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Introduction to Polymers                                                      17



                      TABLE 1.11 (continued)
                      Major Chemical Producers Based on (Net) Sales (>2,500 Million Dollars; in
                      Millions of U.S. Dollars; 2008)
                       Yara (Norway)             15,800    LG Chem (S. Korea)      13,600
                       Reliance Industries (India)   12,200  Braskem (Brazil)       9,800
                       Sasol (South Africa)      8,300     National Petrochemical Co. (Iran)   7,800
                       Israel Chemicals (Israel)  6,900

                      * 2007 values.
                      Source: C & EN.


                 including federal and state laws and initiatives, industrial consciousness, reality, international efforts,
                 individual actions, and so on. Chemistry, chemists, and the chemical industry have been directing much
                 effort in this direction for over several decades with this effort magnified over the past several years.

                 This textbook highlights some of these efforts in polymers. Here a number of terms related to these
                 efforts will be introduced. While these terms are described individually, the environmental activity is
                 a matrix of actions and activities, each one dependent on others to be successful. Many of these studies
                 and assessments are governed somewhat by procedures described by the International Organization for
                 Standardization (ISO). (More about ISO can be found on the web and in Appendix H.)
                    Environmental impact assessment—An environmental impact assessment (EIA) is simply an
                 assessment of the possible impact that a project or material may have on the natural environment.
                 This possible impact may be positive or negative, and often is a combination of positive and nega-
                 tive impacts. The intension of such EIAs is to identify where changes can and should be made and
                 to make us aware of these instances. The International Association for Impact Assessment (IAIA)
                 describes such impact assessments as a process for “identifying, predicting, evaluating and miti-
                 gating the biophysical, social, and other relevant effects of development proposals prior to major
                 decisions being taken and commitments made.” (Petts, J. (Ed.) (1999): Handbook of Environmental
                 Impact Assessment, Vols. 1 and 2, Blackwell, Oxford.) The need and specifications for EIAs depends

                 on the particular country. For the United States it originated as part of the National Environmental
                 Policy Act of 1970. States may also have other requirements.
                    Ecological footprint—The ecological footprint is a measure of our demand on the Earth’s eco-
                 systems. It includes our demand on both natural resources and on the ability for these resources to
                 be regenerated. In the past, the methods and items to be measured varied widely, often based on
                 factors suiting the particular sector making the footprint assessment. Today, more homogeneous
                 standards are emerging. It is intended to refl ect a measure of the land, fresh water, and ocean area
                 required to produce, for instance, a product. Such footprints are often calculated to refl ect other
                 average measures. One such measure is a per capita ecological footprint that compares consumption
                 and lifestyles with the natural ability to provide this consumption.
                    Life cycle assessment—A life cycle assessment (LCA) investigates and valuates the environmental
                 impact of a product or service. It is also referred to as an ecobalance analysis, cradle-to-grave analysis,
                 and life cycle analysis. Such assessments are intended to measure the effects of the cascade of tech-
                 nologies related to products and services. Here we will restrict our comments to products. “Life cycle”
                 can refer to a holistic assessment of raw material used in the production of a product, including energy
                 consumption for procurement and transport of the material, manufacture, distribution, use, and fi nally
                 disposal, including recycling, and if possible, environmental costs. Often guesses and averages are
                 included in these studies. Thus, the cost of transportation could include some proportion of the truck
                 or train construction, road or rail construction, and the deterioration and repair of the same.
                    According to ISO 14040 and 14044 standards, an LCA contains four distinct phases. These phases

                 are goal and scope, inventory analysis, impact assessment, and interpretation of the first three phases. In






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