ABSTRACT
Antimicrobial resistance (AMR) is a threat to public and animal health on the global scale. The origin of the genes associated with resistance has long been unknown. Recently, there is a growing body of evidence demonstrating that environmental bacteria are resistant to a multitude of antibiotic substances and that this environmental reservoir of AMR is still growing. The analysis of the genomes of bacterial pathogens indicates that they have acquired their resistance profiles by incorporating different genetic elements through horizontal gene transfer. The ancestors of pathogenic bacteria, as well as the origin of resistance determinants, lay most likely in the environmental microbiota. Indeed, there is some evidence that at least some clinically relevant resistance genes have originated in environmental bacterial species. Thus, feasible measures are required to reduce the risks posed by AMR genes and resistant bacteria that occur in the environment. It has been shown that a concurrence of factors, such as high concentrations of antibiotics or heavy metals used as biocides and high bacterial densities, promote development and spread of antimicrobial resistance. For this purpose, it is essential to restrict the use of antibiotics for the treatment of livestock and humans to medical necessity, as well as to reduce the application of biocides and heavy metals in animal husbandry. Moreover, it is important to further develop sanitary measures at the interface between the environment and clinical settings or livestock farming.
Subject(s)
Drug Resistance, Microbial/genetics , Gene Transfer, Horizontal/genetics , Public Health/trends , Animal Husbandry/trends , Animals , Anti-Bacterial Agents/therapeutic use , Antimicrobial Stewardship , Disinfectants/adverse effects , Drug Resistance, Microbial/drug effects , Forecasting , Gene Transfer, Horizontal/drug effects , Germany , Humans , Metals, Heavy/adverse effectsABSTRACT
The Fish Sexual Development Test (FSDT) is a non-reproductive test to assess adverse effects of endocrine disrupting chemicals. With the present study it was intended to evaluate whether gene expression endpoints would serve as predictive markers of endocrine disruption in a FSDT. For proof-of-concept, a FSDT according to the OECD TG 234 was conducted with the non-steroidal aromatase inhibitor fadrozole (test concentrations: 10µg/L, 32µg/L, 100µg/L) using zebrafish (Danio rerio). Gene expression analyses using quantitative RT-PCR were included at 48h, 96h, 28days and 63days post fertilization (hpf, dpf). The selection of genes aimed at finding molecular endpoints which could be directly linked to the adverse apical effects of aromatase inhibition. The most prominent effects of fadrozole exposure on the sexual development of zebrafish were a complete sex ratio shift towards males and an acceleration of gonad maturation already at low fadrozole concentrations (10µg/L). Due to the specific inhibition of the aromatase enzyme (Cyp19) by fadrozole and thus, the conversion of C19-androgens to C18-estrogens, the steroid hormone balance controlling the sex ratio of zebrafish was altered. The resulting key event is the regulation of directly estrogen-responsive genes. Subsequently, gene expression of vitellogenin 1 (vtg1) and of the aromatase cyp19a1b isoform (cyp19a1b), were down-regulated upon fadrozole treatment compared to controls. For example, mRNA levels of vtg1 were down-regulated compared to the controls as early as 48 hpf and 96 hpf. Further regulated genes cumulated in pathways suggested to be controlled by endocrine mechanisms, like the steroid and terpenoid synthesis pathway (e.g. mevalonate (diphospho) decarboxylase (mvd), lanosterol synthase (2,3-oxidosqualene-lanosterol cyclase; lss), methylsterol monooxygenase 1 (sc4mol)) and in lipid transport/metabolic processes (steroidogenic acute regulatory protein (star), apolipoprotein Eb (apoEb)). Taken together, this study demonstrated that the existing Adverse Outcome Pathway (AOP) for aromatase inhibition in fish can be translated to the life-stage of sexual differentiation. We were further able to identify MoA-specific marker gene expression which can be instrumental in defining new measurable key events (KE) of existing or new AOPs related to endocrine disruption.
