Ships transport about 80 percent of world trade and transfer approximately three to five billion tons of ballast water internationally every year. Due to the likely presence of pollutants, the ballast water discharged by ships can have negative effects on aquatic ecosystems. This study was conducted on 10 ships that entered the Bushehr port to determine the effectiveness of the ballast water exchange method and also to specify the contents of heavy metals (Ni, Cd, Pb and Cu) in the water and sediment of the ships’ ballast tanks. The samples were collected from January 2017 to July 2018 during a cold and a hot season. The results indicate the values of heavy metals in the samples in this order: Ni> Cu > Pb > Cd. The heavy metals concentrations in the sediment samples did not exceed the standard of the National Oceanic and Atmospheric Administration (NOAA). Whereas, Cu and Ni in all water samples and Cd in samples 2 and 7 exceeded the NOAA quality standard value. A correlation analysis of the metals showed that the sources of heavy metals vary in water and sediment samples, except for Pb and Cu in sediment samples which a positively significant relationship were observed. The results also revealed that the ballast water exchange method cannot by itself be effective and an efficient management together with continuous monitoring seems to be essential to prevent pollution of the ballast tanks of the ships entering the Bushehr port.

Ballast water (BW) is a dead weight used by ships to provide stability in their journeys. It poses health, economic and ecological problems. Since 2017, the International Maritime Organization-IMO mandated management of BW. This research compares plankton mortality and microorganism inactivation in different BW treatments to identify possible decay models. Treatments include solar radiation (Srad), UV, H₂O₂ and advanced oxidation processes (AOPs).In the wild populations, the disinfection capacity was measured in natural seawater pumped from the Santa Marta port zone in Colombia. AOPs showed different models and effectiveness according to the treatment and microorganism. Plankton larger than 50 μm was the most resistant; therefore, it must be removed first by a previous filter. Wild microorganisms showed log-linear and log-linear tail decay models for most AOPs in E. coli. For Vibrio, the models were log-lineal tail and biphasic models.

Ballast water is a major vector of invasion by protozoans and metazoans. Bacterial invasion is less-well understood. We surveyed the bacterial diversity of ballast water from 26 container ships arriving at the Yangshan Deepwater Port, Shanghai, China during 2015–2016. We characterized the ballast microbiome using high-throughput sequencing (HTS) based on V4-V5 region of 16S rRNA genes. We simultaneously monitored physicochemical parameters of the ballast water, including temperature, pH, dissolved oxygen (DO), salinity, turbidity, total suspended solid (TSS), particulate organic carbon (POC), NO₂, NH₄, PO₄. Proteobacteria was the dominant phylum, comprising more than 50% of the OTUs of almost all vessels, followed by Bacteroidetes (12.08%), Actinobacteria (4.86%) Planctomycetes (3.24%) and Cyanobacteria (1.95%). The relative abundance of Cyanobacteria differed among vessels. It was negatively correlated with temperature, NO₃, pH, TSS, PO₄, and turbidity and positively correlated with NH₄, POC. The genus Synechococcus was the most common Cyanobacteria in our results. Escherichia coli were relatively rare; they are indicator-species of D-2 standards published by the IMO. The relative abundance of the genus Vibrio ranged from 0.003% to 24.88% among different vessels. Our results showed that HTS was able to profile the bacterial communities in ballast-waters, even when the approach was restricted by technical and other obstacles.

Although ballast water is a known vector for the global transport of microorganisms, the Ballast Water Management Convention only sets limits for indicator organisms and does not consider antibiotic resistance genes (ARGs). Herein, we examined the concentration of indicator organisms and prevalence of three ARGs (sul1, tet (M), and vanA) in a total of 53 ballast, 21 harbor, and 8 ocean samples collected in Singapore, China, South Africa, and California. E. coli was found in significantly higher concentrations in ballast samples obtained in Singapore and China compared to South Africa (Singapore, p = 0.040) and California (Singapore, p < 0.001; China, p = 0.038). Harbor samples from China had significantly higher concentrations of E. coli than Singapore (p = 0.049) and California (p = 0.001). When compared to ocean samples, there were significantly higher concentrations of normalized tet(M) in ballast samples from California (p = 0.011) and Singapore (p = 0.019) and in harbor samples from California (p = 0.018), Singapore (p = 0.010), and South Africa (p = 0.008). These findings suggest that microbial loads significantly differ among ports. Furthermore, certain ARGs are enriched in ballast and harbor waters when compared to ocean water, which suggests that ballast waters have the potential to either transport higher concentrations of certain ARGs or that ballast tank conditions may exert selective pressure for some ARGs.

The International Maritime Organization and U.S. Coast Guard have implemented regulations to reduce introductions of non-indigenous species via ballast water (BW). For phytoplankton, regulations limit discharges to <10 live/viable cells mL⁻¹ (size: 10–50 μm), ignoring other size fractions. Additionally, challenge conditions of 100 (shipboard) and 1000 (land-based) cells mL⁻¹ are required in BW management system certification testing. How these requirements correspond to natural phytoplankton populations is poorly resolved. We analyzed phytoplankton samples from 31 major ports to evaluate: a) how natural communities compare to challenge requirements and b) abundances of unregulated size fractions (i.e., <10 and ≥50 μm). None of the ports met land-based challenge conditions, and only 32% met requirements for shipboard testing. Approximately 71% of organisms ≥50 μm were centric diatoms, also unregulated by current protocols. This study demonstrates that current regulations do not consider natural phytoplankton populations, limiting control efforts for potentially harmful non-indigenous species.

The uptake and discharge of bivalve larvae through ballast water operations is a highly viable mechanism for transfer of shellfish. In this paper, we investigate the effects of common water treatment processes on the planktotrophic larvae of the two invasive species of shellfish, Mytilopsis sallei and Mytella strigata. The study found that common water treatment processes used in many ballast water treatment systems were effective for the removal of bivalve larvae, although later stages of larval forms required more effort to remove.

In this study, the amount of heavy metals such as Ni, Cd, Pb and Cu and some physiochemical factors including pH, temperature and total organic carbon (TOC) in the ballast water of the ships entering the Bushehr Port were measured for two years (cold and hot seasons) before and after the ballast water convention was enforced. The mean concentrations of Ni, Cd, Pb and Cu, before and after implementation of the convention were 46.55, 3.93, 5.36, 58.83 and 26.41, 2.12, 2.59, 23.54 ppb. It became clear that the concentrations of heavy metals after the implementation of the convention was lower in comparison and there was a significant difference (p < .05). It seems that continuous monitoring of the quality of the ballast water and determination of locations free of pollution and contamination in the Persian Gulf are necessary for ships that intend to exchange their ballast water in this Gulf.

The International Convention for the Control and Management of Ships’ Ballast Water and Sediments (IMO 2018 Edition) was adopted in 2004 and entered into force on 8 September 2017, aiming to introduce global regulations to control the transfer of potentially invasive species Resolution (IMO MEPC.207(62) 2011). These efforts are translated into a wide range of solutions for retrofitting and new building services, which is evidenced through the substantial amount of data disclosed and analysed by different parties showing that optimization processes will have an important role for the existent management systems. Analysing a ballast water management installation project for oil tankers, categorizing the stakeholders involved and assessing properly the outcomes from an engineering perspective are important matters. The experience considered at the BWM Convention and its amendments set an important call to the industry in terms of milestones. Avoiding any delay in terms of operation is not the only answer to this call but also setting up an optimized and sustainable operation after the implementation process. The project management, on the subfield of stakeholders’ management (Bourne 2016), brings a myriad of individuals connected to ballast water management matters with different levels of knowledge, experience and commitment from an engineering perspective. This article aims to measure these factors and the stakeholders’ experience based on qualitative research into the ballast water management convention, with emphasis on the installation process on board. The data herewith analysed was obtained from a series of interviews conducted from January 2019 to August 2019.

The discharge of ship ballast water (containing large amounts of alien organisms) has caused severe ecological hazards to marine environments. In this study, three metal elements (Ag, Fe, and Gd) were doped to nano-TiO₂ material respectively (content: 0.4%, 0.7%, and 1.0%) to improve inactivation effect of Escherichia coli and Enterococci in ballast water. Experimental results indicate that compared with the sole ultraviolet (UV) and the UV and original nano-TiO₂, the UV and metal-doped nano-TiO₂ increased the bacterial inactivation rate to different extents. For each metal element, high external metal content (1.0%) corresponded to high inactivation effort. The doping of Ag resulted in optimal inactivation effort, and the addition of Fe and Gd caused unobvious effort. At the end of the inactivation process (20 s), the UV and 1% Ag-doped nano-TiO₂ reached the highest logarithmic sterilization rates (0.915 for Escherichia coli and 0.805 for Enterococcus). The doping of Ag, Fe, and Gd did not change the anatase phase TiO₂ crystal form, and 1% Ag-doped nano-TiO₂ had the smallest particle diameter and the evenest distribution of nanoparticles. Compared with the sole UV, the UV and Ag-doped nano-TiO₂ treatment resulted in higher malondialdehyde contents (0.0646 μmol/L for Escherichia coli and 0.0529 μmol/L for Enterococci) and lower superoxide dismutase activities (0.672 U/mL for Escherichia coli and 0.792 U/mL for Enterococci), which were in accordance with high inactivation rates in these cases.

In the third paragraph of Introduction, the sentence “Few scholars have conducted static studies on dual-wavelength UV photocatalytic technologies (Ma 2018)”.