Input-Output Analysis [IOA] (including Social Accounting Matrices [SAM])

By |April 27th, 2014||Comments Off on Input-Output Analysis [IOA] (including Social Accounting Matrices [SAM])

Primary Source: Suomalainen, K., with contributions by Heijungs, R. (2006) Input-Output Analysis SWOT Analysis in Report on the SWOT analysis of concepts, methods, and models potentially supporting LCA. Eds. Schepelmann, Ritthoff & Santman (Wuppertal Institute for Climate and Energy) & Jeswani and Azapagic (University of Manchester), pp 96-102

Level of analysis: Mainly macro, can be applied to meso-level in some cases depending on the level of detail of available data and purpose of assessment.

Assessed aspects of sustainability: Economic, generally national economic relationships.

Main purpose of the assessment: To understand interdependencies of transactions between national industries/sectors in order to predict effects of a change in one industry on others.

Description of the methodology: IOA is a method that systematically quantifies the mutual interrelationships between various sectors of an economy. The method uses national statistics of intersectorial transactions to construct a detailed statistical picture of the national economy in matrix form. The interdependence among the sectors is described by a set of linear equations expressing the balances between the total input and the aggregate output of each commodity and service produced and consumed over a defined period of time. The effect of an event at any one point is transmitted to the rest of the economy step by step via the chain of transactions that link the whole system together.
Detailed Description
IOA was developed by Wassily Leontief as an effort to combine economic facts (empirical content) and theory (mathematical formulation of problems) to describe the inter-industry relationships typically within a nation or a region. A detailed statistical picture of the system could be achieved thanks to high-speed computers and accumulated large quantities of statistical data, and the IOA formulation by Leontief. IOA has passed from mere academic investigation [...]

Computable General Equilibrium Model (CGEM / CGE Model)

By |April 26th, 2014||Comments Off on Computable General Equilibrium Model (CGEM / CGE Model)

Primary Source: Suomalainen, K. (2006) Computable General Equilibrium Model SWOT Analysis in Report on the SWOT analysis of concepts, methods, and models potentially supporting LCA. Eds. Schepelmann, Ritthoff & Santman (Wuppertal Institute for Climate and Energy) & Jeswani and Azapagic (University of Manchester), pp 88-95

Level of analysis: Macro.

Assessed aspects of sustainability: Economic, possible to include environmental aspects.

Main purpose of the assessment: To assess macro-economical impact of policy changes.

Description of the methodology: Computable general equilibrium models are a class of economic models that use realistic economic data together with the abstract general equilibrium structure to simulate how an economy might react to changes in policy, technology or other external factors. In other words, CGEMs solve numerically the levels of supply, demand and price that support equilibrium across a specified set of markets. CGE models are a standard tool of empirical analysis, and are widely used to analyse the aggregate welfare and distributional impacts of policies whose effects may be transmitted through multiple markets, or contain menus of different tax, subsidy, quota or transfer instruments. Examples of their use may be found in areas as diverse as fiscal reform and development planning, international trade, and increasingly, environmental regulation (Wing).

Detailed description
Computer models are especially useful when analysing complex systems containing vast amounts of data. The benefits of computer models include explicitness, infallible computing and comprehensiveness (Sterman, 1991). In equilibrium models demand elasticity is introduced. The user specifies a demand curve rather than a single value for the demand. Based on the analysis, the demand level can change in response to changes in prices. The three conditions of market clearance, zero profit and income balance are employed by CGE models to solve simultaneously for the set of [...]

Environmental Impact Assessment (EIA)

By |April 26th, 2014||Comments Off on Environmental Impact Assessment (EIA)

Primary Source: Jöborn, I. (2006) Environmental Impact Assessment Swat Evaluation in Report on the SWOT analysis of concepts, methods, and models potentially supporting LCA. Eds. Schepelmann, Ritthoff & Santman (Wuppertal Institute for Climate and Energy) & Jeswani and Azapagic (University of Manchester), pp 83-87.

Level of analysis: Micro level. EIA is made for public and private projects, for example when planning for a new industry or infrastructure (roads, railroads, pipelines).

Assessed aspects of sustainability: Impacts on the environment and on human health, it can also include socio-economic or social impacts.

Main purpose of the assessment: To predict and communicate the impacts on the environment of projects in order to prevent negative environmental and assess socioeconomic impacts of the development. The outcomes of EIA are used to inform decision-making on whether to proceed with the development.

Description of the methodology: Environmental Impact Assessment (EIA) is a systematic procedure that examines the environmental consequences of development projects, at the proposal stage. It is a framework and can include several different methods and tools for analysis, depending on the technical/environmental content of the decision at hand. The analysis is prospective and site specific.

Detailed description

Environmental Impact Assessment (EIA) was first introduced in the USA in the National Environmental Policy Act (NEPA) in 1969. The aims were to evaluate environmental impacts of proposed developments, make the planning decisions more transparent and the process more democratic. NEPA has led to the adoption of similar environmental impact laws all over the world. The European Community Directive on EIA was introduced in 1985 (85/337/EEC) and was updated in 1997 (97/11/EC). The directive is applied to the assessment of the environmental effects of public and private projects that are likely to have significant effects on the environment.

EIA [...]

Environmental Risk Analysis (ERA/HRA)

By |April 26th, 2014||Comments Off on Environmental Risk Analysis (ERA/HRA)

Primary Source: Jeswani, H and Azapagic, A. (2006) EIOA/EEIOA Swat Evaluation in Report on the SWOT analysis of concepts, methods, and models potentially supporting LCA. Eds. Schepelmann, Ritthoff & Santman (Wuppertal Institute for Climate and Energy) & Jeswani and Azapagic (University of Manchester), pp 77-82

Level of analysis: Micro (on substances) and Macro (on policies)

Assessed aspects of sustainability: Environmental and social

Main purpose of the assessment: To assess either environmental or health risks (or both) from a product, process, project or policy in qualitative and/or quantitative ways to assist in decision-making for minimising those risks.

Description of the methodology: Risk assessment is most-commonly used in assessing the environmental, health and safety related risks posed by chemicals, harmful substances, industrial plants, etc. Methodologically, it is rooted in two analytical approaches: probability theory and methods for identifying causal links between adverse effects and different types of hazardous activities.

Detailed description

Risk assessment is used in wide range of professions to examine risks of different natures. It is most-commonly used in assessing the environmental, health and safety related risks posed by chemicals, harmful substances, industrial plants, etc. Environmental Risk Assessment (ERA) is usually used as an umbrella term covering Human Health Risk Assessment (HRA), Ecological (or eco-toxicological) Risk Assessment, and specific industrial applications of risk assessment that examine endpoints in people, biota or ecosystems (Calow, 1998). The risks examined in the assessment can be physical such as radiation, biological such as a genetically modified organism or pathogen, or chemical such as an immuno-toxic substance (Fairman et al., 1998). Although the foundations of environmental risk assessment methodologies have traditionally been based on the investigation of effects on human health, the methodologies have also been expanded to examine the threats to ecosystem (DEFRA, 2000).

Methodologically, [...]

Hybrid Analysis, Integrated Hybrid Analysis (IHA)

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Primary Source: Heijungs, R. (2006) EIOA/EEIOA Swat Evaluation in Report on the SWOT analysis of concepts, methods, and models potentially supporting LCA. Eds. Schepelmann, Ritthoff & Santman (Wuppertal Institute for Climate and Energy) & Jeswani and Azapagic (University of Manchester), pp 72-76

Level of analysis: Micro at the level of substances and products, meso at the level of businesses and sectors.

Assessed aspects of sustainability: Environmental

Main purpose of the assessment: Hybrid analysis is a term that can in principle refer to any combination of two or more specific forms of analysis. However, in many cases, it is used for the combination of a process-based LCA and an environmentally extended input-output analysis. The idea is that a foreground system is specified in terms of detailed processes, while the data for more general upstream processes are taken from environmental IO tables. Thus the strength of process-based LCA and the strength of environmental IOA are used together.

Detailed description

Hybrid analysis is a term that can in principle refer to any combination of two or more specific forms of analysis (Udo de Haes et al., 2004). However, in many cases, it is used for the combination of a process-based LCA and an environmentally extended input-output analysis (EIOA). The idea is that a foreground system is specified in terms of detailed processes (e.g., for the production of a can of beer), while the data for more general upstream processes (e.g., relating to equipment and transport) are taken from environmental IO tables. Thus the strength of process-based LCA and the strength of EIOA are used together.

For Lave et al (1995), a main motivation to use EIOA for product assessment (i.e. EIO-LCA), thus instead of traditional ISO-LCA, is the more complete system and the [...]

Environmental Input-Output Analysis / Environmentally Extended Input-Output

By |April 26th, 2014||Comments Off on Environmental Input-Output Analysis / Environmentally Extended Input-Output

Primary Source: Suomalainen, K. (2006) EIOA/EEIOA Swat Evaluation in Report on the SWOT analysis of concepts, methods, and models potentially supporting LCA. Eds. Schepelmann, Ritthoff & Santman (Wuppertal Institute for Climate and Energy) & Jeswani and Azapagic (University of Manchester), pp 62-71

Level of analysis: Mainly macro, can be applied to meso-level in some cases depending on the level of detail of available data and purpose of assessment. Bottom-up approaches of IO-based LCA allow micro level assessment.

Assessed aspects of sustainability: Environmental, generally national environmental accounting.

Main purpose of the assessment: To account for environmental burdens and understand interdependencies of environmental impacts at a national level, related to transactions between national industries/sectors.

Description of the methodology: EIOA/EEIOA are expansions of conventional IOA introducing the environmental dimension to the conventionally monetary analysis. EIOA uses physical units to describe the activities between sectors, added as extra lines to the conventional IO-table. EEIOA defines a separate so called intervention matrix, which shows the amount of pollutants emitted and natural resources consumed to produce one unit monetary output of each industry. In addition to flows (input materials) corresponding to monetary trade, quantifiable externalities such as pollution are typically also included.
Detailed description
Input-output analysis accounts for the level of output of each sector corresponding to that level of activity in all the other sectors in a national economy. By-products, mostly negative from the environmental view point (e.g. pollution), are often linked directly to the network of physical flows that build up an IO-table. This technical interdependence can be described in terms of structural coefficients similar to those already used to trace the interdependence of production between the sectors of the economy (Leontief, 1970).

EIOA

In EIOA pollutants can be integrated to the conventional IO-tables [...]

Total Cost of Ownership (TCO)

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Primary Source: Jeswani, H, and Azapagic, A. (2006) Total Cost Assessment Swat Evaluation in Report on the SWOT analysis of concepts, methods, and models potentially supporting LCA. Eds. Schepelmann, Ritthoff & Santman (Wuppertal Institute for Climate and Energy) & Jeswani and Azapagic (University of Manchester), pp 58-61

Level of analysis: Micro

Assessed aspects of sustainability: economic

Main purpose of the assessment: To determine direct and indirect costs relating to the purchase of a product or service.

Description of the methodology: It is a structured approach for calculating the costs associated with buying and using a product or service. Total cost of ownership takes the purchase cost of an item into account but also considers related costs such as ordering, delivery, subsequent usage and maintenance, supplier costs, and after-delivery costs.

Detailed description

Total Cost of Ownership (TCO) is a management-accounting oriented tool to find the lifetime costs of acquiring, operating, and changing something. The concept takes into account all costs that the purchase and the subsequent use of components entail in the entire value chain of the company, and thus expands the notion of purchasing cost by combining the life cycle cost effects with the acquisition price (Ellram and Siferd, 1998).

TCO analysis if properly done could bring out the “hidden” or non-obvious ownership costs that might otherwise be overlooked in making purchase decisions or planning budgets. It is a valuable tool for the evaluation and/or selection of suppliers and/or offerings, since it considers not just price, but also the cost effects of the alternatives (Wynstra and Hurkens, 2005). These cost effects could be ordering costs, stock keeping costs, inspection costs, maintenance, etc. These cost components are often divided into pre-transaction costs, transaction costs and post-transaction costs (Ellram, 1993).

The analysis begins with [...]

Total Cost Assessment (Total Cost Accounting)

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Primary Source: Jeswani, H, and Azapagic, A. (2006) Total Cost Assessment Swat Evaluation in Report on the SWOT analysis of concepts, methods, and models potentially supporting LCA. Eds. Schepelmann, Ritthoff & Santman (Wuppertal Institute for Climate and Energy) & Jeswani and Azapagic (University of Manchester), pp 52-5

Level of analysis: Micro

Assessed aspects of sustainability: economic

Main purpose of the assessment: To provide economic assessment of environmental initiatives. It is a long-term oriented cost accounting method which pays specific attention to identifying hidden, less tangible and liability costs.

Description of the methodology: TCA methodology encompasses a broad decision-making perspective and incorporates sustainable development considerations through identification, compilation, analysis, and use of environmental and human health cost, both internal and external information associated with a business decision.

Detailed description

Total Cost Assessment (TCA) is a financial tool used to provide a more complete assessment of the true profitability of business investments and operations. It has been used to evaluate alternative capital investments, operational expenditures and procurement decisions. In most cases, it is used for assessing the costs and benefits derived from the environmental initiatives and policies to support decision making (Beaver, 2000).

TCA is a useful tool for identifying, analysing, and improving cost estimates in key areas such as energy, waste, and prevention management, both internally and externally. It can incorporate a wide spectrum of costs and benefits in business cases for all new product and process projects, focusing on internal and external considerations. TCA pays specific attention to identifying hidden, less tangible and liability costs (Curkovic and Sroufe, 2007). Less tangible costs are, for example, consumer acceptance, corporate image and external relations. Liability costs are fines due to the liability for such things as future clean up, health care and property [...]

Life Cycle Costing (LCC)

By |April 25th, 2014||Comments Off on Life Cycle Costing (LCC)

Primary Source: Kock, E, Rydberg, T. and Ekvall, T.. (2006) Life Cycle Costing Swat Evaluation in Report on the SWOT analysis of concepts, methods, and models potentially supporting LCA. Eds. Schepelmann, Ritthoff & Santman (Wuppertal Institute for Climate and Energy) & Jeswani and Azapagic (University of Manchester), pp 46-51

Level of analysis: any, but primary focus on the micro level (products & services),

Assessed aspects of sustainability: economic and environmental

Main purpose of the assessment: Quantify and analyse the life cycle costs.

Description of the methodology: This method entails data collection and calculations of all costs associated within the life cycle of a product that are directly covered by one, or more, of the actors involved in the products life cycle, including external costs that are anticipated to be internalised in the decision-relevant future.

Detailed description

Life cycle costing (LCC) belongs to the group of sustainability tools that focus on flows in connection with production and consumption of goods and services. They focus on evaluating different flows in relation to various products or services instead of for example regions or nations LCC is an economic approach that sums up” total costs of a product, process or activity discounted over its lifetime”. It is associated with cost in general rather than just environmental cost for example (Ness 2007).

A robust LCC framework will be able to link life cycle analysis studies to the monetary cost systems used by business decision-makers. Unless these dollar driven decisions can be assessed in terms of the physical limits of natural systems, it will be difficult to assess progress toward sustainability. Therefore, LCC is seen alongside LCA as two of the three pillars in an evaluation of sustainability, with the third, social assessment, still in its infancy [...]

Cost Benefit Analysis (CBA)

By |April 25th, 2014||Comments Off on Cost Benefit Analysis (CBA)

Primary Source: Armines, A. R.. (2006) Cost Benefit Analysis Swat Evaluation in Report on the SWOT analysis of concepts, methods, and models potentially supporting LCA. Eds. Schepelmann, Ritthoff & Santman (Wuppertal Institute for Climate and Energy) & Jeswani and Azapagic (University of Manchester), pp 38-45

Level of analysis: Micro, meso and macro

Assessed aspects of sustainability:  environmental, economic plus possibly other external costs (time spent by consumers, space required in household, etc.)

Main purpose of the assessment:

Compare costs and benefits of a proposed action (e.g. environmental directive, choice of technology, environmental policy, …)

Description of the methodology:

Description of the methodology: evaluate all the significant costs and benefits entailed by the proposed action. Both direct and indirect or induced effects need to be taken into account. For many choices this involves evaluation of upstream and downstream impacts, using LCA. But by contrast to most conventional LCA, it includes monetary valuation of the impacts. A typical and very important example is the CBA of the CAFE program (Clean Air for Europe) [Holland et al 2005; EC 2006]. Similar CBAs have been carried out in the USA, for example the study by Abt [2000] for the EPA.

Detailed description

Whereas the basic principle of CBA is straightforward, the practical implementation can be extremely difficult. Countless examples of CBA can be found in the literature, ranging in complexity from a simple comparison of two technology choices (e.g. an evaluation of stricter limits for the emission of PM10 from cement kilns that use waste as fuel [Rabl 2000]) to the evaluation of an entire policy (e.g. the CAFE program (Clean Air for Europe) [Holland et al 2005]).

For environmental CBA a crucial tool is the analysis of impact pathways, i.e. of the chain emission [...]