%), other
manufactured products (14%), mining and
quarrying (2%) and other products and services
The second example is a calculation of the carbon
footprint of UK households, taking into account
direct and indirect emissions occurring on UK
territory due to consumption activities of UK
residents as well as the (indirect) emissions that are
embodied in imports to the UK. The results,
presented in the 'Counting Consumption' report
(SEI et al. 2006), suggest that the carbon footprint
of an average UK household was 20.7 tonnes of
CO2in 2001. A breakdown of this total is presented
in Figure 1.
ISAUK Research Report 07-01
20 Private cars
Direct fuel use in the home
Electricity in the home
Aviation and public transport
Recreation, leisure and tourism
Food, drink and catering
Household appliances
Clothing and footwear
Health, hygiene and education
Other goods
Other services
Figure 1: Carbon dioxide emissions associated with UK household consumption in 2001
(tonnes of CO2per household) (SEI et al. 2006)
Direct emissions occur through heating and car
use. Indirect emissions are the emissions that occur
during the generation of electricity and the
production of goods and services (whether they
are produced in the UK or in other countries).
They make up 70 per cent of the almost 21 tonnes
of CO2per household. Transport (private cars,
aviation and public transport) accounts for 28% of
total emissions. Electricity use in the home and use
of fuels for space and water heating in the home
account for almost one third of the emissions.
These findings have also been published by the UK
Department for the Environment, Food and Rural
Affairs (DEFRA) in the 'The Environment in your
Pocket' publication (DEFRA 2006).
A review of scientific literature, publications and
statements from the public and private sector as
well as general media suggests that the term
'carbon footprint' has become widely established in
the public domain albeit without being clearly
defined in the scientific community. In this report
we suggest a definition of the term 'carbon
footprint' and hope to stimulate an academic
debate about the concept and process of carbon
footprint assessments.
We argue that it is important for a 'carbon
footprint' to include all direct as well as indirect
CO2emissions, that a mass unit of measurement
should be used, and that other greenhouse gases
should not be included (or otherwise the indicator
should be termed 'climate footprint'). We discuss
the appropriateness of two major methodologies,
process analysis and input-output analysis, finding
that the latter one is able to provide
comprehensive and robust carbon footprint
assessments of production and consumption
activities at the meso level. As an appropriate
solution for the assessment of micro-systems such
as individual products or services we suggest a
Hybrid-EIO-LCA approach, where life-cycle
assessments are combined with input-output
analysis. In this approach, on-site, first- and
second-order process data on environmental
impacts is collected for the product or service
system under study, while higher-order re-
quirements are covered by input-output analysis.6
Whatever method is used to calculate carbon
footprints it is important to avoid double-counting
along supply chains or life cycles. This is because
there are significant implications on the practices
of carbon trading and carbon offsetting
(Hammerschlag and Barbour 2003, Lenzen 2007,
Lenzen et al. 2007).
6For example by using the Bottomline3tool
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... The carbon footprint is a measure of the exclusive total amount of carbon dioxide emission that is directly and indirectly caused by an activity or that is accumulated over the life stages of a product (Wiedmann and Minx 2007). The greenhouse gas emissions caused by the energy used in the production, transfer, and blockchain storage of NFTs are included in their carbon impact. ...
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The market for non-fungible token (NFT) art is expected to reach USD 44.2 billion in 2021 and increase by 67.57 percent in 2022, revolutionizing the relationship between artists, collectors, and investors. Despite this, concerns regarding the environmental impact of blockchain technology’s high energy consumption persist. NFT art transactions will continue to generate significant carbon emissions after Ethereum’s “Merge” to a Proof-of-Stake (PoS) system in September 2022, rendering many low-carbon solutions obsolete and necessitating further research into post-Merge alternatives. This study identifies solutions in the NFT art market, such as carbon neutrality, lazy minting, alternative consensus mechanisms, Layer 2 solutions and policy interventions. Carbon neutrality is achieved through investments in renewable energy or carbon credits to mitigate emissions generated by NFT art transactions. Lazy minting reduces energy consumption by postponing the creation of NFT art until a buyer is secured. In the NFT art ecosystem, alternative consensus mechanisms such as Proof of Authority (PoA) and Proof of Spacetime (PoST) reduce energy consumption. By offloading transactions from the primary blockchain, Layer 2 solutions enhance scalability and reduce energy consumption. Carbon taxes and energy consumption levies are examples of policy interventions that promote cleaner energy sources in the NFT art market. This study will explore the role of artists, collectors, galleries, and other significant players in encouraging environmentally sustainable practices in the NFT art market. In addition, it will investigate the effect of prominent NFT art sales on carbon emissions and the adoption of eco-friendly alternatives. By integrating and optimizing current carbon reduction strategies, the NFT art market can continue to flourish while reducing its environmental impact. The study emphasizes the significance of implementing a comprehensive strategy that incorporates multiple solutions that are tailored to the specific challenges of the NFT art market.
... There is confusion about the carbon footprint terminology (Wiedmann and Minx, 2007). The CO 2 and SO 2 emissions are considered during the project's lifetime. ...
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A cost and financial evaluation model is proposed for floating wind farm designs. The model evaluates the cost of the offshore farms depending on the required capacity, technical aspects, and technology implemented, among other aspects. The costs involved in the different phases of the farm construction are studied. The main equations developed for the model construction are simplified and presented in this document. This study presents a comparison of several financial indicators for the following floating concepts: Spar-Buoy (TELWIND), Tension-Leg-Platform (CENTEC-TLP) and Semi-Submersible (SATH). The model is applied to a farm composed of thirty-four 10 MW floating turbines in a Life Cycle Analysis perspective. The model allows the determination of the optimal floating platform for a site and identifies the optimal solution for a floating farm depending on the economic and financial aspects associated.
... Por ello, es necesario reforzar las medidas de ahorro de energía, lo que supone la aplicación de estudios y auditorías que, con sólidas bases técnicas, analicen, midan y evalúen los principales consumos de energía, ofreciendo una posibilidad de mejora, modernización y ahorro, con lo que se puede llegar a una mayor eficiencia energética (Morales et al., 2016) y, por lo tanto, una reducción de la huella de carbono. Por huella de carbono se entiende que es una medida de la cantidad total, exclusiva, de emisiones de dióxido de carbono que es causada directa o indirectamente por una actividad o acumulada durante las etapas de vida de un producto (Wiedmann and Minx, 2008). Este trabajo tiene como objetivo evaluar el consumo eléctrico en aire acondicionado e iluminación, así como la huella de carbono resultante de este consumo, en el Instituto Tecnológico de Linares. ...
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Vivimos en una emergencia climática y los niveles de gases de efecto invernadero siguen aumentando. Por estos motivos, “tomar medidas urgentes para combatir el cambio climático y sus impactos” y “garantizar el acceso a una energía asequible, fiable, sostenible y moderna para todos” son dos de los 17 Objetivos de Desarrollo Sostenible, acordados por Naciones Unidas en 2015. Poco a poco, las universidades han ido incorporando estrategias y acciones de desarrollo sostenible. Este trabajo determina la Huella de Carbono del Instituto Tecnológico de Linares (parte del Tecnológico Nacional de México) utilizando el protocolo GEI: Alcance 2. En primer lugar, se realizó un levamiento de las 10 edificaciones del instituto, con el fin de calcular el consumo anual y índice de consumo de energía eléctrica (ICEE). La Huella de Carbono total del Instituto Tecnológico de Linares en 2018 fue de 141 tCO2e (emisiones alcance 2). Combinar la auditoría energética con el cálculo de la huella de carbono nos permite, por un lado, diagnosticar los edificios desde el punto de vista de la eficiencia energética y, por otro lado, implementar un plan de mitigación del cambio climático que nos obligue a cumplir con nuestra responsabilidad social ambiental.
... A fenntarthatósági mutatószám az ökológiai lábnyomnak az a része, amely a valamilyen tevékenység, személy, területegység stb. által közvetlenül vagy közvetve a levegőbe kibocsátott teljes CO 2 -mennyiséget, illetve az e CO 2 -mennyiség semlegesítéséhez szükséges területegységet méri (Wiedmann, 2007). A szénlábnyom kiszámításához az ISO 14040 és 14044 szabványok ajánlásainak megfelelően az életciklus-értékelés (LCA) módszertanát alkalmazzák (International Organisation for Standardization 2009). ...
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The paper presents the practical application of the latest economic theory (circular economy), the combination of algorithmic and systems thinking (LCA) in the field of hospitality. Growing and changing consumer demands are constrained by resource scarcity, driving new technological innovations. By measuring the environmental impacts, different scenarios are compared for a known catch, all from a life-cycle perspective. We will show, by determining the carbon footprint using computer software, at which stages and to what extent a change at different stages of the process makes the conventional process “greener”. A legújabb gazdasági elmélet (körkörös gazdaság), az algoritmikus és rendszerszemléletű gondolkodásmód (LCA) együttes alkalmazásának gyakorlati megvalósítását mutatja be a tanulmány a vendéglátás területén. A növekvő és átalakuló fogyasztói igényeknek korlátot szab az erőforrások szűkössége, ezzel újabb és újabb technológiai újításokat ösztönöz. A környezeti hatások mérésével különböző forgatókönyveket hasonlítunk össze egy ismert éttermi fogásra, mindezt életciklus szemléletben. Kimutatjuk, a karbonlábnyom számítógépes szoftverrel történő meghatározásával, hogy a folyamat különböző fázisaiban véghez vitt változtatás mely szakaszokban és mekkora mértékben teszi „zöldebbé” a hagyományos konyhatechnológiai eljárást.
... Recently, more than 200 leading health journals have published a joint commentary on the current climate emergency, with a call for urgent action to reduce the impact of climate change on health [13]. Carbon footprint modelling is a tool that has been applied to countries, institutions, industries, and individuals to determine the total Greenhouse Gas (GHG) emissions that are caused by an activity or product over its life stages [14]. Its application in the health sector is recent, but it has a large scope to aid policy makers, health care supply chain procurement, hospital managers, and clinical practitioners to develop novel solutions to reduce the climate change contributions of health care [15]. ...
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The primary aim of this systematic analysis is to highlight opportunities to improve the environmental impact of advanced therapy medicinal products (ATMP) manufacturing. We have compared the Greenhouse Gas (GHG) emissions expressed in CO2eq of a classic clean room open system (AinB) Cell Factory versus a comparable closed system equipped with isolators (AinD). We have therefore outlined a theoretical situation to simulate the use of a closed system with an equivalent production output to that obtained in the Cell Factory (CF) of the Regina Margherita Children’s Hospital. Open and closed systems for ATMPs have been compared as regards energy requirements, ecological footprints, and costs by analyzing a hypothetic cell production cycle of 21 days. The results demonstrate energy saving and a reduction of 52% in GHG emissions using closed systems per process cycle. Moreover, a reduction in production costs in an isolator setting is also evident. This study shows that the closed system solution has evident advantages compared with the open one.
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The global availability of web-based computing coupled with the need to address pressing problems in the environment and in society have led to the articulation of new information management, problem solving and communication skills for 21st century learners (UNESCO, 2011). This paper describes how opportunities to practice these skills may be implemented in the classroom using investigative case-based pedagogy with online data and tools for making evidence-based decisions about contemporary issues such as energy utilization. In Singapore in August 2011, a group of lower secondary teachers were introduced to investigative case-based pedagogy, newly published 21st century competencies for the classroom, and an online carbon calculator developed for public use. The following paper presents a review of the project planning, methods and materials used, example products, and conclusions.
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Günümüzde küresel ölçekte yaşanan en önemli sorunlardan biri çevre kaynaklı olaylardır. Bu çalışmanın amacı sağlık çalışanlarının yeşil örgütsel davranış konusundaki farkındalık düzeylerinin değerlendirilmesidir. Araştırmanın evrenini özel bir hastanede görev yapan sağlık çalışanları oluştururken, örneklemini araştırmaya katılmaya gönüllü 262 çalışan oluşturmuştur. Veriler kişisel bilgi formu ve Yeşil Örgütsel Davranış Ölçeği kullanılarak toplanmıştır. Veri analizinde Epi Info 7 istatistik programı kullanılmıştır. Araştırmada medeni duruma göre yeşil örgütsel davranış ölçeği alt boyutları karşılaştırıldığında, bekarların teknolojik duyarlılık alt boyutu puan ortalaması evlilere göre daha yüksek bulunmuştur. Çalışmada eğitim durumuna göre çevresel katılım ve ekonomik duyarlılık alt boyutları için ilköğretim mezunlarının (4,76-4,93), yeşil satın alma için ön lisans mezunlarının ortalama puanlarının (4,66) daha yüksek olduğu görülmüştür. Gelir durumuna göre yeşil örgütsel davranış ölçeği alt boyutları arasında istatistiksel olarak anlamlı bir farklılık olduğu (p
This paper presents a tinyNARM which is an experimental effort in approaching/tailoring the classical Numerical Association Rule Mining to limited hardware devices, precisely on ESP32 microcontrollers so that devices do not need to depend on in-cloud remote servers. The tinyNARM reduces the number of attributes in the transaction database by discretizing the continuous numeric attributes, and replacing the stochastic evolutionary algorithm for association rule mining with its deterministic counterpart. The preliminary results of the comparative study, in which the in-cloud NiaARM and the on-device tinyNARM were included by mining several UCI ML datasets, revealed that the quality of mined association rules and the time complexity were good enough for continuing the research in the direction of the tinyML.Keywordsnumerical association rule miningNiaARMtinyML
Technical Report
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Not withstanding the traditional smokestack image of the manufacturing sectors, its overall TBL performance is reasonably balanced. Energy use and greenhouse emissions are above average while employment generation and income are below average. Many of the manufacturing sectors currently face strong competition from countries with lower wages and larger scale, and effective solutions are difficult to define. Nevertheless three issues emerge from this analysis. Industry strategies which aim to increase value adding in Australia bring with them the social returns of increased employment and possibly increased use of resources such as energy and water. If these products can be developed with environmentally advanced production chains, then this may give an advantage in affluent countries where markets are concerned with sustainability issues. Finally, meeting the environmental challenges may require industrial processes and material fabrication skills that are currently underdeveloped in Australian industry. Overall, there does not seem much advantage in Australia relying solely on being a cost efficient producer of average quality materials and products.
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Calculating the Ecological Footprint of a company must fulfil certain requirements. It must take into account the direct Footprint impacts such as direct land appropriation and emissions from vehicles and premises. And it also must take account of indirect impacts that are embodied in all the purchases the company makes. As companies and individual (final) consumers are not at the same place in the life-cycle of production and consumption, different calculations and conversion factors have to be applied, otherwise there would be double-counting and non-comparability of Footprints. Splitting up the life-cycle to account for the correct impacts of intermediate purchases and products is not trivial as every company is embedded in a complex web of suppliers and clients, each of which contribute their own Footprint to the total impact. We present an extended input-output approach to calculate Footprints of companies that are truly comparable. For purpose of international comparisons, results from different economies can be presented with an identical aggregation of economic sectors. The single region model currently in use leads to some limitations with respect to imports and international supply chains. We discuss the implications and how this shortcoming can be addressed in the future. We present a practical, quantitative example calculated with a new software tool ( ), including detailed breakdowns of all Footprint land types, sector benchmarking, structural path analysis (upstream supply chain analysis) and production layer decomposition. We discuss the implications for sustainable chain management and sector sustainability.
British Sky Broadcasting (Sky) has announced achievement of carbon neutral status through the measurement, reduction, and offsetting of its CO2 emissions. The carbon footprint was calculated by measuring the CO2 equivalent emissions from its premises, company-owned vehicles, business travel and waste to landfill. This positive result was obtained through implementation of innovations that include features that decrease power consumption and creating a research and development roadmap aimed at energy efficiency.
Corus' Shotton Works plant in Deeside, North Wales, part of the Strip Products Division that produces organic paint-coated prefinished steel, for cladding, and roofing have installed modern oxidizer systems in order to destroy hazardous air pollutants (HAP) and volatile organic compounds (VOC). The increased environmental regulations, energy prices and emergence of new technologies influence the company to re-evaluate its entire system in order to improve manufacturing efficiency. The company decided to replace multiple air pollution control systems with one regenerative thermal oxidizer (RTO). The system has several features such as a three-chamber design that processes 55,000 SCFM of air, achieving over 99-percent DRE without visible emissions, and 85-percent beat recovery and a secondary heat exchanger that recycles waste heat directly back to the ovens, reducing the amount of natural gas required for product curing.
Methods are presented for calculating the energy required, directly and indirectly, to produce all types of goods and services. Procedures for combining process analysis with input-output analysis are described. This enables the analyst to focus data acquisition effects cost-effectively, and to achieve down to some minimum degree a specified accuracy in the results. The report presents sample calculations and provides the tables and charts needed to assess total energy requirements of any technology, including those for producing or conserving energy.
Input-output tables (I-O tables) can play an important role in delivering a suitable data base for studies on sustainable development. Experience has shown that the quality of specialized studies on various aspects of sustainability is enhanced by drawing on I-O tables presented in different units, such as: I-O tables in monetary units for economic issues; I-O tables in physical units (tonnes etc.) for ecological issues; I-O tables in time units for social issues. This article gives a detailed description of the advantages and disadvantages of the three types of units for presenting I-O data. For illustrative purposes, comparable I-O tables using the abovementioned different types of units are shown describing the German economy in the year 1990. The production boundary is extended to all paid and unpaid human activities, consumer durables and educational services are treated as investment goods.
Preface. 1. Introduction. 2. The basic model for inventory analysis. 3. The refined model for inventory analysis. 4. Advanced topics in inventory analysis*. 5. Relation with input-output analysis*. 6. Perturbation theory. 7. Structural theory. 8. Beyond the inventory analysis. 9. Further extensions*. 10. Issues of implementation*. A. Matrix algebra. B. Main terms and symbols. C. Matlab code for most important algorithms. References. Index.