Ballast water treatment using UV/TiO2 advanced oxidation processes: An approach to invasive species prevention

Abstract Spread of marine invasive species (MIS) via ships’ ballast water causes global biotic homogenization and extinctions. In this study, a UV/TiO2 ballast water treatment system (BWTS) was designed to reduce transport of MIS. UV dose profiles simulated by computational fluid dynamics indicated that, depending on the flow rate and UV light intensity, the average applied UV dose was 260 mJ/cm2. Combined UV/TiO2 treatment produced excess hydroxyl radicals that were confirmed by high performance liquid chromatography using a trapping agent. We then compared the effectiveness of UV/TiO2 BWTS against UV-alone BWTS at two different UV doses (i.e., 100% and 75%). We found that, even though UV alone reduced the abundance of all tested organisms, UV/TiO2 significantly reduced the abundance of all groups and led to a greater reduction than UV alone. Each trial should include the storage of treated ballast water for at least 120 h according to Guideline G8 of the International Maritime Organization. Comparison tests after 120 h of storage period showed that the plankton densities of treated water for UV/TiO2 treatment in the ⩾50 μm group further deceased from 4 to 2 individuals (ind.)/m3, whereas those for UV-alone treatment increased from 6 to 57 ind./m3, revealing that UV/TiO2 treatment had the potential to inhibit plankton regrowth, but UV alone did not. Although the efficacy of both strategies increased after 120 h of storage period, the densities of microbes in discharge samples from the UV/TiO2 treatment were significantly lower than those in samples from UV-alone treatment. Moreover, the advantages of UV/TiO2 at low UV dose (i.e., 75%) were much greater and the concentrations of disinfection by-products (e.g., trihalomethanes, haloacetic acids) were observed in levels of 0.01–1 μg/L.

[1]  Efi Tsolaki,et al.  Technologies for ballast water treatment: a review , 2010 .

[2]  Marinko Učur,et al.  International convention for the control and management of ships’ ballast water and sediments (imo, 2004) , 2011 .

[3]  A. Fujishima,et al.  TiO2 Photocatalysis: A Historical Overview and Future Prospects , 2005 .

[4]  Numerical simulation of mixing process of gas-liquid impinging jet in ballast water discharge pipe , 2009 .

[5]  Dorin Boldor,et al.  Design and implementation of a continuous microwave heating system for ballast water treatment. , 2008, Environmental science & technology.

[6]  M. Pilson,et al.  An Introduction to the Chemistry of the Sea , 1998 .

[7]  D. Bahnemann,et al.  Mechanistic studies of water detoxification in illuminated TiO2 suspensions , 1991 .

[8]  Xinyong Li,et al.  Role of hydroxyl radicals and mechanism of Escherichia coli inactivation on Ag/AgBr/TiO2 nanotube array electrode under visible light irradiation. , 2012, Environmental science & technology.

[9]  E. Lancelot,et al.  Detection of hydroxyl radicals in rat striatum during transient focal cerebral ischemia: possible implication in tissue damage , 1995, Neuroscience Letters.

[10]  M. Tamburri,et al.  Enumerating Sparse Organisms in Ships’ Ballast Water: Why Counting to 10 Is Not So Easy , 2011, Environmental science & technology.

[11]  Duu-Jong Lee,et al.  Inactivation of Amphidinium sp. in ballast waters using UV/Ag-TiO2+O3 advanced oxidation treatment. , 2011, Bioresource technology.

[12]  Chang Nyung Kim,et al.  Computational fluid dynamics (CFD) modeling of UV disinfection in a closed-conduit reactor , 2011 .

[13]  Jun Ma,et al.  Formation of carbonaceous and nitrogenous disinfection by-products from the chlorination of Microcystis aeruginosa. , 2010, Water research.

[14]  E. Diamadopoulos,et al.  Electrochemical disinfection of simulated ballast water using Artemia salina as indicator , 2010 .

[15]  Allegra Cangelosi,et al.  Multidimensional approach to invasive species prevention. , 2013, Environmental science & technology.

[16]  J. Peres,et al.  Oxidation of p-hydroxybenzoic acid by UV radiation and by TiO2/UV radiation: comparison and modelling of reaction kinetic. , 2001, Journal of hazardous materials.

[17]  K. Liu,et al.  On the application of 4-hydroxybenzoic acid as a trapping agent to study hydroxyl radical generation during cerebral ischemia and reperfusion , 2002, Molecular and Cellular Biochemistry.

[18]  J. Yates,et al.  Photocatalysis on TiO2 Surfaces: Principles, Mechanisms, and Selected Results , 1995 .

[19]  C. Levings,et al.  Effect of a ballast water treatment system on survivorship of natural populations of marine plankton , 2001 .

[20]  H. You,et al.  Enhanced inactivation of Escherichia coli with Ag-coated TiO2 thin film under UV-C irradiation , 2011 .

[21]  S. Esplugas,et al.  Application of UV and UV/H2O2 to seawater: Disinfection and natural organic matter removal , 2012 .

[22]  B. V. Pepich,et al.  Collaborative study of EPA Method 317.0 for the determination of inorganic oxyhalide disinfection by-products in drinking water using ion chromatography with the addition of a postcolumn reagent for trace bromate analysis. , 2001, Journal of chromatographic science.

[23]  O. Vadstein,et al.  Recolonization by heterotrophic bacteria after UV irradiation or ozonation of seawater; a simulation of ballast water treatment. , 2010, Water research.

[24]  W. J. Cooper,et al.  Ozonation of seawater from different locations: formation and decay of total residual oxidant--implications for ballast water treatment. , 2006, Marine pollution bulletin.

[25]  B. Werschkun,et al.  Disinfection by-products in ballast water treatment: an evaluation of regulatory data. , 2012, Water research.

[26]  A. Lavín,et al.  The regrowth of phytoplankton cultures after UV disinfection. , 2013, Marine pollution bulletin.

[27]  Helge Liltved,et al.  Disinfection by-products and ecotoxicity of ballast water after oxidative treatment--results and experiences from seven years of full-scale testing of ballast water management systems. , 2013, Marine pollution bulletin.