Abstract
The International Maritime Organization (IMO) will enforce a new abundance-based performance standard for ballast water in September, 2017. Strong oxidants, like chlorine, have been proposed as a method for achieving this standard. However chlorine treatment of ballast water can produce hazardous trihalomethanes. We assessed maximum trihalomethane production from one chlorine dose for three types of ballast water (fresh, brackish and marine) and three levels of total organic carbon (TOC) concentration (natural, filtered, enhanced). While the current standard test considers a 5 day voyage, there is a high possibility of shorter trips and sudden change of plans that will release treated waters in the environment. Water source and TOC significantly affected trihalomethane production, with the highest amounts generated in brackish waters and enhanced TOC concentration. The concentration of brominated trihalomethanes increased from background levels and was highest in brackish water, followed by marine and fresh water.
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Agus E, Voutchkov N, Sedlak DL (2009) Disinfection by-products and their potential impact on the quality of water produced by desalination systems: a literature review. Desalination 237:214–237
Amy GL, Chadik PA, King PH, Cooper WJ (1984) Chlorine utilization during trihalomethane formation in the presence of ammonia and bromide. Environ Sci Technol 18:781–786
Boorman GA, Dellarco V, Dunnick JK, Chapin RE, Hunter S, Hauchman F, Gardner H, Cox M, Sills RC (1999) Drinking water disinfection byproducts: review and approach to toxicity evaluation. Environ Health Perspect 107:207–217
Boudjellaba D, Dron J, Revenko G, Démelas C, Boudenne JL (2016) Chlorination by-product concentration levels in seawater and fish of an industrialised bay (Gulf of Fos, France) exposed to multiple chlorinated effluents. Sci Total Environ 541:391–399
Bruchet A, Rousseau C, Mallevialle J (1990) Pyrolysis-GC-MS for investigating high-molecular-weight THM precursors and other refractory organics. J Am Water Works Assoc 82:66–74
Budziak D, Junior LR, Beltrame E, Carasek E (2007) Monitoring the formation of trihalomethanes in the effluents from a shrimp hatchery. Environ Monit Assess 127:435–444
Bull RJ, Birnbaum LS, Cantor KP, Rose JB, Butterworth BE, Pegram R, Tuomisto J (1995) Water chlorination: essential process or cancer hazard?. Fundam Appl Toxicol 28:155–166
Carlton JT (1987) Patterns of transoceanic marine biological invasions in the Pacific Ocean. Bull Mar Sci 41:452–465
Chang EE, Lin YP, Chiang PC (2001) Effects of bromide on the formation of THMs and HAAs. Chemosphere 43:1029–1034
Cowman GA, Singer PC (1995) Effect of bromide ion on haloacetic acid speciation resulting from chlorination and chloramination of aquatic humic substances. Environ Sci Technol 30:16–24
Fabbricino M, Korshin GV (2005) Formation of disinfection by-products and applicability of differential absorbance spectroscopy to monitor halogenation in chlorinated coastal and deep ocean seawater. Desalination 176:57–69
Ged EC, Boyer TH (2014) Effect of seawater intrusion on formation of bromine-containing trihalomethanes and haloacetic acids during chlorination. Desalination 345:85–93
Globallast IMO (2015) Ballast water as a vector. International Maritime Organization, London. http://globallast.imo.org/ballast-water-as-a-vector/
Gregg M, Rigby G, Hallegraeff GM (2009) Review of two decades of progress in the development of management options for reducing or eradicating phytoplankton, zooplankton and bacteria in ship’s ballast water. Aquat Invasions 4:521–565
IMO (2008a) Guidelines for approval of ballast water management systems (G8). International Maritime Organization, London. http://globallast.imo.org/wp-content/uploads/2015/01/G8-GUIDELINES-FOR-APPROVAL-OF-BALLAST-WATER-MANAGEMENT-SYSTEMS.pdf. Accessed 7 Dec 2015
IMO (2008b) Procedure for approval of BWM systems that make use of active substances (G9). International Maritime Organization, London. http://globallast.imo.org/wp-content/uploads/2015/01/G9-PROCEDURE-FOR-APPROVAL-OF-BALLAST-WATER-MANAGEMENT-SYSTEMS-THAT-MAKE-USE-OF-ACTIVE-SUBSTANCES.pdf. Accessed 7 Dec 2015
IMO (2016) International convention for the control and management of ships’ ballast water and sediments. International Maritime Organization, London. http://www.imo.org/en/About/Conventions/ListOfConventions/Pages/International-Convention-for-the-Control-and-Management-of-Ships’-Ballast-Water-and-Sediments-(BWM).aspx. Accessed 9 Sep 2016
Ivahnenko T, Zogorski JS (2006) Sources and occurrence of chloroform and other trihalomethanes in drinking-water supply wells in the United States, 1986–2001. USGS Report # 2006–5015
Liu Y, Thornton DC, Bianchi TS, Arnold WA, Shields MR, Chen J, Yvon-Lewis SA (2015) Dissolved organic matter composition drives the marine production of brominated very short-lived substances. Environ Sci Technol 49:3366–3374
Madabhushi BS (1999) What are trihalomethanes?. On Tap Spring 1999:18–19. http://www.nesc.wvu.edu/ndwc/articles/QandA/OTsp99_Q_A.pdf. Accessed 9 Sep 2016
Paim APS, Souza JB, Adorno MAT, Moraes EM (2007) Monitoring the trihalomethanes present in water after treatment with chlorine under laboratory condition. Environ Monit Assess 125:265–270
Paolucci EM, Hernandez MR, Potapov A, Lewis MA, MacIsaac HJ (2015) Hybrid system increases efficiency of ballast water treatment. J Appl Ecol 52:348–357
Singer PC (1999) Humic substances as precursors for potentially harmful disinfection by-products. Water Sci Technol 40:25–30
Stack MA, Fitzgerald G, O’Connell S, James KJ (2000) Measurement of trihalomethanes in potable and recreational waters using solid phase micro extraction with gas chromatography-mass spectrometry. Chemosphere 41:1821–1826
Symons JM, Krasner SW, Simms LA, Sclimenti M (1993) Measurement of THM and precursor concentrations revisited: the effect of bromide ion. J Am Water Works Assoc 85:51–62
Tsolaki E, Pitta P, Diamadopoulos E (2010) Electrochemical disinfection of simulated ballast water using Artemia salina as indicator. Chem Eng J 156(2):305–312
Werschkun B, Sommer Y, Banerji S (2012) Disinfection by-products in ballast water treatment: an evaluation of regulatory data. Water Res 46:4884–4901
Werschkun B, Banerji S, Basurko OC, David M, Fuhr F, Gollasch S et al (2014) Emerging risks from ballast water treatment: the run-up to the International Ballast Water Management Convention. Chemosphere 112:256–266
Zhang N, Ma B, Li J, Zhang Z (2013) Factors affecting formation of chemical by-products during ballast water treatment based on an advanced oxidation process. Chem Eng J 231:427–433
Zhao R, Lao W, Xu X (2004) Headspace liquid-phase microextraction of trihalomethanes in drinking water and their gas chromatographic determination. Talanta 62:751–756
Zimmer-Faust AG, Ambrose RF, Tamburri MN (2014) Evaluation of approaches to quantify total residual oxidants in ballast water management systems employing chlorine for disinfection. Water Sci Technol 70:1585–1593
Acknowledgements
We thank the captain and crew of the Helen C vessel for allowing us to collect ballast samples during port operations, C. van Overdijik, B. Middleton, S. Collins and S. Jarison for valuable assistance. We also want to thank the editor, Dr. Erin Bennett, and two anonymous reviewers who provided valuable comments to improve this work. This study was funded by a CONACYT graduate scholarship to MRH and NSERC Discovery grant and Canada Research Chair to HJM.
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Hernandez, M.R., Ismail, N., Drouillard, K.G. et al. Ships’ Ballast Water Treatment by Chlorination Can Generate Toxic Trihalomethanes. Bull Environ Contam Toxicol 99, 194–199 (2017). https://doi.org/10.1007/s00128-017-2125-3
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DOI: https://doi.org/10.1007/s00128-017-2125-3