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OPTIMISING THERMAL ENERGY RECOVERY

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OPTIMISING THERMAL ENERGY RECOVERY ( optimising-thermal-energy-recovery )

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Industrial Water Law was introduced to restrict the use of groundwater by the rapidly growing Japanese industries (Judd and Jefferson, 2003). This was followed by the introduction of the Federal Water Pollution Control Act of 1972 in the USA, and from there different countries and regions in the world started adopting policies for natural water protection. In industry, the decision for water reuse or recycling is usually based on the reliability and cost-effectiveness of the process to provide water of the desired quality. Most of the time, the cost benefit is largely or wholly determined by statutory requirements; for example, some industries may have zero liquid discharge imposed upon their operation; hence, in such cases wastewater recovery or reuse is no longer an option but an absolute necessity. There are also cases where the decision is solely based on economics. In this scenario, the total cost of purification to produce water of the desired quality is always considered against the cost of freshwater supply and wastewater discharge. In the industrial context, direct “closed loop” industrial water recycling is currently attracting greater interest and is being applied more often than the municipal system of water reclamation, especially in processes where other resources are recovered in addition to water (Judd and Jefferson, 2003). However, two major factors militate against its widespread application in some processes. Firstly, most industrial processes involve a number of individual operations that give rise to wastewaters of certain compositional ranges. These individual effluent streams are generally combined to produce wastewater whose resultant temporal variation in quality is immense, thus 48

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