Neurotoxic effects of sublethal concentrations of cyanobacterial extract containing anatoxin-a(s) on Nauphoeta cinerea cockroaches.

The detection of cyanotoxins, such as the anatoxin-a(s), is essential to ensure the biological safety of water environments. Here, we propose the use of Nauphoeta cinerea cockroaches as an alternative biological model for the biomonitoring of the activity of anatoxin-a(s) in aquatic systems. In order to validate our proposed model, we compared the effects of a cyanobacterial extract containing anatoxin-a(s) (CECA) with those of the organophosphate trichlorfon (Tn) on biochemical and physiological parameters of the nervous system of Nauphoeta cinerea cockroaches. In brain homogenates from cockroaches, CECA (5 and 50 µg/g) inhibited acetylcholinesterase (AChE) activity by 53 ±â€¯2% and 51 ±â€¯7%, respectively, while Tn (5 and 50 µg/g) inhibited AChE activity by 35 ±â€¯4% and 80 ±â€¯9%, respectively (p < 0.05; n = 6). Moreover, CECA at concentrations of 5, 25, and 50 µg/g decreased the locomotor activity of the cockroaches, diminishing the distance travelled and increasing the frequency and duration of immobile episodes similarly to Tn (0.3 µg/g) (p < 0.05, n = 40, respectively). CECA (5, 25 and 50 µg/g) induced an increase in the leg grooming behavior, but not in the movement of antennae, similarly to the effect of Tn (0.3 µg/g). In addition, both CECA (50 µg/200 µl) and Tn (0.3 µg/200 µl) induced a negative chronotropism in the insect heart (37 ±â€¯1 and 47 ±â€¯8 beats/min in 30 min, respectively) (n = 9, p > 0.05). Finally, CECA (50 µg/g), Tn (0.3 µg/g) and neostigmine (50 µg/g) caused significant neuromuscular failure, as indicated by the monitoring of the in vivo neuromuscular function of the cockroaches, during 100 min (n = 6, p < 0.05, respectively). In conclusion, sublethal doses of CECA provoked entomotoxicity. The Tn-like effects of CECA on Nauphoeta cinerea cockroaches encompass both the central and peripheral nervous systems in our insect model. The inhibitory activity of CECA on AChE boosts a cascade of signaling events involving octopaminergic/dopaminergic neurotransmission. Therefore, this study indicates that this insect model could potentially be used as a powerful, practical, and inexpensive tool to understand the impacts of eutrophication and for orientating decontamination processes.

Cyanobacterial Toxins of the Laurentian Great Lakes, Their Toxicological Effects, and Numerical Limits in Drinking Water.

Cyanobacteria are ubiquitous phototrophic bacteria that inhabit diverse environments across the planet. Seasonally, they dominate many eutrophic lakes impacted by excess nitrogen (N) and phosphorus (P) forming dense accumulations of biomass known as cyanobacterial harmful algal blooms or cyanoHABs. Their dominance in eutrophic lakes is attributed to a variety of unique adaptations including N and P concentrating mechanisms, N2 fixation, colony formation that inhibits predation, vertical movement via gas vesicles, and the production of toxic or otherwise bioactive molecules. While some of these molecules have been explored for their medicinal benefits, others are potent toxins harmful to humans, animals, and other wildlife known as cyanotoxins. In humans these cyanotoxins affect various tissues, including the liver, central and peripheral nervous system, kidneys, and reproductive organs among others. They induce acute effects at low doses in the parts-per-billion range and some are tumor promoters linked to chronic diseases such as liver and colorectal cancer. The occurrence of cyanoHABs and cyanotoxins in lakes presents challenges for maintaining safe recreational aquatic environments and the production of potable drinking water. CyanoHABs are a growing problem in the North American (Laurentian) Great Lakes basin. This review summarizes information on the occurrence of cyanoHABs in the Great Lakes, toxicological effects of cyanotoxins, and appropriate numerical limits on cyanotoxins in finished drinking water.

A systematic review on guanitoxin: General characteristics and ecological risks.

Guanitoxin (GNT) is a potent cyanotoxin, with a relatively low number of publications (n = 51) compared to other cyanotoxins. Among the published studies, 35 % were on the effect of the toxin in animals, mainly in rodents and in vitro testing, followed by studies that identified species of cyanobacteria that produce GNT in aquatic systems and consequently accidental poisoning in wild and domestic animals (27 %). Studies that developed or tested methods for identifying the molecule, based on colorimetric and analytical techniques, represented 14 %, while 8 % were on GNT biosynthesis. Review articles and chemical isolation (6 %) and on the stability of the molecule (4 %) were the topics with the lowest number of publications. The results show the occurrence of GNT was identified mainly in eutrophic environments with a higher incidence in the American continent. Chemical characteristics of the molecule, such as short half-life in the environment, instability in solutions with alkaline pH values, temperature >23 °C, added to the lack of an analytical standard, are factors that make it difficult to identify and quantify it. However, GNT monitoring can be performed using LC-MS-MRM methods or genes specific to the newly discovered molecule.

Availability of Guanitoxin in Water Samples Containing Sphaerospermopsis torques-reginae Cells Submitted to Dissolution Tests.

Guanitoxin (GNT) is a potent neurotoxin produced by freshwater cyanobacteria that can cause the deaths of wild and domestic animals. Through reports of animal intoxication by cyanobacteria cells that produce GNT, this study aimed to investigate the bio-accessibility of GNT in simulated solutions of the gastrointestinal content in order to understand the process of toxicosis promoted by GNT in vivo. Dissolution tests were conducted with a mixture of Sphaerospermopsis torques-reginae (Cyanobacteria; Nostocales) cultures (30%) and gastrointestinal solutions with and without proteolytic enzymes (70%) at a temperature of 37 °C and rotation at 100 rpm for 2 h. The identification of GNT was performed by LC-QqQ-MS/MS through the transitions [M + H]+m/z 253 > 58 and [M + H]+m/z 253 > 159, which showed high concentrations of GNT in simulated gastric fluid solutions (p-value < 0.001) in comparison to simulated solutions of intestinal content. The gastric solution with pepsin promoted the stability of GNT (p-value < 0.05) compared to the simulated solution of gastric fluid at the same pH without the enzyme. However, the results showed that GNT is also available in intestinal fluids for a period of 2 h, and solutions containing the pancreatin enzyme influenced the bio-accessibility of the toxin more compared to the intestinal medium without enzyme (p-value < 0.05). Therefore, the bio-accessibility of the toxin must be considered both in the stomach and in the intestine, and may help in the diagnosis and prediction of exposure and risk in vivo through the oral ingestion of GNT-producing cyanobacteria cells.

Use of cholinesterase activity as an ecotoxicological marker to assess anatoxin-a(s) exposure: Responses of two cladoceran species belonging to contrasting geographical regions.

The specificity of cholinesterase (ChE) activity to detect the presence of anatoxin-a(s) and sublethal effects of a 7-day exposure to Anabaena spiroides extract containing anatoxin-a(s) were assessed in two freshwater cladoceran species. Activities of ChE of both Pseudosida ramosa and Daphnia magna can be used to indicate the presence of the neurotoxin anatoxin-a(s), but not for the hepatotoxic microcystin. Activity of ChE of P. ramosa, however, performed better as a biomarker of exposure to A. spiroides than that of D. magna. Furthermore, sublethal exposure to A. spiroides extract significantly inhibited the ChE activity in P. ramosa and negatively affected both individual and population endpoints. For D. magna, the inhibition of ChE activity was not related to effects at higher levels of biological organization, since no direct effect was recorded on the individual and population endpoints. The activity of ChE in P. ramosa also proved to be a good predictor of chronic effects of the A. spiroides extract at higher levels of biological organization, since 48-h ChE inhibition was linked to the sublethal effects on the individual and population. These relationships could not be established for D. magna. Since relationships between the effects of A. spiroides extract at different levels of biological organization were species-specific, it can be concluded that the choice of test organism interferes with the accuracy of the environment risk assessment of this neurotoxin and, hence, the use of native species is recommended for its assessment.

Acute effects of Anabaena spiroides extract and paraoxon-methyl on freshwater cladocerans from tropical and temperate regions: links between the ChE activity and survival and its implications for tropical ecotoxicological studies.

Cholinesterase (ChE) activity was measured in Pseudosida ramosa and Daphnia magna, which had previously been exposed to Anabaena spiroides extract or to paraoxon-methyl for 48 h. These activities were then related to survival at 48 h. For A. spiroides extract, the observed 48-h LC50 was 2.27 and 2.70 × 10(6)cells mL(-1), while for paraoxon-methyl it was 0.60 and 2.17 µg L(-1), respectively, for P. ramosa and D. magna. Dose-response relationships were obtained for both P. ramosa and D. magna, when exposed to A. spiroides extract or paraoxon-methyl. Thus, when the tested concentrations of the toxicants increased, ChE activity and survival decreased. The ratio between 48-h IC50 for ChE and 48-h LC50 ranged from 75% to 81% for P. ramosa and from 77% to 81% for D. magna. This indicated that the concentrations of both A. spiroides extract and paraoxon-methyl that cause 50% mortality also inhibit ChE activity by 50%. Also, it was found that, for P. ramosa, a 50% inhibition of ChE activity was associated with a survival of 59.5% and 60.9%, respectively, for A. spiroides extract and paraoxon-methyl. However, for D. magna, at high levels of inhibition of ChE activity, almost no mortality was detected. In this specific case, 50% inhibition of the ChE activity was associated with 90.4 and 95.4% survival for A. spiroides extract and paraoxon-methyl, respectively. In contrast, enzyme inhibition slightly above 60% had a strong detrimental effect on survival in D. magna. These different patterns found in the relationship between ChE inhibition and survival may be due to species-specific differences in the affinities of both acetylcholinesterase and pseudocholinesterases, since the cladoceran ChE assays were performed with whole-body homogenates. In conclusion, when using ChE as a biochemical biomarker in risk assessment of cyanobacterial neurotoxic blooms in tropical regions, it is strongly recommended that native species are used, since our results revealed that P. ramosa was more sensitive than D. magna for both assay endpoints and both toxicants. Furthermore, the relationship between ChE activity and survival had a species-specific response. Therefore, the use of the model species D. magna in acute toxicity tests and ChE assays in tropical regions may lead to errors in the estimation of risks to the local species.

Can mixtures of cyanotoxins represent a risk to the zooplankton? The case study of Daphnia magna Straus exposed to hepatotoxic and neurotoxic cyanobacterial extracts.

Worldwide, cyanobacterial blooms have been increasing in intensity and frequency, with toxic cyanobacteria sometimes dominant throughout the year in many freshwater bodies. Since the coexistence of more than one type of cyanotoxins in freshwater environments is a common phenomenon, studies on the joint effects of these toxins would be very useful. In this study, the single and combined effects of two cyanotoxins with different modes of action (hepatotoxic and neurotoxic) on the survival (lethal exposure) and feeding (sublethal exposure) of the cladoceran Daphnia magna were investigated. With the single exposures, it was observed that both the survival and feeding activity of the daphnids were impaired by the hepatotoxic and neurotoxic extracts at environmentally relevant concentrations. In the combined exposures, both survival and feeding rate endpoints showed a good fit to the independent action model. For the acute assay and 24h exposure period in the feeding inhibition test, there was no interaction between components of the hepatotoxic and neurotoxic extracts, although a slight tendency to a synergistic deviation could be seen in the feeding rates. On the other hand, for the 4h post-exposure period, a synergistic deviation was found in feeding rates at all mixture concentrations tested. Hence, the combined exposure of hepatotoxins and neurotoxins should also be taken into account in risk assessments of freshwater bodies, since the mixture of these toxins can result in more severe post-exposure effects on the feeding of daphnids than the sum of those expected for single exposures.

Effects of a cyanobacterial extract containing-anatoxin-a(s) on the cardiac rhythm of Leurolestes circunvagans

This work presents the effects of an anatoxin-a(s)-containing extract on a cockroach semi-isolated heart preparation and the results supporting the extract’s biological activity on acetylcholinesterase (purified from ell). The presence of the toxin in cyanobacterial strains Anabaena spiroides (ITEP-024, ITEP-025 and ITEP-026) isolated from the Tapacurá reservoir in Pernambuco, Brazil, was confirmed by means of liquid chromatography coupled to an ion-trap mass spectrometer. The anticholinesterase activity was assessed biochemically by the Ellman test and was confirmed by measuring the cockroach’s heart rate. The concentration of the extract containing the tested anatoxin-a(s) (antx-a(s)) (10, 16 and 100 μg.μL-1) inhibited the eel acetylcholinesterase (AChE) by more than 90%. The cockroach cardiac frequency increased by a maximum of about 20% within 29 min after the addition of 2.5x10³ μg of extract containing antxa (s).g-1 bw (n=9, p<0.05). Our results strongly indicate that antx-a(s) is capable of exerting biological effects on cockroach, indicating that more research might be conducted to determine its role in the environment, especially on insects.

Investigação de mecanismos bioquímicos e fisiológicos em organismos expostos a anatoxina-a(s) / Study of the biochemical and physiologycal mechanisms in organisms exposed to anatoxin-a(s)

A anatoxina-a(s) (antx-a(s)) é uma neurotoxina produzida por cianobactérias, cujo mecanismo de ação conhecido consiste na inibição irreversível da atividade da enzima acetilcolinesterase (AChE). Em razão da instabilidade da molécula e da inexistência de um padrão analítico, as informações referentes a presença dessa toxina nos reservatórios de água doce e, a completa elucidação dos processos envolvidos na sua toxicidade, são escassas. Na última década, a pesquisa referente a capacidade dos inseticidas organofosforados de induzir estresse oxidativo em humanos e animais tem sido bastante importante. Pelo fato da antx-a(s) ser o único organofosforado produzido por cianobactérias conhecido, este trabalho teve como objetivo investigar os mecanismos bioquímicos envolvidos na ação pró-oxidante de extratos aquosos contendo antx-a(s). A atividade das enzimas colinesterásicas AChE e butirilcolinesterase (BuChE) e, das enzimas antioxidantes catalase (CAT), glutationa peroxidase (GPx), glutationa redutase (GR) e superóxido dismutase (SOD) foram avaliadas em dois modelos experimentais: (i) Camundongos Swiss tratados por via intraperitoneal (ip) com uma dose sub-letal (20 mg.kg-1) de extrato contendo antx-a(s) e sacrificados após 24 h, 48 h, 7 e 14 dias e, (ii) sementes de alfafa regadas com extrato contendo antx-a(s) por um período de 7 dias. Também foi avaliado o efeito de extratos contendo antx-a(s) em coração de baratas da espécie Leurolestes circunvagans. A atividade enzimática das colinesterases avaliadas em camundongos tratados com extrato contendo antx-a(s) manteve-se inibida 58% até 48 h após tratamento (n=9, p<0,001), voltando a níveis normais (comparada ao controle) a partir do sétimo dia (n=10, p>0,05). Em contraposição, as alterações na atividade das enzimas antioxidantes avaliadas iniciaram-se após 48 h do tratamento, quando foi observada uma diminuição na atividade das enzimas CAT e GPx (n=9, p<0,001). No sétimo dia, enquanto a atividade das enzimas CAT...

Anatoxin-a(s) (antx-a(s)) is a cyanobacterial neurotoxin whose principal mechanism of action is the irreversible inhibition of the enzymatic activity of acetylcholinesterase (AChE). Because of the molecule´s instability and the lack of an analytical standard, the occurrence of this toxin in freshwater reservoirs and the knowledge of the whole events related to its toxicity are scarce. In the last decade, research related to organophosphates insecticides capability to induce oxidative stress in humans and animals has been profuse. Considering that antx-a(s) is the unique organophosphate produced by cyanobacteria currently known; the main of this work was to investigate the biochemical mechanism related to the pro-oxidant capacity of antx-a(s)-containing extracts. In order to achieve the objective, there was determined the activity of cholinesterasic and antioxidant enzymes such as acetylcholinesterase (AChE), butirylcholinesterase (BuChE), catalase (CAT), glutathione peroxidase (GPx), glutathione reductase (GR) and superoxide dismutase (SOD). Two experimental models were used: (i) Swiss mice were treated intraperitoneally (ip) with 20 mg.kg-1 of antx-a(s)-containing extract and sacrificed after 24 h, 48 h, 7 and 14 days of treatment and, (ii) alfalfa seeds were irrigated with antx-a(s)-containing extract for 7 days. Additionally, the cardiac effect of antx-a(s)-containing extract on Leurolestes circunvagans cockroach was evaluated. The AChE and BuChE activity in mice treated with antx-a(s)-containing extract stayed inhibited more than 55% during 48 h (n=9, p<0,001). Normal activity of both enzymes was observed after seven days of treatment. By the other hand, changes in the antioxidant enzymes activity only began after the second day of treatment. Initially, both CAT and GPx showed lower activity than the control group after 48 h. Among those enzymes, GPx showed the highest decreased activity (n=9, p<0,001). After seven days, while the antx-a(s)- containing...