Bioassay of mycotoxins using terrestrial and aquatic, animal and plant species

Agricultural contaminants in amphibian breeding ponds: Occurrence, risk and correlation with agricultural land use

Anthropogenic pressure such as agricultural pollution globally affects amphibian populations. In this study, a total of 178 different compounds from five agrochemical groups (i.e. antimicrobial drugs residues (ADRs), coccidiostats and anthelmintics, heavy metals, mycotoxins and pesticides) were determined monthly, from March until June 2019 in 26 amphibian breeding ponds in Flanders, Belgium. Furthermore, a possible correlation between the number and concentration of selected contaminants that were found and the percentage of arable land within a 200 m radius was studied. Within each group, the highest detected concentrations were obtained for 4-epioxytetracycline (0.422 μg L^-1), levamisole (0.550 μg L^-1), zinc (333.1 μg L^-1), 3-acetyldeoxynivalenol (0.013 μg L^-1), and terbuthylazine (38.7 μg L^-1), respectively, with detection frequencies ranging from 1 (i.e. 3-acetyldeoxynivalenol) to 26 (i.e. zinc) out of 26 ponds. Based on reported acute and chronic ecotoxicological endpoints, detected concentrations of bifenthrin, cadmium, copper, cypermethrin, hexachlorobenzene, mercury, terbuthylazine, and zinc pose a substantial ecological risk to aquatic invertebrates such as Daphnia magna and Ceriodaphnia dubia, which both play a role in the food web and potentially in amphibian disease dynamics. Additionally, the detected concentrations of copper were high enough to exert chronic toxicity in the gray treefrog (Hyla versicolor). The number of detected compounds per pond ranged between 0 and 5 (ADRs), 0 - 2 (coccidiostats and anthelmintics), 1 - 7 (heavy metals), 0 - 4 (mycotoxins), and 0 - 12 (pesticides) across the four months. Furthermore, no significant correlation was demonstrated between the number of detected compounds per pond, as well as the detected concentrations of 4-epioxytetracycline, levamisole, copper, zinc, enniatin B and terbuthylazine, and the percentage of arable land within a 200 m radius. For heavy metals and pesticides, the number of compounds per pond varied significantly between months. Conclusively, amphibian breeding ponds in Flanders were frequently contaminated with agrochemicals, yielding concentrations up to the high μg per liter level, regardless of the percentage surrounding arable land, however showing temporal variation for heavy metals and pesticides. This research also identifies potential hazardous substances which may be added to the European watch list (CD 2018/408/EC) in the future.

Changes of DNA Damage Effect of T-2 or Deoxynivalenol Toxins during Three Weeks Exposure in Common Carp (Cyprinus carpio L.) Revealed by LORD-Q PCR

The present study aimed to adapt a Long-run Real-time DNA Damage Quantification (LORD-Q) qPCR-based method for the analysis of the mitochondrial genome of Common carp (Cyprinus carpio L.) and detect the DNA damaging effect of T-2 (4.11 mg kg⁻¹) and deoxynivalenol (5.96 mg kg⁻¹) mycotoxins in a 3-week feeding period. One-year-old Common carp were treated in groups (control, T-2 and DON). The mycotoxins were sprayed over the complete pelleted feed, and samples were taken weekly. Following the adaptation of LORD-Q PCR method for the Common carp species, the number of lesions were calculated to determine the amount of DNA damage. In the first and second weeks, the T-2 and the DON treated groups differed significantly from each other; however these differences disappeared in the third week. There was a significant difference in the DNA lesion values between weeks 1 and 3 in the deoxynivalenol-contaminated groups. While in the T-2 treated groups, the DNA lesion values were significantly reduced on weeks 2 and 3 compared to week 1. The results suggested that the trichothecene mycotoxins have a relevant DNA damaging effect.

Multi-residue analysis of 20 mycotoxins including major metabolites and emerging mycotoxins in freshwater using UHPLC-MS/MS and application to freshwater ponds in flanders, Belgium

Mycotoxins are known for their negative impact on human and animal health as they frequently contaminate food and feed products from crop origin that are consumed by humans and animals. Furthermore, mycotoxins can leach out of plant tissue, to be transported through runoff water into nearby ponds where they can exert negative effects on aquatic organisms, such as fish, amphibians and zooplankton. The overall goal of this study was to develop a SPE-UHPLC-MS/MS method for the detection and quantification of multiple mycotoxins in amphibian breeding ponds. The method was validated and yielded acceptable within-run and between-run apparent recoveries and precision, as well as good linearity. Matrix effects (i.e. 75.7-109.6%, ≤ 17.8% RSD) were evaluated using water from 20 different ponds in Flanders, Belgium. By incorporating internal standards, overall results improved and adequate precision values (i.e. ≤ 15%) were obtained according to the EMA guideline. Additionally, extraction recovery (n = 3) was evaluated, yielding good results for all mycotoxins (i.e. 75.3-109.1%, ≤15% RSD), except for AME (i.e. 6.7 ± 0.7%), which implied the need for a matrix-matched calibration curve. Detection sensitivity was in the low nanograms per liter range. Storage stability experiments indicated that sample storage at 4 °C in amber glass bottles and analysis performed within 96 h after sampling was sufficient to avoid loss by degradation for all compounds, excluding β-ZAL and β-ZEL, for which analysis within 24 h is more indicated. The method was successfully applied to water samples originating from 18 amphibian breeding ponds situated across Flanders. Overall, enniatins B, B1 and A1 were most commonly detected at maximum concentrations of 6.9, 3.3 and 2.6 ng L^-1, respectively, followed by detection of beauvericin (1.1 ng L^-1 and < 1 ng L^-1), alternariol monomethyl ether (< 10 ng L^-1), HT2-toxin (< 40 ng L^-1), zearalenone (< 25 ng L^-1) and α-zearalanol (< 10 ng L^-1). We believe that this method will boost further research into the dynamics and ecotoxicological impact of mycotoxins in aquatic environments.

Microbial Detoxification of Deoxynivalenol (DON), Assessed via a Lemna minor L. Bioassay, through Biotransformation to 3-epi-DON and 3-epi-DOM-1

Mycotoxins are toxic metabolites produced by fungi. To mitigate mycotoxins in food or feed, biotransformation is an emerging technology in which microorganisms degrade toxins into non-toxic metabolites. To monitor deoxynivalenol (DON) biotransformation, analytical tools such as ELISA and liquid chromatography coupled to tandem mass spectrometry (LC-MS/MS) are typically used. However, these techniques do not give a decisive answer about the remaining toxicity of possible biotransformation products. Hence, a bioassay using Lemna minor L. was developed. A dose-response analysis revealed significant inhibition in the growth of L. minor exposed to DON concentrations of 0.25 mg/L and higher. Concentrations above 1 mg/L were lethal for the plant. This bioassay is far more sensitive than previously described systems. The bioassay was implemented to screen microbial enrichment cultures, originating from rumen fluid, soil, digestate and activated sludge, on their biotransformation and detoxification capability of DON. The enrichment cultures originating from soil and activated sludge were capable of detoxifying and degrading 5 and 50 mg/L DON. In addition, the metabolites 3-epi-DON and the epimer of de-epoxy-DON (3-epi-DOM-1) were found as biotransformation products of both consortia. Our work provides a new valuable tool to screen microbial cultures for their detoxification capacity.

Fungal secondary metabolite dynamics in fungus-grazer interactions: novel insights and unanswered questions

In response to fungivore grazing fungi are assumed to have evolved secondary metabolite-based defense mechanisms that harm and repel grazers, and hence provide a benefit to the metabolite producer. However, since research into the ecological meaning of highly diverse fungal secondary metabolites is still in its infancy, many central questions still remain. Which components of the enormous metabolite diversity of fungi act as direct chemical defense mechanisms against grazers? Is the proposed chemical defense of fungi induced by grazer attack? Which role do volatile compounds play in communicating noxiousness to grazers? What is the relative impact of grazers and that of interactions with competing microbes on the evolution of fungal secondary metabolism? Here, I briefly summarize and discuss the results of the very few studies that have tried to tackle some of these questions by (i) using secondary metabolite mutant fungi in controlled experiments with grazers, and by (ii) investigating fungal secondary metabolism as a flexible means to adapt to grazer-rich niches.

Use of the genus Artemia in ecotoxicity testing

Information related to varied uses of several species of the genus Artemia (commonly known as brine shrimp), is dispersed among literature from several scientific areas, such as Ecology, Physiology, Ecotoxicology, Aquaculture and Genetics. The present paper reviews information related to Artemia that may be considered relevant for ecotoxicity testing. Integration of different areas of scientific knowledge concerning biology, life cycle and environmental needs of Artemia is of crucial importance when considering the interpretation of results drawn from tests involving this genus. Furthermore, this paper provides suggestions to overcome problems related to toxicity assessment with the use of Artemia as test organism in bioassays, under the scope of estuarine, marine and hypersaline environments. Aspects related to variability in results, adoptable toxicity end-points, culture conditions, characteristics of species and strains, influence of geographical origins over physiological features and responses to exposure to chemical agents are considered.

Cytotoxicity of fungal metabolites to lepidopteran (Spodoptera frugiperda) cell line (SF-9)

The toxicity of sixteen fungal metabolites produced by some entomopathogenic fungi or biological control fungi agents was evaluated on lepidopteran Spodoptera frugiperda (SF-9) cell line by Trypan blue dye exclusion and MTT-colorimetric assay, after 48 h of incubation. No statistical difference was found between IC50values (50% Inhibiting Concentration) and CC50 values (50% Cytotoxicity Concentration) obtained by MTT test and Trypan blue dye exclusion for each fungal metabolite. By MTT assay, the cytotoxicity ranking was fusarenon X (IC50 0.3 microM) = diacetoxyscirpenol (IC50 0.5 microM) = beauvericin (IC50 2.5 microM) = nivalenol (IC50 5.3 microM) = enniatin (IC50 6.6 microM) > or = gliotoxin (IC50 7.5 microM) > zearalenone (IC50 17.5 microM) > deoxynivalenol (IC50 47.6 microM). By Trypan blue dye exclusion the cytotoxicity ranking was fusarenon X (CC50 0.4 microM) = diacetoxyscirpenol (CC50 1.1 microM) beauvericin = (CC50 3.0 microM)=gliotoxin (CC50 4.0 microM) = enniatin (CC50 6.7 microM) > or = nivalenol (CC50 9.5 microM) > zearalenone (CC50 18.3 microM) > deoxynivalenol (CC50 45.0 microM). The comparison with other bioassays showed that the SF-9 insect cell line could represent a further tool to screen for the toxic effects of fungal metabolites especially for beauvericin, gliotoxin, and zearalenone.

Comparison of the toxicity of reference mycotoxins and spore extracts of common indoor moulds

There is an unclear endangering potential by toxic influences of inhaled conidiospores and therefore the conidia of indoor mould species were cultured and toxicologically examined after their mechanical disintegration. For this purpose high-performance liquid chromatography (HPLC) and three colorimetric bioassays, the PTGT (pollen tube growth test), the MB (methylene blue) and the MTT (methylthiazoltetrazolium) assay were applied. The sensitivity of the biological methods was evaluated by using 12 reference mycotoxins and 3 structural cell wall components. Only in one extract of disintegrated spores (Aspergillus fumigatus) a mycotoxin (0.22 microg gliotoxin/6.2 x 10(8) spores) was determined. All nine spore extracts, however, turned out to be cytotoxic and in this case the MTT assay was remarkably more sensitive than the two other test methods. The IC50 values of six different spore extracts determined by the MTT assay were lower than 10(6) spores/well (well = 0.2 ml) whereas the IC50 values determined by the MB assay and PTGT were higher than 10(6) spores per 0.2 ml for each spore extract. An examination of four spore extracts, which were fractionated depending on their polarity by HPLC, showed that single substances as well as synergistic effects contribute to the toxic properties of the spores. The results of this work indicate a health hazard due to toxic effects after the inhalation of extremely high spore concentrations of indoor moulds. This risk will also exist if the spores do not contain any mycotoxins.

CYTOTOXICITY INDUCED BY NIVALENOL, DEOXYNIVALENOL, AND FUMONISIN B1 IN THE SF-9 INSECT CELL LINE

The toxicity of the mycotoxins nivalenol (NIV), deoxynivalenol (DON), and fumonisin B1 (FB1) was studied in the lepidopteran Spodoptera frugiperda (SF-9) cells, by the trypan blue dye-exclusion and 3-(4,5-dimethylthiozole-2-yl)-2,5-biphenyl tetrazolium bromide (MTT) tests, uptake analyses of cytotoxicity, and cell metabolism, respectively. Deoxyribonucleic acid analysis by flow cytometry was used to identify apoptosis and cell cycle distribution. After 48 h of exposure, the MTT and trypan blue dye-exclusion tests indicated that NIV was significantly more toxic than DON, and both were significantly more toxic than FB1. The IC50 (mycotoxin concentration resulting in 50% inhibition of proliferation) values for NIV and DON were 4.5 and 41 microM, and the CC50 (mycotoxin concentration that caused 50% cytotoxicity) values were 9.5 and 45 microM, respectively. At the highest concentration of FB1 (100 microM), there was 80% viability. With the same incubation time, cell cycle distribution showed an arrest of cells in the G0/G1 phase in the presence of NIV (up to 0.3 microM), DON (up to 3 microM), and FB1 (up to 10 microM). Morphological evidence of apoptosis was related to the toxicity of the substances in that the more toxic NIV induced late apoptosis, whereas DON and FB1 produced less-severe morphological changes characteristic of early apoptosis. This study suggests that NIV is more toxic than DON, which in turn is more toxic than FB1. These mycotoxins can modify the normal progression of the cell cycle and induce an apoptotic process.

Indoor mold, toxigenic fungi, and Stachybotrys chartarum: infectious disease perspective

Damp buildings often have a moldy smell or obvious mold growth; some molds are human pathogens. This has caused concern regarding health effects of moldy indoor environments and has resulted in many studies of moisture- and mold-damaged buildings. Recently, there have been reports of severe illness as a result of indoor mold exposure, particularly due to Stachybotrys chartarum. While many authors describe a direct relationship between fungal contamination and illness, close examination of the literature reveals a confusing picture. Here, we review the evidence regarding indoor mold exposure and mycotoxicosis, with an emphasis on S. chartarum. We also examine possible end-organ effects, including pulmonary, immunologic, neurologic, and oncologic disorders. We discuss the Cleveland infant idiopathic pulmonary hemorrhage reports in detail, since they provided important impetus for concerns about Stachybotrys. Some valid concerns exist regarding the relationship between indoor mold exposure and human disease. Review of the literature reveals certain fungus-disease associations in humans, including ergotism (Claviceps species), alimentary toxic aleukia (Fusarium), and liver disease (Aspergillys). While many papers suggest a similar relationship between Stachybotrys and human disease, the studies nearly uniformly suffer from significant methodological flaws, making their findings inconclusive. As a result, we have not found well-substantiated supportive evidence of serious illness due to Stachybotrys exposure in the contemporary environment. To address issues of indoor mold-related illness, there is an urgent need for studies using objective markers of illness, relevant animal models, proper epidemiologic techniques, and examination of confounding factors.

Cytotoxicity assays for mycotoxins produced by Fusarium strains: a review

Mycotoxins are naturally occurring toxic secondary metabolites of fungi that may be present in food and feed. Several of these mycotoxins have been associated with human and animal diseases. Fusarium species, found worldwide in cereals and other food types for human and animal consumption, are the most important toxigenic fungi in northern temperate regions. The overall economical loss and the detrimental health effects in humans and animals of mycotoxin contamination are enormous and therefore, rapid screening methods will form an important tool in the protection of humans and animals as well as to minimize economical losses by early detection. An overview of methods for the determination of cytotoxicity and the application of such bioassays to screen solid fungal cultures, cereals, respectively, food/feedstuffs for the presence and toxic potential of Fusarium mycotoxins is presented. Various cell lines including different endpoints of toxicity using vertebrate cells and the predictive value of the in vitro assays are reviewed. Bioassays are compared with existing chemical analytical methods and the possibilities and limitations of such systems are discussed. The review is based on 149 references.

A yeast bioassay for trichothecenes

Like all eucaryotic cells, yeasts are sensitive to trichothecenes, especially T-2 toxin and verrucarin A. Based on this sensitivity, a yeast bioassay was developed to evaluate the toxicity of corn samples. The bioassay was optimized using spiked maize extracts. The toxicity of samples was defined as toxicity equivalent to a certain concentration of T-2 toxin standards. The assay can be performed on crude extracts, but the results are more precise after column clean-up. The test can also be used for the screening of trichothecene toxicity in general. The relative standard deviation (RSD) at 85 % growth inhibition (EC85) was 4.5% for the T-2 toxin standards (n = 8). This corresponds to an initial T-2 toxin concentration of approximately 58 ppb in the corn sample. Samples containing 188 and 113 ppb T-2 toxin caused a growth inhibition higher than 85%, whereas samples with toxin concentrations of 56 and 19 ppb had a growth inhibition less than 85%. Therefore the test can be used for the qualitative evaluation of corn samples up to a level of 58 ppb +/- 2.8 ppb. The bioassay is easy to perform with minimum requirements for equipment. Results can be obtained within 24 h and a large number of samples can be analysed daily. The costs are low and the results obtained are repeatable. With some modifications this test can be used for toxicity studies on trichothecene metabolites as well as for extracts with unknown compounds with properties similar to trichothecenes.

The use of the chicken embryo screening test and brine shrimp (Artemia salina) bioassays to assess the toxicity of fumonisin B1 mycotoxin

Chicken embryos and brine shrimp naulpii were utilized in short-term toxicity bioassays to assess their sensitivity to the mycotoxin fumonisin B1 (FB1). Fertile chicken eggs (Cobb x) were dosed with FB1 on day 2 of incubation by the injection of 100 microliters of aqueous solution into the air space of each egg. Eggs were incubated with mechanical rotation until hatch, at which time mortality was assessed. Probit transformation of the mortality data produced a linear line of best fit (P < 0.05), from which an LD50 of 52 micrograms FB1/egg, equivalent to a concentration of 1.3 microns hatched in artificial seawater and exposed to FB1 in an optimized 96-well plate assay with a 48 hr mortality endpoint. Probit transformation of the mortality data resulted in an LC50 of 1.7 microns FB1, or 1.2 micrograms FB1/ml. Thus, at the cellular level, both bioassays appeared sensitive to FB1; however, from the standpoint of use as a screening assay, the chicken embryo bioassay is limited by the relatively high dose of FB1 required per egg. It is anticipated that the design and simplicity of the brine shrimp bioassay will accommodate screening for FB1 toxicity in contaminated samples.

Reduction of risks associated with fumonisin contamination in corn

Fumonisins, produced by Fusarium moniliforme, have been recognized as an important group of chemicals which cause health risks in domestic animals and humans. Decontamination procedures for fumonisin B1 (FB1) were evaluated to determine chemical modification and reduction in toxic/carcinogenic potentials. Ammoniation, a procedure used for decontamination of aflatoxins, yielded a 79% reduction in FB1 levels in naturally contaminated corn. Authentic FB1 and FB1-contaminated corn were exposed to alternative treatments containing various combinations of Ca(OH)2, NaHCO3, and H2O2 simulating a modified nixtamalization procedure. Treatments also included NH4Cl alone or in combination with H2O2 or horseradish peroxidase. The brine shrimp assay (Artemia spp.) was used to monitor toxicity of reaction products and the Salmonella/microsomal mutagenicity assay, using tester strains TA-100 and TA-102, was used to evaluate mutagenicity. Treatments of FB1-contaminated corn simulating modified nixtamalization (Ca(OH)2 alone or with Na-HCO3 + H2O2) gave 100% reduction of FB1 and reduced brine shrimp toxicity by ca. 40%. The positive mutagenic potential (without S-9) for extracts of corn naturally contaminated with FB1 was eliminated following exposure to modified nixtamalization. Reaction products formed when pure FB1 was treated with Ca(OH)2 and H2O2/NaHCO3 were inhibitory to Bacillus cereus, B. subtilis, and B. megaterium. No inhibitory potential was evident for contaminated corn extracts following the chemical treatments.