Biological toxicity risk assessment of two potential neutral carbon diesel fuel substitutes.

We investigated the biological response of soluble organic fraction (SOF) and water-soluble fraction (WSF) extracted from particulate matter (PM) emitted by an automotive diesel engine operating in a representative urban driving condition. The engine was fueled with ultra-low sulfur diesel (ULSD), and its binary blends by volume with 13% of butanol (Bu13), and with hydrotreated vegetable oil (HVO) at 13% (HVO13) and 20% (HVO20). Cytotoxicity, genotoxicity, oxidative DNA damage and ecotoxicity tests were carried out, and 16 polycyclic aromatic hydrocarbons (PAH) expressed as tbenzo(a)pyrene total toxicity equivalent (BaP-TEQ) were also analyzed. The Hepatocarcinoma epithelial cell line (HepG2) was exposed to SOF for 24 h and analyzed using comet assay, with the inclusion of formamidopyrimidine DNA glycosylase (FPG) and endonuclease III (Endo III) to recognize oxidized DNA bases. The WSF was evaluated through acute ecotoxicity tests with the aquatic microcrustacean Daphnia pulex (D. Pulex). Results showed that there was no cytotoxic activity for all tested SOF concentrations. Genotoxic responses by all the SOF samples were at same level, except for the HVO13 which was weaker in the absence of the enzymes. The addition of the FPG and Endo III enzymes resulted in a significant increase in the comet tail, indicating that the DNA damage from SOF for all tested fuel blends involves oxidative damage including a higher level of oxidized purines for ULSD and Bu13 in comparison with HVO blends, but the oxidized pyrimidines for HVO blends were slightly higher compared to Bu13. The WSF did not show acute ecotoxicity for any of the fuels. Unlike other samples, Bu13-derived particles significantly increase the BaP-TEQ. The contribution to the genotoxic activity and oxidative DNA from SOF was not correlated to BaP-TEQ, which means that the biological activity of PM might be affected also by other toxic compounds present in particulate phase.

In vitro evaluation of the cytotoxicity, mutagenicity and DNA damage induced by particle matter and gaseous emissions from a medium-duty diesel vehicle under real driving conditions using palm oil biodiesel blends.

The influence of palm oil biodiesel content on the cytotoxicity, mutagenicity and genotoxicity of particle- and gas-phase diesel vehicle emissions was investigated. The emissions were collected on-board of a EURO IV diesel truck, fuelled with mixtures of 10% (B10), 20% (B20) and 100% (B100) of palm oil biodiesel, under real driving conditions. Organic extracts of the particulate matter (PM) and gases were characterised for 17 PAH (including EPA priority) and used for the biological assay. Increasing biodiesel content in the fuel mixture results in a decrease in the PM and PAH emission factors, both in the particulate and gas-phase. The majority of the PAH are present in the gas-phase. The mutagenic potencies, in TA98 bacteria, are higher for B20 in both phases, whereas the mutagenicity emission factor, that takes into account the lower emission of PM and PAH, is not significantly different between the fuels. Higher direct mutagenicity (TA98 + S9) is observed in all the tested fuels, indicating the action of carcinogenic compounds other than non-substituted PAH. The gas-phase extracts present higher cytotoxicity and genotoxicity in lung epithelial cell A549, which may be related to the higher PAH content in the gas-phase. The increase in biodiesel content have a different impact on cytotoxicity, being larger in the gas-phase and lower in the particle-phase. This indicates that pulmonary toxicity may be higher for the gaseous emissions, due to the role of different toxic compounds compared to the PM. The adverse biological effects when biodiesel content increases are not consequent with the reduction of the PAH characterised, indicating that other toxic compounds are more relevant. Further investigations to identify these compounds are required in order to update and focus the efforts regarding emission targets and controls.

[Evaluation of the genotoxic effect of malaria in a cohort of patients in Medellín and Quibdó]. / Evaluación del efecto genotóxico en pacientes con malaria de una región de Colombia.

INTRODUCTION: During malaria infection, both parasite and host are under the effects of oxidative stress due to the increased production of reactive oxygen species, which can induce DNA damage by its genotoxic effects. OBJECTIVE: To evaluate genotoxic effects in human lymphocytes in a cohort of patients with malaria from Medellin and Quibdó. METHODS: We performed an observational cross sectional study in 100 individuals with malaria and 100 healthy controls. Patients infected with Plasmodium consulting the Institute Colombiano of Medicina Tropical of Medellin and the Hospital Ismael Roldán Valencia of Quibdó were included. Genotoxic effects (genetic damage) was analysed by electrophoresis using alkaline single cell gel (Commet assay). RESULTS: The average of tail length of malaria samples (26.9±9.8) was significantly higher than of controls (14.8±3.2) (p<0.01). CONCLUSION: In our study population, malaria infection was associated with increased genotoxicity, while other variables such as smoking, antimalarial treatment, and occupation were not.

Evaluación del efecto genotóxico en pacientes con malaria de una región de Colombia / Evaluation of the genotoxic effect of malaria in a cohort of patients in Medellín and Quibdó

Introduction: During malaria infection, both parasite and host are under the effects of oxidative stress due to the increased production of reactive oxygen species, which can induce DNA damage by its genotoxic effects. Objective: To evaluate genotoxic effects in human lymphocytes in a cohort of patients with malaria from Medellin and Quibdó. Methods: We performed an observational cross sectional study in 100 individuals with malaria and 100 healthy controls. Patients infected with Plasmodium consulting the Institute Colombiano of Medicina Tropical of Medellin and the Hospital Ismael Roldán Valencia of Quibdó were included. Genotoxic effects (genetic damage) was analysed by electrophoresis using alkaline single cell gel (Commet assay). Results: The average of tail length of malaria samples (26.9 ± 9.8) was significantly higher than of controls (14.8 ± 3.2) (p < 0.01). Conclusion: In our study population, malaria infection was associated with increased genotoxicity, while other variables such as smoking, antimalarial treatment, and occupation were not.

Introducción: Durante la infección de la malaria, tanto el parásito como el hospedero están bajo los efectos de estrés oxidativo, dado que se aumenta la producción de especies reactivas del oxígeno, las cuales pueden inducir daños en el ADN debido a su gran efecto genotóxico. Objetivo: Evaluar el efecto genotóxico en linfocitos humanos en una cohorte de pacientes con malaria de Medellín y Quibdó. Métodos: Se realizó un estudio observacional transversal en 100 personas con malaria y 100 controles sanos. Se incluyeron pacientes infectados con Plasmodium, que consultaron en el Instituto Colombiano de Medicina Tropical de Medellín y el Hospital Ismael Roldán Valencia de Quibdó. Se realizó una valoración transversal del efecto (daño genético) mediante electro-foresis en gel de células individuales (ensayo Cometa). Resultados: El promedio de longitud de la cola de los pacientes (26,9 ± 9,8) fue significativamente mayor que la media de los controles sanos (14,8 ± 3,2) (p < 0,01). Conclusión: Se evidenció en la población de estudio que la infección por malaria generó genotoxicidad, no así variables como tabaquismo, tratamiento antimalárico y ocupación.

Interacciones genotóxicas de mutágenos en mezclas binarias mediante ensayo cometa alcalino en linfocitos humanos / Interaction of mutagens in binary mixtures using the alkaline comet assay in human lymphocytes

Introducción. Los mutágenos contenidos en mezclas complejas presentan interacciones de sinergismo, aditivas o antagónicas. Se han desarrollado enfoques experimentales que permitan dilucidar el responsable de las interacciones en la mezcla. Objetivo. Desarrollar un diseño experimental para comprender los procesos que se llevan a cabo entre los compuestos presentes en las mezclas complejas. Materiales y métodos. Se expusieron linfocitos humanos a mezclas binarias de mutágenos B[a]P, DMBA, Trp-P-1 y MX durante una hora, con activación metabólica y sin ella. La viabilidad se evaluó con azul de tripano y, la genotoxicidad, con cometa alcalino. Resultados. Ningún hidrocarburo tuvo efecto con furanona. Con S9 y sin él, se observó que se presentaban interacciones tóxicas entre hidrocarburos. Se observó sinergismo sin S9 entre B[a]P y Trp-P-1 y, con actividad metabólica, entre DMBA y Trp-P-1. Sin S9 se observó interacción antagónica entre Trp-P-1 y DMBA y, con S9, entre Trp-P-1 y MX y entre MX y DMBA. Se observó un incremento dependiente de la dosis en la longitud de la cola. Hubo daño genotóxico medio y aumento de las células dañadas. Para todas las mezclas se pudo determinar la concentración mínima en la que se observaban efectos adversos y solo para algunas se determinó la concentración máxima en la cual no se observaron efectos adversos. Conclusión. Se hace un aporte para comprender los procesos que ocurren cuando en una mezcla hay presentes, al menos, dos mutágenos y se valida un modelo de análisis que permite dilucidar el compuesto que tiene efecto sobre otro. También, se demostró que según el tipo de compuestos en la mezcla, se tendrá o no un umbral de riesgo.

Introduction. Mutagens contained in complex mixtures can present synergistic interactions, either additive or antagonistic. Therefore, development of experimental approaches is necessary to elucidate which is the responsible agent for the effect in the mixtures. Objective. An experimental design was developed that allowed an understanding of the processes between the compounds of complex mixtures. Materials and methods. Human lymphocytes were exposed to binary mixtures of the mutagens B[a]P, DMBA, Trp-P-1 and MX for 1 hour with or without S9. Viability was assessed with trypan blue dye and the genotoxicity by the comet assay. Results. All of the hydrocarbon showed an effect with furanone. With and without S9, the most toxic interactions were observed between hydrocarbons. Synergistic interaction was observed without S9 between B [a] P and Trp-P-1 and between DMBA and Trp-P-1 with metabolic activity. Without S9 antagonistic interaction was observed only between Trp-P-1+DMBA, and with S9 between Trp-P-1+MX and MX+DMBA. It observed an increase dose dependent in tail length. Half the cultures showed genotoxic damage and increased cell damage. For each mixture, minimum concentrations were determined at which adverse effects are observed; for some only the maximum concentration was determined at which no adverse effects are observed. Conclusion. The processes between mutagens present in a mixture have become better understood, and the results validated an analytical model that determined which component had an effect on another. The results also showed that the type of compounds in the mixture determined whether or not a risk threshold was present.

[Interaction of mutagens in binary mixtures using the alkaline comet assay in human lymphocytes]. / Interacciones genotóxicas de mutágenos en mezclas binarias mediante ensayo cometa alcalino en linfocitos humanos.

INTRODUCTION: Mutagens contained in complex mixtures can present synergistic interactions, either additive or antagonistic. Therefore, development of experimental approaches is necessary to elucidate which is the responsible agent for the effect in the mixtures. OBJECTIVE: An experimental design was developed that allowed an understanding of the processes between the compounds of complex mixtures. MATERIALS AND METHODS: Human lymphocytes were exposed to binary mixtures of the mutagens B[a]P, DMBA, Trp-P-1 and MX for 1 hour with or without S9. Viability was assessed with trypan blue dye and the genotoxicity by the comet assay. RESULTS: All of the hydrocarbon showed an effect with furanone. With and without S9, the most toxic interactions were observed between hydrocarbons. Synergistic interaction was observed without S9 between B [a] P and Trp-P-1 and between DMBA and Trp-P-1 with metabolic activity. Without S9 antagonistic interaction was observed only between Trp-P-1+DMBA, and with S9 between Trp-P-1+MX and MX+DMBA. It observed an increase dose dependent in tail length. Half the cultures showed genotoxic damage and increased cell damage. For each mixture, minimum concentrations were determined at which adverse effects are observed; for some only the maximum concentration was determined at which no adverse effects are observed. CONCLUSION: The processes between mutagens present in a mixture have become better understood, and the results validated an analytical model that determined which component had an effect on another. The results also showed that the type of compounds in the mixture determined whether or not a risk threshold was present.