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2009, The International Journal of Life Cycle Assessment
Background, aim, and scope Impact assessment can be completed with the help of Life Cycle Impact Assessment (LCIA) as a part of Life Cycle Assessment (LCA) and External Cost Assessment methods. These methods help, for project and product classifications, to protect human health and the environment. Comparison of different impact assessment methods along parallel evaluations of real air pollution case studies helps to detect similarities and dependencies between them. The comparison helps and supports the work in both areas by mutually exploiting the merits of both methods. On the other hand, the detected similarities and dependencies also support the accuracy of the assessment work. Materials and methods Two impact assessment methods are compared to detect the dependencies between them. These are: the damage-oriented Life Cycle Impact Assessment method Eco-indicator 99 (EI99) and the Cost-Benefit Analysis (CAFE CBA) carried out within the framework of the Clean Air for Europe Programme of the European Union. Arithmetic comparison of the two methods' impact indicators is carried out in order to show how differently they assess and evaluate the environmental impacts of the same pollutants. Moreover, air pollution inventories of five industrialized cities in Poland are evaluated in parallel with the two impact assessment methods. The uncertainties of the two methods are also considered and Monte Carlo simulations are completed to obtain probability intervals of impact indicators and overall mean values of the generated populations. The arithmetic comparison of the impact indicators shows a strict correlation between the two impact assessment methods. This correlation is confirmed by results of the parallel evaluation of the real case studies. The comparison of the overall mean values obtained by the Monte Carlo simulations also shows a clear dependency between the results of the two impact assessment methods. After detecting the dependencies between the two methods, the best guess values of the EI99 indicator are selected and applied to make a ranking of the air pollutants and their emission sources for an industrialized Polish city. Conclusions It can be concluded that the detected correlation between the two methods (EI99 and CAFE CBA) supports and helps the accuracy of the impact assessment. If the uncertainties of the methods are also considered, it is proved for the examples of real case studies that they correlate in their results. On the other hand, the best guess of the EI99 indicators can be used to rank emissions according to their relative damage to human health and the ecosystem, and to locate emission sources. These results help decision-makers to conclude an efficient environmental conscious policy.
2003
Life cycle assessment (LCA) is a popular tool for evaluating environmental impacts of products and services. However, the methodological choices and framework to assess environmental impacts in LCA are still under discussion. Despite intensive development worldwide, few attempts have been made hitherto to systematically present the theoretical bases of life cycle impact assessment (LCIA). In this study, the decision analytic foundations for LCIA are illustrated. It is shown that the typical aggregation equation used in LCIA for calculating indicator results can be derived from multiattribute value theory (MAVT) if certain simple assumptions hold. The decision analysis framework presented in this work offers additional values for all the phases of LCIA. A value tree, a tool used for structuring multicriteria decision making problems, can be helpful for selection of impact categories and classification. MAVT can clarify the debate concerning marginal and average approaches in the determination of characterisation factors. On the basis of MAVT, normalisation is needed before weighting. The methods and experiences of preference elicitation derived from the field of decision analysis can be utilised in the determination of subjective characterisation factors and impact category weights. Furthermore, experiences and techniques for the sensitivity analysis of multi-criteria decision models can be utilised in LCIA. In addition, MAVT assists in the calculation of impact category indicator results and total impact indicator results according to the appropriate aggregation equations. The decision analysis framework presented in this work is flexible and suitable for different impact assessment approaches developed in LCIA and it can help the methodological development with which the non-linearity aspects of impact assessment are taken into account. It is shown in the work that site-dependent characterisation methods can easily be fitted into the framework. In a case study of the Finnish forest industry a Finlandspecific impact assessment model utilising the results of other tools, such as air quality and transport models and even expert judgements, was developed. In addition, the so-called ratio estimation method for the elicitation of impact category weights was applied and developed so that interval-valued ratio judgements could be used in the uncertainty analysis of the model. In the case of the Finnish metals industry, decision analysis impact assessment was applied to produce a solution in which global, regional and local environmental problems were assessed in the same framework. In both case studies, experts working with the environmental issues valuated impact category weights with the help of decision analysis techniques. In the work it was shown that MAVT provides a foundation for a logical and rational approach to impact assessment in LCA. In the future, there is a need to demonstrate quantitatively the differences between LCIA conducted according to MAVT and according to current practices. Furthermore, there is a need for research to study the strengths and weaknesses of the different decision analysis methods for LCIA purposes.
Journal of Hazardous Materials, 2010
The impact on human health of substances emitted to air by the Flemish industry was calculated with characterization factors (CFs) provided by the CML, Eco-indicator 99, EPS, EDIP and USEtox impact assessment methods. A comparison of the results pointed out that the choice of the CFs can greatly influence conclusions on the trend of the impact over time and on the relative contribution of the individual substances. If the impact on human health of organic substances and heavy metals was assessed separately, the differences between methods were less pronounced. In this case, the impacts on human health obtained by simply dividing the emitted masses of substances by the respective minimal risk concentrations or minimal risk doses, were comparable to those calculated with the CFs of the model-based methods.
International Journal of Environmental Technology and Management, 2007
The paper deals with the introduction of a complex index capable of evaluating environmental air quality in industrial areas. In Italy regional plans of recovery and protection of air quality have been put in practice in order to identify areas where the increase of the emissions into atmosphere, owing to urban and/or industrial development, should be limited or prevented. The methodology is founded on an evaluation system of energy efficiency of cogeneration plants, based on some meaningful energy-environmental performance indicators, containing weighting factors taking into account the Best Available Techniques (BATs), even considering the contribution of secondary particulate matter.
Building and Environment, 2005
A methodology which can be applied to the environmental impact study (EIS) and which facilitates to analyse the urban variables as a whole is explained. The work can be done in different scales (urban sectors and areas) which depend on the analysis complexity degree. This would allow to qualify and to quantify the local and regional environmental impact. Different concepts, methods and techniques have been considered and conveniently integrated. A body of relational decision matrices has been developed, in which the magnitude, sign, significance and temporality impact concepts are included. Different indices levels have also been developed. r
2011
The paper presents some comparative aspects in terms of discharges into the environment (i.e. air, water resources, soil/subsoil, and noise) such as gaseous discharges in the air, final effluents into receiving basins or sewerage system, discharges onto soil/subsoil. There are mentioned the principal pollutants expressed by different physicochemical indicators with their direct on-line measurements or laboratory analysed values corresponding to some specific economic activities and their evaluation scores in terms of discharge quality and effect onto different life forms, but especially onto environment and human health. The quantification of environmental impact is performed by using of the same assessment methodology applied for calculation of global pollution index (I * GP). The values of I * GP for different economic activities were synthesized together with the estimation of their potential environmental impact and pollution effect against environment and especially against different life forms.
Environmental Impact Assessment study is key for any project, without which it is unlikely to get the authorization for the commencement of a project. Keeping this in view, this review has been taken. The principle objective of this is to concentrate the benchmark status of air, noise, water, organic and socioeconomic conditions. System for Impact Assessment has been coordinated inside a zone of 7 km go around the project for an Automobile Industry site as per ISO Standards of Air Quality, Noise Quality Water Quality, Soil Quality. Socioeconomic conditions, Biological conditions under this accessibility of review zone have been considered and Solid Waste Management, Occupational Safety and Health Safety procedures have been suggested. This kind of studies particularly helpful for keenness in EIA Reports.
2001
Distance-to-target weighting methods are widely used in life cycle impact assessment. The methods rank impacts as being more important the further away society's activities are from achieving the desired targets for the pollutants. However, we feel that the scientific bases of the distance-to-target methods still need more clarification. This article illustrates how multiattribute value theory (MAVT) can be applied to interpret the impact category weights as well as the aggregation rule and normalisation used in the distant-to-target methods. Our comparison revealed that under certain conditions two of the three commonly used impact assessment methods (Ecoindicator 95, ET-method) applying distance-to-target weighting are consistent with the impact assessment framework derived from MAVT. This consistency holds for non-zero targets with equal importance and linear damage functions passing through the origin. We show that the MAVT framework offers a foundation for the methodological development in life cycle impact assessment.
International Journal of Life Cycle Assessment, 2015
Purpose Assessing comprehensively the overall environmental impacts of a region remains a major challenge. Within life cycle assessment (LCA), this evaluation is performed calculating normalisation factors (NFs) at different scales. Normalisation represents an optional step of LCA according to ISO 14040/44 which may help in understanding the relative magnitude of the impact associated to a product when compared to a reference value. In order to enhance the robustness and comprehensiveness of NFs, this paper presents a methodology for building an extended domestic inventory of emission and resources extraction. The domestic inventory refers to emissions and extractions due to the processes located within a geographical region, Europe (EU 27), in 2010. A robust regional inventory is a fundamental element for supporting the calculation of global factors, often resulting form extrapolation and upscaling from regional ones. Methods The NFs for EU 27 in 2010 are based on extensive data collection and the application of extrapolation strategies for data gaps filling. The inventory is based on domestic emissions into air, water and soil and on resource extracted in EU, adopting a production-based approach. A hierarchy is developed for selection of data sources based on their robustness
In this work, a methodological framework under the form of an algorithmic procedure, including 28 activity stages and 6 decision nodes, has been developed for evaluating environmental impact caused by industrial activities. The main part of this procedure is a modification of the Contingent Valuation Method (CVM), which is heavily relied on survey-based estimation of WTP-WTA (willingness to pay/accept, respectively). The survey may take place either under a strictly controlled environment or in situ and as-is ('laboratory conditions' or 'field conditions', respectively, in the terminology of experimental economics). Implementation of this methodology is presented, referring to three cases of industrial pollution (in three different sites) caused by (i) a cement producing units, (ii) an oil refinery complex, and (iii) an industrialized small city with an intensively polluted port, where several industrial units co-exist, all of them located in the vicinity of Athens, Greece. The results are interpreted/discussed and conclusions are drawn.
This paper describes the conceptual framework for a damage value-oriented weighting method for endpoint problems. It is developed with the aim to be transparent, and with a minimum of subjective features. Calculations of external environmental impacts are based on data for material-and energy flows, emission factors, and characterisation of emissions into contribution to environmental impact categories. These environmental impact values are then weighted by using damage values (total number of DALY (Disability Adjusted Life Years)) for each type of problem. Estimations of the number of persons possibly affected by a problem caused by emissions have been made and multiplied by the severity for each affected person. The category weight is the sum of all damage values in an impact category. This approach has several advantages: (1) A clear distinction between the characterization step and valuation step of the LCA, (2) A knowledge driven method where an improvement in quality and relia...
The International Journal of Life Cycle Assessment, 2013
Purpose This study discusses the significance of the use of non-renewable fossil cumulative energy demand (CED) as proxy indicator in the beverage packaging sector, in order to detect those situations in which companies can benefit from the use of proxy indicators before a full life cycle assessment (LCA) application. Starting from a case study of two milk containers, the objectives of this paper are to assess if the use of this inventory indicator can be a suitable proxy indicator both (1) to decide which is the packaging alternative with the lowest environmental impact and (2) to identify the most impacting process units of the two products under study. Method The analysis was made according to ISO14040-44. The goal of the comparative LCA was to evaluate and to compare the potential environmental impacts from cradle to grave of a laminated carton container and a HDPE bottle. The results of the comparative LCA obtained with the nonrenewable CED indicator are compared with a selection of impact categories: climate change, particulate matter formation, terrestrial acidification, fossil depletion, photochemical oxidant formation. A further analysis is made for the two products under study in order to determine which are the environmental hot spots in terms of life cycle stages, by the means of a contribution analysis. Results and discussion From the comparative LCA, the use of non-renewable CED revealed to be useful for a screening as the results given by the non-renewable CED indicator are confirmed by all the impact categories considered, even if underestimated. If the aim of the LCA study was to define which is the packaging solution with a lower environmental impact, the choice of this inventory indicator could have led to the same decision as if a comprehensive LCIA method was used. The contribution analysis, focusing on the identification of environmental hot spots in the packaging value chain, revealed that the choice of an inventory indicator as non-renewable CED can lead to misleading results, if compared with another impact category, such as climate change.
Air Pollution XXIII, 2015
Air pollution is a worldwide problem with broadly known harmful effects on health and environment. A great research challenge lies in quantifying the intensity of these adverse effects as well as the associated external costs. To this end, several methodologies involving exposure-response relationships and economic evaluation of externalities have been developed. A literature review of existing methodologies to estimate air pollution impacts on human health and subsequent external costs has been performed aiming to identify strengths and major gaps in current knowledge. The most common practice is to estimate health impacts taking into account morbidity (disability-adjusted life years due to episodes of cardiovascular and respiratory diseases) and mortality (e.g. years of life lost due to lung cancer) indicators. For the quantification of the resulting external costs, a monetary valuation of the extent of damage, grounded in treatment/remediation costs, is applied. Notwithstanding the significant efforts to improve the economic evaluation of air pollution impacts, there is some controversy on damage cost estimates. For example, the monetary valuation is not a straightforward procedure as many of the impacts have no market value. In addition, it is increasingly recognized that Air Pollution XXIII 181
Urban Transport XIII: Urban Transport and the Environment in the 21st Century, 2007
We intend to build a global environmental impact indicator of air pollution to assess transport infrastructures and technologies. This indicator should be simple and transparent to facilitate its use in decision-making. The intention is for the indicator to resemble the Global Warming Potential (GWP), which establishes a relationship between the emission of six greenhouse gases and the average temperature increase of the Earth. The indicator will therefore permit estimating the global environmental impact of transport-generated air pollution, while simultaneously conserving the value of the environmental impact of each type of air pollution and the emission assessment. This work is based on an impact typology, a set of indicators, and an aggregation architecture of atmospheric pollution. The typology is established as a combination of the specific and homogenous characteristics of each type of pollution in terms of pollutant, impact mechanism, target and environmental impact. To ensure exhaustiveness and non-redundancy, 10 types of air pollution impact are proposed: greenhouse effect, ozone depletion, direct ecotoxicity (this type of pollution excludes greenhouse effects on nature, ozone depletion, eutrophication, acidification and photochemical pollution), eutrophication, acidification, photochemical pollution, restricted direct health effects (not taking into account welfare, and excluding the effects on health of the greenhouse effect, ozone depletion, acidification and photochemical pollution), sensitive pollution (annoyance caused by odours and fumes), and degradation of common and historical man-made heritage. Indicators similar to GWP can be identified in the literature for each type of atmospheric pollution, except for the degradation of common and historical manmade heritage, for which the financial cost of conservation could be used. However, these indicators do not seem to have achieved wide scientific consensus, except for GWP, which may make it necessary to continue research in this field. Aggregating the different indicators is proposed by using an architecture composed of two structures that aggregate types of air pollution. One is based on the target affected, whereas the second has three dimensions, i.e. targets, space and time. This architecture allows the indicator's users to establish a hierarchy of concerns for each type of atmospheric pollution.
Environmental Science & Technology, 2006
The impact assessment phase of Life Cycle Assessment (LCA) has received much criticism due to lack of consistency. While the ISO standards for LCA did make great strides in advancing the consensus in this area, ISO is not prescriptive, but has left much room for innovation and therefore inconsistency. To address this lack of consistency, there is currently an effort underway to provide a conceptual framework for Life Cycle Impact Assessment (LCIA) and a recommended practice to include a list of impact categories, category indicators, and underlying methodologies. This is an enormous undertaking, especially in light of the current fundamental lack of consensus of the basic elements to be included in a LCIA (e.g., impact categories, impacts, and areas of protection). ISO 14042 requires selection of impact categories that "reflect a comprehensive set of environmental issues" related to the system being studied, especially for "comparative assertions" that involve public marketing claims. To be comprehensive, it is necessary to have a listing of impacts that "could" be included within the LCIA before entering into discussions of impacts that "should" be included. In addition to providing a critical analysis of existing and emerging impact assessment approaches, this paper will formulate a structured representation that allows more informed selection of approaches. The definitions and relationships between midpoint, endpoint, damage, and areas of protection will be presented in greater detail, along with the equations that are common to many of the approaches. Finally, a discussion of the advantages and disadvantages of displaying results at various stages in the environmental models will be presented in great detail.
Chemosphere, 1997
The Fraunhofer-Gesellschaft has sponsored the development of a conceptual and flexible, computer aided tool to perform the impact assessment within LCA (life cycle assessment) for technical products and processses. The developed general framework ,,Ela 1.0'' (environmental loads analysis) consists of four elements: the selection of appropriate impact categories, the categorization of emissions and wastes leaving the systems as well as of resource and energy consumption, the characterization and an analysis of the results of the impact assessment. The latter compares the product-based emissions with the total of emissions of a region such as Germany, the EU or OECD countries. The framework Eia 1.0 considers the environmental categories: global warming, ozone depletion, resource and energy consumption, wastes, eutrophication (including COD and BOD as measured parameters), acidification, ecotoxicity, ozone formation and human toxicity. The latter categories are handled by listing of precursors for ozone formation, and by listing of emissions scored according to their human hazard potential. The options, possibilities and limitations of the conceptual framework are presented in part A of a series of publications.
Environmental Science and Pollution Research, 2012
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Sustainability, 2017
One of the applied methods for environmental impact assessment is the index of global pollution (I GP) proposed by Rojanschi in 1991. This methodology enables the global estimation for the ecosystem state affected more or less by human activities. Unfortunately, Rojanschi's method has a limitation; it can be applied only if at least three environmental components are considered. Frequently, many environmental impact assessment applications rely on analysis of only two environmental components. Therefore, this work aimed to develop a new graphical method to extend Rojanschi's approach for the case of two environmental components. The proposed method avoids the average value of evaluation grades and uses only the graphical correspondence for calculation of the index of global pollution. A right-angle triangle graph methodology was proposed, where bases represented the values of evaluation grades. Thus, for the case of two environmental components, the index of global pollution was calculated as the relation between the ideal and real ecosystem states represented by the ratio between areas of external and enclosed right triangles. The developed graphical method was tested and validated for real case studies: the environmental impact assessment from a refinery located on the Romanian Black Sea Coast considering Air and Water environmental components and from a coal-fired thermoelectric power plant from Eastern Romania regarding Air and Soil environmental components. In this way, it was provided a reliable and faster tool to be used for the pollution characterization of human-derived chemicals for better decisions in risk management.
14th SGEM GeoConference on ECOLOGY, ECONOMICS, EDUCATION AND LEGISLATION, 2014
Life-cycle assessment is a technique to assess environmental impacts associated with all the stages of a product's life from-cradle-to-grave -from raw material extraction through materials processing, manufacture, distribution, use, repair and maintenance, and disposal or recycling. It is fairly new approach, but till now many methodologies and tools have been developed on the basis of LCA. They usually compile an inventory of relevant energy and material inputs and environmental releases, evaluate the potential impacts associated with identified inputs and releases and finally they could be used to interpret the results in order to help decision makers to make a more informed decision.
The purpose of this paper is to propose an alternative methodology for aggregation in a life cycle assessment (LCA). The comprehensive aggregation method is based on a damage approach and done through an analytical hierarchy process. Consistency analysis is also presented to justify the reliability of the judgements and the magnitude of change in the values developed. A case study of electricity generation is applied to demonstrate its applicability in LCA study within a Malaysian context. Results from this case study show that the weighting value is higher compared to global and European values; however, they are consistent as in the case of product ranking towards greener products. Regional impacts such as particulate matter formation and photochemical oxidant formation have higher score compared to global impacts such as climate change. The results show that the method is simple and replicable.
Journal of Sustainable Development, 2016
Monetary values of environmental impacts from emissions and from use of natural resources help in understanding the environmental significance of human activities. It is however a complicated and time consuming task to determine these values, and the values are easy to uncritically accept without understanding the many ways they may be determined, the many preferences they may represent and the different contexts for which they may be relevant. This article aims at increasing the usefulness of monetary valuation and decreasing some of its shortcomings by demonstrating a way to model and calculate monetary values of environmental impacts from emissions and use of natural resources, highlight subjective choices that have to be made in modelling and calculations, and discuss how some of them influence the values assessed. The method we use is based on the principles of the EPS default impact assessment method, which comply with the requirements of the ISO 14044 life cycle assessment standard. Monetary values for 98 endpoint category indicators are determined, and calculations of characterization factors are demonstrated for CO 2 , N 2 O, CH 4 , and NO x . Two methodological choices have proven particularly important for the values obtained. One is the long term perspective and intergenerational equity. The other is the approach to uncertainty. Both is important for what is included in the assessments and to what extent.
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