Financial analysis: | --- |
Environmental impact analysis: | |
Waste management/P2: | --- |
Environmental cost listing/database: | --- |
Cost estimation: | --- |
Alternative product/process comparison: |
The approach used is to describe impacts on the environment in terms of one or several safeguard subjects and value changes in them according to the willingness to pay to restore them to their normal status. The five safeguard subjects are
Activities are then valued according to their estimated contribution to the changes in the five safeguard subjects. The EPS Enviro-Accounting method
Raw material acquisition | |
Manufacturing stage | |
Use/reuse/maintenance | |
Recycle/waste management |
Background information is derived from LCA-based inventories of the materials and processes under review. However, the methodology itself does not categorize impacts as they occur in various life-cycle stages of a process or product. Much of the EPS Enviro-Accounting method is applicable to life-cycle cost integration and to the development of the E-CYCLE.
Conventional | --- |
Potentially hidden | --- |
Contingent | --- |
External |
The methodology can be used for valuing external intangible costs. Costs of environmental impacts on the five safeguard subjects listed previously are evaluated. The report includes estimated indices for a wide range of environmental impacts. The system is not meant to include internal company costs; it is designed to value external environmental impacts.
WTP to avoid environmental effects is used to estimate costs. Impacts are valued on a relative scale using environmental load units (ELU) according to the WTP for avoiding negative effects on the safeguard subjects. Using life-cycle data, users can calculate environmental indices for the materials and processes being studied. Users can also include qualitative information for describing how the indices were estimated. The values are not absolute figures but rather points of reference for further analysis and refinement.
The output from the EPS system is a value, based on a common metric, for different environmental impacts. The value may be broken down into its individual components for further analysis and users can determine the level of detail desired. The authors address several criticisms of using monetary values to assess environmental impacts. These include the following:
Environmental impact valuation is described as a subjective matter that can be given some degree of objectivity by studying decisions made in society or by surveying people's opinions. Contingent valuation is cited as a method for generating a relative rating of various environmental effects. Contingent valuation is used here to determine individuals' WTP to avoid certain environmental effects.
Net present value (NPV) | --- |
Payback period | --- |
Internal rate of return (IRR) | --- |
Benefits cost ratio | --- |
Other | --- |
Some positive characteristics of the tool are as follows.
The EPS system goes a step beyond the complex flows in a life-cycle analysis to provide users with easy to understand and manageable information.
The method itself does not evaluate various alternatives, rather it supports decision-making by providing users with information that they can further use in analysis or further refine to suit their requirements. It is aimed to be used to value current and foreseeable impacts within legal limits (not sudden spillsor accidents). The choice of unit effects also has certain limitations, such as the ability for the effects to be quantitatively valued. Additionally, the authors acknowledge the difficulty in assessing the actual value of an ecosystemin its entirety. The EPS method does not generate financial indicators such as NPVs, because it assesses environmental impacts alone-not costs and benefits.
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