Industrial Environmental Management. Tapas K. Das

Чтение книги онлайн.

Читать онлайн книгу Industrial Environmental Management - Tapas K. Das страница 15

Industrial Environmental Management - Tapas K. Das

Скачать книгу

and the implementation could be accelerated. Ultimately, the integration of the environmental responsibility with the environmental systems and allocation of the resources needed shall lead to implementation of the environmental strategies and it can contribute to both improvements in the environmental performance and in increasing long‐term profitability of the industry.

      1.2.1 Environmental Challenges

      Our avid interest in environmental sustainability and environmental management issues can be traced directly to awareness that as the world's population continues to expand and to consume natural resources, humanity faces shortages that threaten quality of life in developed areas and elsewhere on the Earth, life itself. In attempts to find solutions to these problems, we have created an ever growing inventory of manufactured goods, chemicals, drugs, ostensibly to improve the quality of life that has in fact contributed to the pollution of our environment. “Pollution prevention,” an environmental buzz word since the 1990s, encompasses designing processes that generate no waste to plants that emit only harmless compounds such as pure water.

      Zero defect and zero effect (ZDZE) is different from pollution prevention in that it converts raw materials into useful products or valuable resources that have “no defect” in manufactured products and “zero effect” has no adverse effect on health and environment. In this book, the meanings of “Zero Effect,” “Zero Discharge,” or “Zero Emissions” are complimentary and all terms are used interchangeably (Das 2005). Within the ZDZE paradigm the goal of resource extraction, refining, or commodity production is approached in much the same way that the mining, iron and steel, pulp and paper, petroleum, energy, automobiles, petrochemical, pharmaceutical, fertilizer, agricultural, and chemical industries go about processing raw materials. Sometimes the conversion of wastes or by‐products into resources having value to another industry is more efficient than the implementation of pollution prevention techniques – that is industrial ecology (also see Chapter 9).

      A waste is defined as an unwanted by‐product or damaged, defective, or superfluous material of a manufacturing process. Most often, in its current state, it has or is perceived to have no value. It may or may not be harmful or toxic if released to the environment. Pollution is any release of waste to environment (i.e. any routine or accidental emission, effluent, spill, discharge, or disposal to the air, land, or water) that contaminates or degrades the environment.

      In contrast, the U.S. Environmental Protection Agency (USEPA) (1992) definition of pollution prevention recognizes only source reduction and conservation, which encompasses only the upper two tiers in the hierarchy – minimize generation and minimize introduction. The USEPA describes the seven‐level hierarchy of Figure 1.1 as “environment management options.” The European Community, on the other hand, includes the entire hierarchy in its definition of pollution prevention. The tiers in the pollution prevention hierarchy are broadly described as follows.

       Minimize generation: Reduce to a minimum the formation of nonsalable by‐products in chemical reaction steps and waste constituents (such as tars, fines, etc.) in all chemical and physical separation steps.

       Minimize introduction: Cut down as much as possible on the amounts of process materials that pass through the system unreacted or are transformed to make waste. This implies minimizing the introduction of materials that are not essential ingredients in making the final product. For examples, plant designers can decide not to use water as a solvent when one of the reactants, intermediates, or products could serve the same function, or they can add air as an oxygen source, heat sink, diluent, or conveying gas instead of large volumes of nitrogen.

       Segregate and reuse: Avoid combining waste streams together with no consideration to the impact on toxicity or the cost of treatment. It may make sense to segregate a low‐volume, high‐toxicity wastewater stream from high‐volume, low‐toxicity wastewater streams. Examine each waste stream at the source and identify any that might be reused in the process or transformed or reclassified as valuable coproducts.

       Recycle: Many manufacturing facilities, especially chemical plants, have internal recycle streams that are considered part of the process. In addition, however, it is necessary to recycle externally such materials as polyester film and bottles, Tyvek envelopes, paper, and spent solvents.

       Recover energy value in waste: As a last resort, spent organic liquids, gaseous streams containing volatile organic compounds (VOCs), and hydrogen gas can be burned for their fuel value. Often the value of energy and resources required to make the original compounds is much greater than that which can be recovered by burning the waste streams for their fuel value (also see Appendix G).

       Treat for discharge: Before any waste stream is discharged to the environment, measures should be taken to lower its toxicity, turbidity, global warming potential, pathogen content, and so on. Examples include, but not limited to, biological wastewater treatment, carbon adsorption, filtration, and chemical oxidation.

       Safe disposal: Render waste streams completely harmless so that they do not adversely impact the environment. In this book, we define this as total conversion of waste constituents to carbon dioxide, water, and nontoxic minerals. An example would be posttreatment of a wastewater treatment plant effluent in a private wetland. So‐called secure landfills do not fall within this category unless the waste is totally encapsulated in granite.

      1.4.1

Скачать книгу