Process integration techniques for optimizing seawater cooling systems and biocide discharge

This work addresses the problem of using seawater for cooling and the associated environmental problems caused by the usage and discharge of biocides. The discharged biocide and its byproducts are toxic to aquatic lives and must be decreased below certain discharge limits on load prior to discharge. The conventional approach has been to add biocide removal units as an end-of-pipe treatment. This work introduces an integrated approach to reducing biocide discharge though a set of coordinated strategies for in-plant modifications and biocide removal. In particular, process integration tools are used to reduce heating and cooling requirements through the synthesis of a heat-exchange network. Heat integration among process hot and cold streams is pursued economically by reconciling cost reduction in utilities versus any additional capital investment of the heat exchangers. Other strategies include maximization of the temperature range for seawater through the process and optimization of biocide dosage. This new approach has the advantage of providing cost savings while reducing the usage and discharge of biocides. A case study is used to illustrate the usefulness of this new approach and the accompanying design techniques.

[1]  Kaj-Mikael Björk,et al.  Solving large-scale retrofit heat exchanger network synthesis problems with mathematical optimization methods , 2005 .

[2]  U. V. Shenoy,et al.  Heat Exchanger Network Synthesis:: Process Optimization by Energy and Resource Analysis , 1995 .

[3]  L. Nowell,et al.  Photolysis of aqueous chlorine at sunlight and ultraviolet wavelengths—I. Degradation rates , 1992 .

[4]  J. C. Goldman,et al.  Chlorine disappearance in sea-water☆ , 1979 .

[5]  Brungs Wa Effects of residual chlorine on aquatic life. , 1973 .

[6]  Mahmoud M. El-Halwagi,et al.  Synthesis of optimal heat-induced separation networks , 1995 .

[7]  J. Oldfield,et al.  Corrosion problems caused by bromine formation in MSF desalination plants , 1981 .

[8]  S. R. Wild,et al.  Environmental management of coastal cooling water discharges in Hong Kong , 1998 .

[9]  P. Rochelle,et al.  Disinfection of Cryptosporidium parvum WITH polychromatic UV light , 2001 .

[10]  B. Linnhoff,et al.  The pinch design method for heat exchanger networks , 1983 .

[11]  Zdravko Kravanja,et al.  MINLP retrofit of heat exchanger networks comprising different exchanger types , 2004, Comput. Chem. Eng..

[12]  Petar Sabev Varbanov,et al.  Rules for paths construction for HENs debottlenecking , 2000 .

[13]  M. Stenstrom,et al.  Removal of organohalogens and organohalogen precursors in reclaimed wastewater—I , 1990 .

[14]  M. A. Yukselen,et al.  Inactivation of coliform bacteria in Black Sea waters due to solar radiation. , 2003, Environment international.

[15]  Leonard W. Hom,et al.  Kinetics of Chlorine Disinfection in an Ecosystem , 1972 .

[16]  T. Bott,et al.  Biocide Dosing Strategies for Biofilm Control , 2005 .

[17]  Lei Yang,et al.  Natural disinfection of wastewater in marine outfall fields , 2000 .

[18]  Mahmoud M. El-Halwagi,et al.  Pollution prevention through process integration , 1997 .

[19]  P. Goodman Effect of chlorination on materials for sea water cooling systems: a review of chemical reactions , 1987 .

[20]  R. Lambert,et al.  Disinfection kinetics: a new hypothesis and model for the tailing of log‐survivor/time curves , 2000, Journal of applied microbiology.