Bioaccumulation of the antifouling paint booster biocide Irgarol 1051 by the green alga Tetraselmis suecica

3,4-Dioxygenated xanthones as antifouling additives for marine coatings: in silico studies, seawater solubility, degradability, leaching, and antifouling performance

Marine biofouling pollution is a process that impacts ecosystems and the global economy. On the other hand, traditional antifouling (AF) marine coatings release persistent and toxic biocides that accumulate in sediments and aquatic organisms. To understand the putative impact on marine ecosystems of recently described and patented AF xanthones (xanthones 1 and 2), able to inhibit mussel settlement without acting as biocides, several in silico environmental fate predictions (bioaccumulation, biodegradation, and soil absorption) were calculated in this work. Subsequently, a degradation assay using treated seawater at different temperatures and light exposures was conducted for a period of 2 months to calculate their half-life (DT₅₀). Xanthone 2 was found to be non-persistent (DT₅₀ < 60 days) at 50 μM, contrary to xanthone 1 (DT₅₀ > 60 days). To evaluate the efficacy of both xanthones as AF agents, they were blended into four polymeric-based coating systems: polyurethane- and polydimethylsiloxane (PDMS)-based marine paints, as well as room-temperature-vulcanizing PDMS- and acrylic-based coatings. Despite their low water solubility, xanthones 1 and 2 demonstrated suitable leaching behaviors after 45 days. Overall, the generated xanthone-based coatings were able to decrease the attachment of the Mytilus galloprovincialis larvae after 40 h. This proof-of-concept and environmental impact evaluation will contribute to the search for truly environmental-friendly AF alternatives.

Glutathione S-transferase activity in aquatic macrophytes and halophytes and biotransformation potential for biocides

Glutathione S-transferase (GST) participates in the biotransformation of many xenobiotics including biocides. Its activity in plants is generally associated with their phytoremediation capabilities. Biocides have been used in agriculture and antifouling paints and they represent risks for the aquatic environment. The present study aimed to: (1) evaluate the basal GST activity in roots, stems, and leaves from thirteen plants (eleven aquatic macrophytes and two halophytes) collected at South Brazil wetlands; (2) estimate the biotransformation potential of Nothoscordum gracile for five biocides using competitive kinetic assays with 1-chloro-2,4-dinitrobenzene (CDNB), a typical GST substrate. The N. gracile, Spartina alterniflora and Cakile maritima presented the highest GST activities among the tested plants. The Lineweaver-Burk plot obtained from the GST competitive kinetic assays confirmed that the biocides chlorothalonil, 4,5-dichloro-N-octyl-3(2H)-isothiazolone (DCOIT), dichlofluanid, and diuron, but not irgarol, compete with the substrate CDNB for GST. Chlorothalonil and DCOIT showed the lowest IC₂₀ values (11.1 and 10.6 μM, respectively), followed by dichlofluanid (38.6 μM) and diuron (353.1 μM). The inhibition of GST-CDNB activity by 100 nM biocide was higher for chlorothalonil, DCOIT, and dichlofluanid (46.5, 49.0, and 45.1%, respectively) than for diuron (6.5%) and irgarol (2.2%). The present study indicates plant species that have significant GST activity and could be potentially used for phytoremediation. The competitive kinetic tests suggest that among the five biocides that were tested, chlorothalonil, DCOIT, and dichlofluanid are probably preferred for biotransformation via GST in plant.

Significance of antifouling paint flakes to the distribution of dichlorodiphenyltrichloroethanes (DDTs) in estuarine sediment

Recently published literature indicated that dichlorodiphenyltrichloroethane (DDT)-containing antifouling paint flakes were heterogeneously distributed within estuarine sediments. However, the significance of antifouling paint flakes in the fate and transport of DDT compounds and other organic pollutants in estuarine sediment is yet to be adequately addressed. To fill this knowledge gap, estuarine sediment and paint flakes from cabin and boat surfaces were collected from a fishery base in Guangdong Province of South China and analyzed for DDT compounds. Coarse fractioned samples collected from the vicinity of boat maintenance facilities contained appreciable amounts of colorful particles, which were identified as paint flakes by Fourier transform infrared spectroscopy. The highest concentrations of DDXs (sum of DDTs and its metabolites) occurred in the heavy-density (>1.7 g cm(-3)) fraction of coarse-size (200-2000 μm) sediments from near the boat maintenance facilities, suggesting the importance of paint flakes in the distribution pattern of "hot spots" in estuarine sediment. Moreover, the desorption rates of DDT compounds from paint flakes and the heavy-density fraction of coarse-size sediment were both extremely slow. Apparently, unevenly distributed paint flakes in sediment can artificially inflate the sorption capacity of heavy-density sediment for DDT compounds, and therefore can substantially change the environmental fate and behavior of hydrophobic organic chemicals in estuarine sediment. Finally, commonly used source diagnostic indices of DDT compounds were mostly grain-size and density dependent in sediment, as a result of the occurrence of paint flakes, which may strongly compromise the outcome of any source diagnostics efforts.

Risk assessment of triazine herbicides in surface waters and bioaccumulation of Irgarol and M1 by submerged aquatic vegetation in Southeast Florida

Irgarol is a common antifoulant present in coastal environments experiencing high boating activities. Irgarol, its degradation product M1, and the similarly structured herbicide Atrazine, are highly toxic to non-target marine organisms and thus pose a continual risk to the environment. Nearshore areas with intensive boating activity were assessed for environmental exposure to Irgarol, M1, and Atrazine. Irgarol levels up to 241 ng/L were measured in surface water collected at Key Largo Harbor. Irgarol's metabolite, M1, was detected at levels up to 50 ng/L. Atrazine levels reached 21 ng/L throughout Miami River, and were also detected in waters within Biscayne Bay Aquatic Preserve at 7 ± 4 ng/L. The Irgarol 90th percentile exposure concentration (176 ng/L) in Southeast Florida--including Biscayne Bay--surface waters were found to exceed most toxicity benchmarks, suggesting Irgarol concentrations may be high enough to cause undesired effects on aquatic plants. Indigenous species of SAVs were also collected throughout Southeast Florida and assessed for their Irgarol and M1 bioaccumulation capabilities. All SAV species collected revealed Irgarol bioaccumulation capabilities and a 90th centile bioconcentration factor (BCF) of 9830. Several of those species were also capable of bioaccumulating M1, with a 90th centile BCF of 391. A 43-day in situ transplant between an impacted area and a pristine area within Biscayne Bay waters showed SAVs were able to uptake Irgarol from the environment with quick kinetics: tissue concentrations were 66 times greater than the water concentration within 6 weeks. Halodule and Syringodium had the highest capacity to bioaccumulate from marina surface waters, as indicated by the Irgarol BCF (Halodule=6809, Syringodium=6681) and M1 BCF (Halodule=277, Syringodium=558). Halodule and Syringodium are therefore the best candidate species to serve as bioindicators indicators of acute Irgarol contamination.

Polygodial: a contact active antifouling biocide

Ongoing investigation of the candidate antifouling (AF) biocide polygodial (PG) has revealed that this compound may be contact active, whereby it can confer effect while remaining bound within a stable matrix. To test this hypothesis, the AF activity of PG-laced coatings was compared to that of seawater in which PG-laced coatings had been soaked. Four coating types spanning high to low affinity for PG were examined and AF activity was assessed based on inhibition of settlement and metamorphosis of larvae of three fouling organisms: Ciona savignyi Herdman, Mytilus galloprovincialis Lamarck and Spirobranchus caraniferus Gray. Direct exposure to the coatings had a significantly greater impact on larval metamorphosis than indirect exposure to seawater in which the coatings had been soaked. In particular, metamorphosis was almost completely inhibited by high-affinity coatings containing ≥ 200 ng of PG per replicate, while corresponding soaking waters had no detectable effect. These findings support the assertion that PG is contact active.

A comparison of toxicant-induced succession for five antifouling compounds on marine periphyton in SWIFT microcosms

Five antifouling biocides, chlorothalonile, dichlofluanide, medetomidine, tolylfluanide, and zinc pyrithione, were evaluated regarding their effect on the composition of the periphyton community and the subsequent toxicant-induced succession (TIS). The periphyton communities were exposed in a semi-static setting for 96 h using a SWIFT microcosm. As a measure of community composition, pigment profiles from the exposed communities were used as effect indicators and compared with unexposed parts of the same community using the Bray-Curtis dissimilarity index. Chlorothalonile caused changes in the community starting at 85 μg l(-1) while dichlofluanide had no effect even at the highest concentrations used, 810 μg l(-1). The related substance tolylfluanide only affected the community composition at 2700 μg l(-1). Medetomidine had a different response curve with a small effect on the community composition at 0.8 μg l(-1) which then disappeared only to reappear at 240 μg l(-1). Zinc pyrithione had the largest effect on the periphyton community with changes starting at 10 μg l(-1) and no detectable pigments at 100 μg l(-1). The changes in the community composition for the five substances were also compared using multidimensional scaling. When all substances were analyzed and plotted together, chlorothalonile, dichlofluanide, medetomidine, and tolylfluanide showed surprisingly similar effects compared to zinc pyrithione that gave very different TIS. However, when only chlorothalonile, dichlofluanide, and tolylfluanide were plotted together, clear differences in TIS between the three toxicants were revealed. Dichlofluanide only induced small effects, while concentration-dependent TIS trajectories for chlorothalonile and tolylfluanide took off in opposite directions indicating very different responses of the periphyton communities. This study demonstrates that substances with a similar chemical structure and mechanisms of action can have different effects on the community composition. With the exception of zinc pyrithione, none of the recorded effect levels were at concentrations reported from marine environments so far.

Risks of using antifouling biocides in aquaculture

Biocides are chemical substances that can deter or kill the microorganisms responsible for biofouling. The rapid expansion of the aquaculture industry is having a significant impact on the marine ecosystems. As the industry expands, it requires the use of more drugs, disinfectants and antifoulant compounds (biocides) to eliminate the microorganisms in the aquaculture facilities. The use of biocides in the aquatic environment, however, has proved to be harmful as it has toxic effects on the marine environment. Organic booster biocides were recently introduced as alternatives to the organotin compounds found in antifouling products after restrictions were imposed on the use of tributyltin (TBT). The replacement products are generally based on copper metal oxides and organic biocides. The biocides that are most commonly used in antifouling paints include chlorothalonil, dichlofluanid, DCOIT (4,5-dichloro-2-n-octyl-4-isothiazolin-3-one, Sea-nine 211^®), Diuron, Irgarol 1051, TCMS pyridine (2,3,3,6-tetrachloro-4-methylsulfonyl pyridine), zinc pyrithione and Zineb. There are two types of risks associated with the use of biocides in aquaculture: (i) predators and humans may ingest the fish and shellfish that have accumulated in these contaminants and (ii) the development of antibiotic resistance in bacteria. This paper provides an overview of the effects of antifouling (AF) biocides on aquatic organisms. It also provides some insights into the effects and risks of these compounds on non-target organisms.

Toxic and accumulative potential of the antifouling biocide and TBT successor irgarol on freshwater macrophytes: a pond mesocosm study

After the ban of tributyltin (TBT) for vessels not longer than 25 m in 1986, Irgarol has become a commonly used antifouling biocide. Irgarol is highly toxic to autotrophic organisms and has the potential to accumulate in organic material. In the literature, environmental concentrations of Irgarol up to 2.4 microg L(-1) were reported forfreshwater. Within a comprehensive freshwater mesocosm study, experiments were conducted to gain more information on the effects of Irgarol on macrophytes. Six indoor pond mesocosms were contaminated once with concentrations between 0.04 and 5 microgl(-1) Irgarol and monitored for 150 days; two mesocosms served as controls. The mesocosm study revealed that all macrophytes were directly affected by this single application. Myriophyllum verticillatum was the most sensitive macrophyte with an EC50 (Day 150) of 0.21 microg L(-1) Irgarol. The duckweed Spirodela polyrhiza was the least sensitive species tested in the mesocosms and number of fronds even increased with increasing Irgarol concentrations. Time-weighted average calculations yielded high BCF values of up to 10,580 L kg(-1) dry weight for M. verticillatum indicating a high potential for accumulation. The results give cause for concern that natural macrophyte communities are impaired at actual environmental concentrations.