Pseudomonas aeruginosa and other microbial indicators of pollution in fresh and marine waters of rio de janeiro,Brazil

Counts of Pseudomonas aeruginosa had a high positive correlation with counts of coliforms, fecal streptococci, presumptive pathogenic yeasts, and heterotrophic bacteria in surface waters of Rio de Janeiro. Pseudomonas aeruginosa counts were notably higher in fresh than in marine waters, and it was isolated from about 50% of marine and 100% of nonchlorinated freshwater samples that passed the fecal coliform based Brazilian bathing standards. The most probable number method for enumeration of P. aeruginosa contained this microbe in 90% of the positive tubes from freshwater samples, but it had reduced selectivity in marine waters with 37.5% false negative and 35% false positive results. Microbial indicators of fecal pollution were not effective for noting the presence of P. aeruginosa in freshwaters. © 1993 John Wiley & Sons Inc.     

Effects of specific dosages of magnesium and zinc on the teratogenicity of cadmium, nickel, and cobalt in Xenopus embryos, as assessed by the FETAX test

The objective of this study was to determine if exposure to divalent cations, Cd(2+), Ni(2+), and Co(2+) would lead to malformations in Xenopus laevis embryos, and whether addition of Mg(2+) and Zn(2+); separately and in combination, would reduce their toxicity and teratogenicity on the embryos of Xenopus laevis as assessed by 96-h FETAX tests. Results indicate that exposure to Cd(2+), Ni(2+) or Co(2+) lead to an increase in toxicity and teratogenicity in embryos, whereas Mg(2+), Zn(2+), or a combination of them reduced the toxic and teratogenic effects of these divalent cations. Modulation of Cd(2+), Ni(2+) or Co(2+) toxicity and teratogenicity by Mg(2+) and Zn(2+), varied with the metal. Zn(2+) was observed to be a better suppressor of Co(2+) toxicity and teratogenicity than Mg(2+). In contrast, Ni(2+), and Cd(2+) teratogenicity was reduced more prominently by Mg(2+). On the other hand, combination of Mg(2+) and Zn(2+) showed potentialization effect on all divalent cation toxicity and teratogenicity. We concluded that Mg(2+) and Zn(2+) reduced the toxicity and teratogenicity of Cd(2+), Ni(2+), Co(2+).     

pH dependent toxicity of five metals to three marine organisms

The pH of natural marine systems is relatively stable; this may explain why metal toxicity changes with pH have not been well documented. However, changes in metal toxicity with pH in marine waters are of concern in toxicity testing. During porewater toxicity testing pH can change 1–2 units as porewater is transferred from in situ to a test container. These changes in pH may alter metal toxicity. Also, deliberately altering the sample pH is an important toxicity identification and evaluations (TIE) manipulation designed to detect changes in ammonia toxicity. If altering pH also changes metal toxicity, this may confound interpretation of TIE manipulation results. This study demonstrates that alteration of pH can also change the toxicity of Cu, Cd, Ni, Pb, and Zn to Mysidopsis bahia (mysid), Ampelisca abdita (amphipod) and Vibrio fischerii [Microtox solid phase test (MSP)]. Changes in toxicity with respect to pH were metal and organism specific with the following trends. For the MSP assay, as pH decreased there was a decrease in toxicity for Pb, Ni, Cd, and Zn and an increase in toxicity for Cu. For mysids, as pH decreased, there was a decrease in toxicity for Pb and an increase in toxicity for Cu and Ni. For amphipods, Cu was the only metal that showed decreased toxicity with decreasing pH; the toxicity of all other metals for amphipods remained constant. Results of this study indicate changes in metal toxicity with respect to pH must be considered for porewater testing and TIE interpretation. ©1999 John Wiley & Sons, Inc. Environ Toxicol 14: 235–240, 1999     

Toxicity of culturable cyanobacteria strains isolated from the Portuguese coast.

Cyanobacteria are common inhabitants of terrestrial and aquatic ecosystems. In the aquatic environments their success is particularly well documented in fresh and brackish waters. References related to the occurrence of these organisms in marine habitats and especially in what concerns to toxicology are scarce. Reports of cyanotoxins in marine habitats are restricted to the warmer temperate and tropical regions. In this study, cyanobacteria strains belonging to the genera Cyanobacterium, Oscillatoria, Synechocystis and Synechococcus were isolated from rocky beaches along the Portuguese coast and were cultured and screened for toxicological properties. The toxicity to mice was observed after intraperitoneal injection of centrifuged and non-centrifuged extracts. The results showed a wide range of responses with strains showing no signs of poisoning and strains producing protracted or slightly protracted toxic effects. Neurotoxic symptoms and effects in liver, kidney, small intestine and lungs are reported. The identity of the toxic compounds is thus far unknown but the implication drawn from the present data is that more than one toxic compound is produced. There was a clear discrepancy between the toxicity of centrifuged and non-centrifuged extracts. In most cases the pellet was toxic indicating that toxicity can be associated with compounds tightly bound to the cell walls.     

Comparative in vitro cytotoxicity of nickel oxides and nickel-copper oxides to rat, mouse, and dog pulmonary alveolar macrophages

Metal oxides containing either Ni alone (NiO's) or both Ni and Cu (Ni-CuO's) are encountered during Ni refining. Six NiO compounds calcined at temperatures ranging from less than 650 to 1045 degrees and four Ni-CuO's containing from 6.9 to 28% Cu and 44 to 69% Ni were screened for their in vitro cytotoxicity to alveolar macrophages (AM). NiO's were less toxic to rat AM than were the Ni-CuO compounds. The toxicity of the Ni-CuO compounds increased with increasing Cu content and decreasing Ni content of the molecules, indicating that the toxicity was due to the Cu content of the molecules. AM obtained from beagle dogs, F344/N rats, and B6C3F1 mice displayed the following species sensitivities: dog greater than rat = mouse, with dog AM being most sensitive. The observed differences in species sensitivities correlated with differences in the phagocytic abilities of dog, rat, and mouse AM, with the ranking of phagocytic abilities of the AM in decreasing order of ability being dog greater than rat greater than mouse.     

Aquatic toxicology

Australia is blessed with a great diversity of unique species in its fresh waters and in the marine environment around its coast. There is evidence that human and natural events are impacting on these species. Such impacts are associated with various agricultural, industrial, and domestic practices and with natural and anthropogenically driven climate change. Among the species most affected are those living in aquatic and marine environments. Some of these, such as cyanobacteria and dinoflagellates, have the potential for toxicity. Linked to this, there is the potential benefit of harnessing the pharmacologic potential of these toxins.     

Aquatic toxicity of four alkylphenols (3-tert-butylphenol, 2-isopropylphenol, 3-isopropylphenol, and 4-isopropylphenol) and their binary mixtures to microbes, invertebrates, and fish

The acute and chronic toxicity of four simple alkylphenols with butyl and propyl substitutions was evaluated with aquatic microbes, invertebrates, and fish. These alkylphenols-3-tert-butylphenol, 2-isopropylphenol, 3-isopropylphenol, and 4-isopropylphenol-have been detected in various environmental media, but their impact on aquatic fauna has seldom been evaluated. Relative susceptibility to each phenolic varied by test species. The marine bacterium Vibrio fischeri was the most susceptible to the alkylphenols, up to 3 orders of magnitude more sensitive than species of higher trophic levels. For 4-isopropylphenol, the 5-min Microtox EC(50) value was 0.01 mg/L, whereas the EC(50) for Ceriodaphnia after a 48-h exposure was 10.1 mg/L. Notable differences in sensitivity to the alkylphenols was also observed with the Microtox assay: 4-isopropylphenol was > 200 times more toxic to V. fischeri than was 2-isopropylphenol (EC(50) = 2.72 mg/L). For V. fischeri, the mixture toxicity of the alkylphenols was additive in nature and was predicted by a concentration addition model. The energy of the lowest unoccupied molecular orbital (ELUMO) explained the observed toxicity of the individual alkylphenols to V. fischeri (r(2) = 0.92, p < 0.05). These results suggest that the mode of action of polar narcotic alkylphenols to V. fischeri is different than that of other test organisms, possibly because of the differences in the cell structure of the prokaryotic V. fischeri.     

A practical and user-friendly toxicity classification system with microbiotests for natural waters and wastewaters

Various types of toxicity classification systems have been elaborated by scientists in different countries, with the aim of attributing a hazard score to polluted environments or toxic wastewaters or of ranking them in accordance with increasing levels of toxicity. All these systems are based on batteries of standard acute toxicity tests (several of them including chronic assays as well) and are therefore dependent on the culturing and maintenance of live stocks of test organisms. Most systems require performance of the bioassays on dilution series of the original samples, for subsequent calculation of L(E)C50 or threshold toxicity values. Given the complexity and costs of these toxicity measurements, they can only be applied in well-equipped and highly specialized laboratories, and none of the classification methods so far has found general acceptance at the international level. The development of microbiotests that are independent of continuous culturing of live organisms has stimulated international collaboration. Coordinated at Ghent University, Belgium, collaboration by research groups from 10 countries in central and eastern Europe resulted in an alternative toxicity classification system that was easier to apply and substantially more cost effective than any of the earlier methods. This new system was developed and applied in the framework of a cooperation agreement between the Flemish community in Belgium and central and eastern Europe. The toxicity classification system is based on a battery of (culture-independent) microbiotests and is particularly suited for routine monitoring. It indeed only requires testing on undiluted samples of natural waters or wastewaters discharged into the aquatic environment, except for wastewaters that demonstrate more than 50% effect. The scoring system ranks the waters or wastewaters in 5 classes of increasing hazard/toxicity, with calculation of a weight factor for the concerned hazard/toxicity class. The new classification system was applied during 2000 by the participating laboratories on samples of river water, groundwaters, drinking waters, mine waters, sediment pore waters, industrial effluents, soil leachates, and waste dump leachates and was found to be easy to apply and reliable.     

Further studies on environmental factors that modify the toxicity of nickel to microbes

The toxicity of nickel (Ni) to mycelial growth of filamentous fungi and to replication of eubacteria, an actinomycete, and yeasts was influenced by various environmental abiotic factors. Sulfide and phosphate reduced the toxicity of Ni by the formation of insoluble salts. The clay minerals, montmorillonite and, to a much lesser extent, kaolinite, and the hydrous oxides of aluminum or manganese reduced the toxicity, presumably by the adsorption of cationic Ni to their net negatively charged surfaces. Amino acids, such as aspartic acid, complex organics, such as tryptone, casamino acids, and yeast extract, and chelating agents, such as citrate, 2,6-pyridine dicarboxylic acid, nitrilotriacetic acid, and ethylenediaminetetraacetic acid, significantly reduced the toxicity of Ni, presumably as the result of decreased attraction between the net negatively charged cell surfaces and the complexed Ni. The toxicity of Ni varied in different commercial media, with greater toxicities occurring in nutrient broth and MR-VP medium and lower toxicities occurring in lauryl tryptone, Elliker, microinoculum, and tryptic soy broths. Nickel had a lower toxicity in solid media gelled with Gelrite than with Bacto-agar.     

Bisphenol A causes mortality and reduced hatching success through increase of cell damage and dysfunction of antioxidant defense system in marine medaka embryo

In this study, marine medaka embryos were continuously exposed to different concentrations of bisphenol A (BPA; 200-1000 μg/L) during post fertilization. Mortality, hatching rate, and cellular death in marine medaka embryos were detected. In addition, survival rate of hatched larvae was measured to analyze whether BPA has persistent effects from BPA-exposed embryos to post-hatching period. Our results clearly showed that the hatching rate was decreased in a dose-dependent manner, while the mortality was increased with induction of cellular death and dysfunction of antioxidant defense system in marine medaka embryos. Of hatched larvae, the survival rate was decreased as the exposure concentrations increasing. Thus, our data suggested that early exposure of BPA caused embryonic toxicity, resulted in persistent effects on larval survival in marine medaka.     

Joint effects of temperature and copper exposure on developmental and gene-expression responses of the marine copepod Tigriopus japonicus

There is growing contamination of copper (Cu) in the marine environment, particularly after the ban of organotin compounds and the increase of the use of Cu-based antifouling paints. Although there are increasing research interests in temperature-dependent chemical toxicity to aquatic organisms, most existing studies focused on acute impacts of chemicals at high concentrations. This study aimed to investigate the interacting effect of temperature and copper exposure at environmentally relevant concentrations on survival and development in the marine copepod Tigriopus japonicus with a partial life-cycle toxicity test. Expressions of five stress response genes in the copepod, namely two glutathione S-transferases (GST-S and GST-O), two heat shock proteins (HSP70 and HSP90), and glutathione reductase (GR) were also investigated. The copepod’s survival was significantly impaired at 15 °C after development to adult stage, while its developmental time reduced significantly with increasing temperature. Copper at the two environmentally relevant test concentrations had no significant impacts on these apical endpoints whereas the interaction between Cu and temperature was more significant in modulating gene expressions. GST-S, GST-O and HSP90 genes in copepods exposed to 100 µg Cu L⁻¹ were significantly upregulated at 20 °C. At 32 °C, most genes were either insignificantly expressed or down-regulated, compared to the control, likely suggesting that thermal stress inhibited the copepod’s antioxidative defense system. Overall, the results revealed that the joint Cu and thermal stresses have significantly elicited antioxidative system in the copepods. It clearly demonstrated the need for more fundamental studies about potential impacts of different environmental factors such as temperature on chemical toxicity under realistic scenario of marine pollution.

     

Differential effects of NAD, nicotinamide and related compounds upon growth and nucleoside incorporation in human cells

Two human melanoma cell lines, MM96 and MM127, were found to be highly sensitive to the toxicity of adenosine (D50 100-150 micrograms/ml) compared with other melanoma lines. HeLa cells and a lymphoblastoid line (D50 greater than 500 micrograms/ml). The MM127 line was also sensitive to NAD (D50 41 micrograms/ml) compared with the other lines (D50 greater than 400 micrograms/ml), and accumulated three-fold more NAD-derived isotopic label. Nicotinamide exhibited little toxicity in any cell type (D50 greater than 400 micrograms/ml); 25-100 micrograms/ml nicotinamide greatly increased the plating efficiency of melanoma cells and fibroblasts when low levels of foetal calf serum were used. The toxicity of DNA-damaging agents (alkylating agents and u.v.) in melanoma cells was not reduced in the presence of NAD, adenosine or nicotinamide. Studies of the effects of the latter compounds upon the incorporation of deoxynucleosides showed that: (a) melanoma cells have lower purine pools than fibroblasts; (b) [3H]deoxyguanosine incorporation was inhibited more than [3H]deoxyadenosine incorporation; (c) incorporation of [3H]deoxyadenosine and [3H]deoxyguanosine into RNA was inhibited by adenosine, thus providing a method for determination of guanine-specific DNA repair; and (d) NAD enhanced thymidine incorporation in intact melanoma cells but not in fibroblasts, in a pattern similar to the release from template restriction previously reported for permeabilised tumour cells.     

Hydromineral balance in the marine gulf toadfish (Opsanus beta) exposed to waterborne or infused nickel

The effects of acute Ni exposure on the marine gulf toadfish (Opsanus beta) were investigated via separate exposures to waterborne nickel (Ni) and arterially infused Ni. Of the plasma electrolytes measured after 72 h of waterborne exposure (215.3 and 606.1 microM Ni in SW (salinity of 34)), only plasma [Ca2+] was significantly impacted (approximately 55% decrease at both exposure concentrations). At both exposure concentrations, plasma [Ni] was regulated for 24h, after which a linear accumulation over time occurred. Accumulation of Ni in the plasma, and in tissues in direct contact with seawater (gill, stomach, and intestine), was roughly proportional to the Ni concentration of the exposure water. Hydromineral balance in the intestinal fluid (IF) was markedly impacted, with Na(+), Cl(-), SO(4)(2-), K+, and Mg2+ concentrations elevated after 72 h of exposure to waterborne Ni. Following arterial Ni infusion (0.40 micromolNikg(-1)h(-1)), perturbation of hydromineral balance of the intestinal fluid was specific only to Na+ (significantly elevated by Ni infusion) and Mg2+ (significantly decreased by Ni infusion). Nitrogen excretion was not significantly impacted by Ni infusion. In all tissues save the kidney, Ni accumulation via infusion was only a fraction of that observed during waterborne exposures. Remarkably, the kidney Ni burden following infusion was almost identical to that resulting from both waterborne exposures, suggesting homeostatic control. Ni excretion, dominated at 24 h by extrarenal routes, was primarily a function of renal excretion by 72 h of infusion. The sum excretion from infused toadfish was relatively efficient, accounting for over 40% of the infused dose by 72 h. Mechanistic knowledge of the mechanisms of toxicity of waterborne Ni in marine systems is a critical component to the development of physiologically based modeling approaches to accurately predict Ni toxicity in marine and estuarine ecosystems.     

Increased metal bioavailability following alteration of freshwater dissolved organic carbon by ultraviolet B radiation exposure

Dissolved organic carbon (DOC) is critically important in the chemistry of freshwater. It complexes heavy metals, making them less bioavailable to aquatic organisms, and absorbs and attenuates UVB radiation, undergoing degradation and alteration in the process. This study examined changes in metal toxicity to the freshwater green alga Pseudokirchneriella subcapitata in high- and low-DOC natural water samples after exposure to UVB radiation. Brown-water and clear-water samples were irradiated for 0, 5, and 10 days. The DOC concentrations of the samples were measured, and they were subsequently spiked with Cu, Ni, Zn, Cd, Co, and Pb and used in algal bioassays to measure changes in metal toxicity following irradiation. DOC concentrations declined only 20% with UVB irradiation in both samples, although DOC concentration was much higher in the brown-water sample than in the clear-water sample. In the brown-water sample metal toxicity increased up to 78% after 10 days of UVB irradiation for Cu, Zn, Co and Pb, but not for Ni and Cd. Changes were less evident in the clear-water sample. The differences observed between IC(50) values for relatively fresh, high-DOC water from the headwaters of the Raisin River and much "older," low-DOC water from Lake Simcoe point to the likelihood of the effects observed in this study being many times greater in the natural environment because of very long exposure to solar radiation. Alteration of DOC by UVB irradiation may influence primary productivity and species composition, especially in waters in which metal concentrations are high.     

Effect of the test media and toxicity of LAS on the growth of <Emphasis Type="Italic">Isochrysis galbana</Emphasis>

In this paper, the toxicity of linear alkylbenzene sulfonate (LAS) was evaluated in the marine microalga Isochrysis galbana using data of growth inhibition toxicity tests at 96-h exposure time. Toxicity was examined in standard conditions and by means of the modification of two variables of the test media: (1) the dilution water and (2) the content of nutrients in the test medium. For this purpose, a total of 10 toxicity test were designed: five dilution waters, four natural marine waters and one synthetic seawater; each in two different nutritive conditions, saturated nutrient concentration (SC) by the addition of modified f/2 nutritive medium, and natural nutrient concentration (NC), i.e., without the addition of f/2. At threshold toxicity levels, the dilution waters used in the test and the nutrient concentrations did not affect the toxicity of LAS. At IC₅₀ concentrations, the toxicity of LAS is influenced by both variables: under SC conditions, the toxic effect of LAS diminishes, obtaining in all the tests IC₅₀ > 10 mg/L LAS. Under NC conditions, IC₅₀ concentrations ranging between 3.15 and 9.26 mg/L LAS have been obtained.     

Toxicity of phenanthrene and lindane mixtures to marine invertebrates

Surface waters near industrialized and agricultural areas are contaminated with hundreds of different pollutants from a variety of sources. Methods for measurement of sediment, surface water, and porewater toxicity in marine environments include the sea urchin (Arbacia punctulata) fertilization and embryological development tests and copepod (Schizopera knabeni) survival and hatching success assessment. The concentration addition model was applied to determine whether toxicity of two compounds, phenanthrene (polycyclic aromatic hydrocarbon) and lindane (organochlorine pesticide), when combined can be accurately assessed because of similar modes of action. Mixture analysis determined the sea urchin fertilization test to exhibit additivity (TU(mix) = 1.13), while the copepod test exhibited a synergistic effect (TU(mix) = 0.22). Mixture toxicity data for the sea urchin embryological test were not conclusive because of the lack of toxicity of the individual chemicals. The synergistic effect to copepods is a concern as it indicates that greater toxic effects may occur when the compounds are present in mixtures. Results from this research suggest that increased toxicity to some categories of organisms should be expected near agricultural and industrial areas where pesticides and other types of compounds may occur simultaneously.     

Overview of key phytoplankton toxins and their recent occurrence in the North and Baltic Seas

The frequency and intensity of harmful algal blooms (HABs) appear to be on the rise globally. There is also evidence of the geographic spreading of toxic strains of these algae. Consequently, methods had to be established and new ones are still needed for the evaluation of possible hazards caused by increased algal toxin production in the marine food chain. Different clinical effects of algae-related poisoning have attracted scientific attention; paralytic shellfish poisoning, diarrhetic shellfish poisoning, and amnesic shellfish poisoning are among the most common. Additionally, cyanobacteria (blue-green algae) in brackish waters often produce neurotoxic and hepatotoxic substances. Bioassays with mice or rats are common methods to determine algal and cyanobacterial toxins. However, biological tests are not really satisfactory because of their low sensitivity. In addition, there is growing public opposition to animal testing. Therefore, there has been increasing effort to determine algal toxins by chemical methods. Plankton samples from different European marine and brackish waters were taken during research cruises and analyzed on board directly. The ship routes covered marine areas in the northwest Atlantic, Orkney Islands, east coast of Scotland, and the North and Baltic seas. The first results on the occurrence and frequency of harmful algal species were obtained in 1997 and 1998. During the 2000 cruise an HPLC/MS coupling was established on board, and algal toxins were measured directly after extraction of the plankton samples. In contrast to earlier cruises, the sampling areas were changed in 2000 to focusing on coastal zones. The occurrence of toxic algae in these areas was compared to toxin formation during HABs in the open sea. It was found that the toxicity of the algal blooms depended on the prevailing local conditions. This observation was also confirmed by monitoring cyanobacterial blooms in the Baltic Sea. Optimal weather conditions, for example, during the summers of 1997 and 2003, favored blooms of cyanobacteria in all regions of the Baltic. The dominant species regarding the HABs in the Baltic was Nodularia spumigena. However, in addition to high concentrations of Nodularia spumigena in coastal zones, other blue-green algae are involved in bloom formation, with changes in plankton communities influencing both toxin profiles and toxicity.     

Comparison of the Qwiklite algal bioluminescence test with marine algal growth rate inhibition bioassays

Although marine algal bioassays based on growth rate inhibition over 72-96 h have been widely used to assess the toxicity of contaminants in waters and sediments, changes in pH over the test duration can lead to changes in contaminant speciation and consequently an under- or over-estimation of toxicity. In addition, high cell densities are used in order to obtain a detectable response, further reducing the tests' environmental relevance in marine waters. There is a need for rapid acute tests with ecologically relevant test endpoints that may be used as surrogates for longer-term chronic tests. This study compares the sensitivity and reproducibility of a rapid marine dinoflagellate (Pyrocystis lunula) bioluminescence test (QwikLite) with standard algal growth rate bioassays (Nitzschia closterium and Entomoneis c.f. punctulata) using ammonia and several antifouling agents (tributyltin [TBT], copper, and diuron) as reference toxicants. QwikLite was of similar sensitivity to ammonia as standard algal growth rate tests, but was less sensitive to copper, diuron and TBT, with 24-h EC50 values of 10 +/- 1.1 mg N/L, 0.128 +/- 0.021 mg Cu/L, 19 +/- 13 mg diuron/L, and 0.226 +/- 0.028 mg TBT/L. Inter-test precision using different batches of P. lunula was generally acceptable. On the basis of NOEC values, QwikLite was more sensitive to copper and ammonia at 25 degrees C than at 21 degrees C. QwikLite shows promise as a rapid, inexpensive screening test for acute toxicity of contaminants in marine environments.     

Effect of cystine,selenium, and fish protein on the toxicity and metabolism of methylmercury in rats

Investigations were made of the effect of 0.4% cystine, 0.6 ppm selenium, and fish protein on the toxicity and metabolism of mercury from methylmercuric chloride in male and female weanling rats. When diets with 10% protein and adequate amounts of other nutrients contained 25 ppm mercury, cystine reduced toxicity, selenium as sodium selenite had a greater effect in reducing toxicity, and the combination of cystine and selenium produced a considerably greater additive effect, as measured by increased growth and survival time. Toxicity signs were reduced when fish protein replaced casein in the basal diet, and a 20% protein level from either source reduced toxicity symptoms as compared to a 10% protein level. Cystine, selenium, and fish protein did not inhibit mercury toxicity by increasing its elimination from the body via the urine and feces and, in fact, slightly more mercury was retained when cystine and selenium were added to diets. Few differences were found in the deposition of mercury in tissues that could be attributed to cystine, selenium, and fish protein. The major difference found was in one experiment in which mercury concentrations in the kidney were considerably lower when diets contained cystine, selenium, and fish protein. Possible explanations for the effects observed in these studies included a reduction in mercury accumulation and, hence, damage in the kidney, complexing of mercury by the additives evaluated, and conversion of organic mercury to the less toxic inorganic form.     

Does light-stick content pose any threat to marine organisms?

Light-stick is a light attractor used in longline fishing which is often dumped or lost into the ocean after used, becoming a potential pollutant to marine organisms. In the present study, toxicity was evaluated by exposing Artemia to light-stick contents. The effects were observed on the survival of nauplii and hatchability of cysts. The LC(50) was 0.063mLL(-1) after 24h of exposure, whilst hatchability was 100% reduced after 48h of exposure to 0.8mLL(-1). The results showed that its content can be toxic to marine organisms, especially under low dilution conditions or direct contact.