Skip to main content
Log in

Process integration techniques for optimizing seawater cooling systems and biocide discharge

  • Original Paper
  • Published:
Clean Technologies and Environmental Policy Aims and scope Submit manuscript

Abstract

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.

This is a preview of subscription content, log in via an institution to check access.

Access this article

Price excludes VAT (USA)
Tax calculation will be finalised during checkout.

Instant access to the full article PDF.

Fig. 1
Fig. 2
Fig. 3
Fig. 4
Fig. 5
Fig. 6
Fig. 7
Fig. 8
Fig. 9
Fig. 10

Similar content being viewed by others

Abbreviations

Q HU :

heating utility

Q HUAHI :

heating utility after heat integration

Q HUOriginal :

original heating utility

Q CU :

cooling utility

Q CUOriginal :

original cooling utility

Q HUAHI :

cooling utility after heat integration

F SW :

seawater flow rate

F Original :

currently used seawater flow rate

F CUAHI :

the required flow rate of seawater after heat integration

F CUATM :

the required flow rate of seawater after heat integration and temperature-span maximization

C P :

specific heat

D Biocide :

dosage of biocide as ppm or mg/l

D BiocideOptimal :

optimal biocide dosage

ΔT SW :

outlet temperature minus inlet temperature of cooled streams of exchanger

ΔT SW, max :

maximum outlet temperature minus inlet temperature of cooled streams of exchanger

T SW,out max :

maximum outlet temperature of seawater

ΔT SWOriginal :

the original outlet temperature minus inlet temperature of cooled streams of exchanger

ΔT SWRevised :

the revised original outlet temperature minus inlet temperature of cooled streams of exchanger

ΔT SWThermal Pollution :

regulated ΔT SW to prevent high temperatures discharge water to sea

L Biocide :

the amount of biocide added/discharged

\(L^{\rm Biocide}_{{\rm Current}_{\rm in}}\) :

the currently added amount of biocide to seawater

L BiocideRegulated :

the maximum amount of biocide regulated to be discharged to sea

\(L^{\rm Biocide}_{{\rm Reduction}_{\rm in}}\) :

reduction in added biocide amount from cooling reduction

\(L^{\rm Biocide}_{{\rm Reduced}_{\rm in}}\) :

amount of added biocide reduced from cooling reduction

References

  • Bauman LC, Stenstrom MK (1990a) Removal of organohalogens and organohalogen precursors in reclaimed wastewater. I. Water Res 24(8):949–955

    Article  CAS  Google Scholar 

  • Bauman LC, Stenstrom MK (1990b) Removal of organohalogens and organohalogen precursors in reclaimed wastewater. II. Water Res 24(8):957–964

    Article  CAS  Google Scholar 

  • Björk KM, Nordman R (2005) “Solving large-scale retrofit heat exchanger network synthesis problems with mathematical optimization methods”. Chem Eng Process 44(8):869–876

    Article  Google Scholar 

  • Brunges WA (1973) Effects of residual chlorine on aquatic life. J Water Pollut Control Fed 45(10):2180

    Google Scholar 

  • Combs R, Ammerer N (1998) Chlorine removal; ultraviolet light oxidation of chlorine in water. Ultra pure Water Apr., 21–24

  • El-Halwagi MM (1997) Pollution prevention through process integration. Systematic Desgin Tools. Academic Press, San Diego

    Google Scholar 

  • El-Halwagi MM (2006) Process integration. Elsevier, Amsterdam

    Google Scholar 

  • Elkin LM (1969) Urea. In: Institute SR (ed) Process economics program. Menlo Park, CA, USA, pp111–127

  • Goldman JC, Wuimby HL, Capuzzo JM (1979) Water Res 13:315

    Article  CAS  Google Scholar 

  • Goodman PD (1987) Effect of chlorine on materials for seawater cooling systems: a review of chemical reactions. Brit Corros J 22:56–62

    CAS  Google Scholar 

  • Grant DM, Bott TR (2003) Biocide dosing strategies for biofil control. Conference on heat exchanger fouling and cleaning: fundamentals and applications. Santa Fe, NM, USA

  • Hass CN, Asce M. General kinatics of disinfection processes. Philadelphia

  • Langford T (1977) Environmental management of coastal cooling discharges in Hong Kong. Chem Ind 612–616

  • Lind C (1995) Wastewater dechlorination options. Public Works, Sep., 69–70

  • Linnhoff B, Hindmarsh E (1983) The pinch design method for heat exchanger networks. Chem Eng Sci 38:745–763

    Article  CAS  Google Scholar 

  • Ma SWY, Kueh CSW, Chiu GWL, Wild SR, Yip JY (1998) Environmental management of coastal cooling water discharges in Hong Kong. Water Sci Technol 38:267–274

    Article  CAS  Google Scholar 

  • Mofidi AA, Baribeau H, Rochelle PA, De Leon R, Coffey BM, Green JF (2001) Disinfection of cryptosporidium parvum with polychromatic UV light. J Am Water Works Ass 93(6):95–109

    CAS  Google Scholar 

  • Nowell LH, Hoigne J (1992) Photolysis of aqueous chlorine at sunlight and ultraviolet wavelengths. I. Degradation rates. Water Res 26(5):593–598

    Article  CAS  Google Scholar 

  • Oldfield JW, Todd B (1981) Desalination 38:233

    Article  CAS  Google Scholar 

  • Shenoy UV (1995) Heat exchange network synthesis: process optimization by energy and resource analysis. Gulf Publ. Co., TX, USA

  • Soršak A, Kravanja Z (2004) “MINLP retrofit of heat exchanger networks comprising different exchanger types”. Comp Chem Eng 28(1–2):235–251

    Google Scholar 

  • Tjoe TN, Linnhoff B (1986) “Pinch technology retrofit: setting targets for an existing plant”. Chemical Engineering, 28 April 1986

  • United States Environmental Protection Agency (1998). National Primary Drinking Water Regulations; Disinfectants and Disinfection Byproducts, Final Rule, Federal Register, 63, 69392

  • Varbanov aP S, Klemeš J (2000) Rules for paths construction for HENs debottlenecking. App Therm Eng 20(15–16):1409–1420

    Article  Google Scholar 

  • White GC (1999) The handbook of chlorination and alternate disinfictants, 4th edn. Wiley, New York

    Google Scholar 

  • Yang L, Chang W-S, Lo Huang M-N (2000) Natural disinfection of wastewater in marine outfall fields. Water Res 34:743–750

    Article  CAS  Google Scholar 

  • Yukselen MA, Calli B, Gokyay O, Saatci A (2003) Inactivation of coliform bacteria in black Seawaters due to solar radiation. Environ Int 29:45–50

    Article  Google Scholar 

Download references

Author information

Authors and Affiliations

Authors

Corresponding author

Correspondence to Mahmoud M. El-Halwagi.

Rights and permissions

Reprints and permissions

About this article

Cite this article

Mahfouz, A.S.B., El-Halwagi, M.M. & Abdel-Wahab, A. Process integration techniques for optimizing seawater cooling systems and biocide discharge. Clean Techn Environ Policy 8, 203–215 (2006). https://doi.org/10.1007/s10098-006-0046-7

Download citation

  • Received:

  • Accepted:

  • Published:

  • Issue Date:

  • DOI: https://doi.org/10.1007/s10098-006-0046-7

Keywords

Navigation