Assessing the mobility of veterinary drugs with column experiments using different soils and under controlled flow conditions.

Veterinary pharmaceuticals are pollutants that received much attention during the last 20 years. Macrocyclic lactones are a class of drugs globally used in animal and human health, as well as crops protection. Some of its members are key substances for global food security. In this research, the mobility of eprinomectin (EPM) in soil columns (25 cm soil height; 10 cm diameter) was assessed for the first time. Soil density in the columns was 1.1-1.2 g/cm3. Porosity was 0.54-0.60. Three different soil types were used (agricultural, pastoral, wetland). In the experiment, chloride was used as a non-reactive tracer to determine the hydrodynamic conditions in the columns. Therefore, water velocity (v) was 0.146-0.151 cm/h, dispersion coefficient (D) 0.011-0.017 cm2/h and dispersivity (D/v) was 0.072-0.121. Our results showed that the drug remained in the top layers of the columns, after applying an extreme irrigation scenario. The retardation factor for EPM was 43.4-54.5 while for chloride was 0.99-1. EPM fraction (% of applied mass) in 0-1 cm was 13.8-18.0% and in 1-5 cm was 53.3-73.0%. An amount 13-29% was irreversibly bound or degraded during this experiment. From a soil management perspective, the continuous application of EPM contaminated manure, could result in high concentrations in the top 10 cm of the soil profile. Soil column experiments, where hydrodynamic conditions are well defined, are useful for the environmental impact assessment of veterinary pharmaceuticals.

Effects of the Antibiotic Amoxicillin on Key Species of the Terrestrial Environment.

The antibiotic amoxicillin (AMX) is globally important for human and animal health. Although AMX is considered as a threat for the aquatic and terrestrial environment, limited data are present for its toxicity against key species such as denitrifying bacteria in soil, earthworms and plants. In the present research, the OECD protocols for environmental risk assessment were applied to study AMX acute toxicity, at nominal concentrations, close to the environmentally relevant, in soil bacteria responsible for nitrogen cycling, in the earthworm species Eisenia fetida and six plant species. The results revealed no significant effects of the antibiotic on the parameters related to the end-points of each respective test, at the selected concentration range. Therefore, the antibiotic did not present acute toxicity for the species, under the framework of the OECD tests. Further research is essential to be conducted also considering the patterns of degradation of AMX during the experimental periods.

Are the parasiticidal avermectins resistant to dissipation in the environment? The case of eprinomectin.

Eprinomectin (EPM) is a veterinary drug currently licensed in many countries for the treatment of endo- and ecto-parasites in cattle. Despite the notable evidence for its high toxicity to the terrestrial and aquatic environment ecosystems, its environmental behavior and fate are currently unknown. In the present research, the dissipation of EPM was studied in three soils and in cattle manure by using the OECD 307 guideline and the recently developed European Medicines Agency (EMA/CVMP/ERA/430327) guideline, respectively. The procedure presented by the FOrum for Co-ordination of pesticide models and their USe (FOCUS) was adopted for estimating the EPM degradation kinetics in soil and cattle manure. The EPM dissipation in soil was best described by the SFO (Simple First Order) and the HS (Hockey Stick) models, under aerobic and anaerobic conditions, respectively. The EPM dissipation in cattle manure was best described by the FOMC (First Order Multi Compartment) model. The Dissipation Time for the 50% of the initial EPM mass (DT50) range was 38-53days under aerobic and 691-1491days under anaerobic conditions. In addition, the DT50 for EPM in cattle manure was 333days. Therefore, EPM could be characterized as moderately to highly persistent to dissipation in soil, which depends on soil type, its oxygen content (aerobic or anaerobic conditions in soil) and the microbial activity. Moreover, the EPM resists dissipation in cattle manure, resulting to a high load in soil after manure application in agricultural land (or direct defecation in grassland). Consequently, the high possibility for EPM accumulation in soil and cattle manure should be considered when assessing the environmental risk of the drug.

Occurrence of priority organic pollutants in Strymon river catchment, Greece: inland, transitional, and coastal waters.

Twenty-five sampling stations were selected in order to monitor persistent organic pollutants (polycyclic aromatic hydrocarbons (PAHs), organochlorine (OC) pesticides and total polychlorinated biphenyls (PCBs)) in surface water from Kerkini Lake, the Strymon River, its main tributaries and estuary in N. Aegean Sea during January to July, 2008, according to recent European Union (EU) guidelines. The data were divided among the high (January to April) and the low flow season (May to July). Generally, the values for organic pollutants were within the range reported worldwide for surface water. Elevated PAHs concentrations were observed compared with other places in Greece. Anthracene and benzo(a)pyrene exceeded maximum allowable concentration (MAC) of the relative EU guideline. Also, concentrations above MAC were observed for OCs, γ-HCH, and a-endosulfan. Despite the fact that it is banned since 1972, Aldrin was detected during the monitoring season (from limit of detection (LOD) to 15 ng L(-1)). Total PCB concentrations ranged from LOD to 162 ng L(-1). In addition, the load of organic pollutants was estimated in April (high flow) and June (low flow) in selected sampling stations. According to this estimation, napthalene, anthracene, and fluoranthene (PAHs), total dichlorodiphenyltrichloroethane (DDT), aldrin, and total PCBs had the highest load. Taking into account the relative EU guidelines concerning the pollutants studied, the water quality in the Strymon River catchment could be characterized as poor, which can lead to negative impacts to its biota.

Sorption of the antiparasitic drug eprinomectin in three soils.

Batch equilibrium studies were conducted to determine eprinomectin partitioning behavior in three Greek soils (agricultural, pastoral and riparian soil). An analytical method was developed to quantify eprinomectin in aqueous 0.01 M CaCl2. Recovery was 95% and limits of detection and quantification were both 0.005 mgL⁻¹. An existing method for its quantification in soil was successfully tested in this study. Mass balance determinations showed that we accounted for 89-98% of the eprinomectin spiked in 5 g soil/25 mL 0.01 M CaCl2. The concentration specific adsorption distribution coefficient (K(d)(ads)) ranged from 6.4 to 21.4 L kg⁻¹ while concentration specific desorption distribution coefficient (K(d)(des)) ranged from 23.2 to 124.6 L kg⁻¹. The Freundlich model adequately described adsorption and desorption with n values from 0.6 to 1.07. Hysteresis between adsorption and desorption was observed in two (agricultural and pastoral) soils. Moreover, eprinomectin binding to the clay mineral vermiculite and natural peat was tested. The drug binds to both materials. Hydroxyl groups and the nitrogen group present in eprinomectin are probably responsible for the binding to vermiculite. Coefficient K(d)(ads) significantly correlated with cation exchange capacity (CEC), Fe and Cu content of the soils when data for eprinomectin and data for ivermectin and abamectin were combined. These could be evidence that eprinomectin fate is related not only to organic matter (lipophilic binding) but also to clay content and other charged inorganic groups typically present in the soil environment.

Analytical procedure for the determination of eprinomectin in soil and cattle faeces.

A new analytical HPLC-fluorescence method was developed for the quantitative determination of eprinomectin (EPM) in soil and cattle faeces. EPM was extracted with acetone and acetonitrile from soil and cattle faeces, respectively. Solid phase extraction and derivatization reaction with N-methylimidazole in the presence of trifluoroacetic anhydride and acetic acid were applied. The limit of quantitation was 1 ng g(-1) air dried soil and 2.5 ng g(-1) moist cattle faeces. Overall recovery (RSD) was 89% (8) in soil and 85% (10) in cattle faeces and its good reproducibility (RSD<15%) allows the application of the method in advanced ecotoxicological studies, required for the environmental fate assessment of EPM.