Synthesis of [2H3]-labelled sulfamethoxazole and its main urinary metabolites

A new [2H]-labelled α-trichloroimidate glucuronic ester for the synthesis of deuterated drug conjugates

A new reaction pathway for the synthesis of a [(2)H]-labelled trichloroacetimidate precursor for the preparation of glucuronides is described. Therewith, stable isotope-labelled drug glucuronides become accessible on a preparative scale, which can further be used as internal standards for quantitative analysis.

Effects of pH and manure on transport of sulfonamide antibiotics in soil

Sulfonamide antibiotics are a commonly used group of compounds in animal husbandry. They are excreted with manure, which is collected in a storage lagoon in certain types of confined animal feeding operations. Flood irrigation of forage fields with this liquid manure creates the potential risk of groundwater contamination in areas with shallow groundwater levels. We tested the hypothesis that-in addition to the soil characteristics-manure as cosolute and manure pH are two major parameters influencing sulfonamide transport in soils. Solute displacement experiments in repacked, saturated soil columns were performed with soil (loamy sand) and manure from a dairy farm in California. Breakthrough of nonreactive tracer and sulfadimethoxine, sulfamethazine, and sulfamethoxazole at different solution pH (5, 6.5, 8.5) with and without manure was modeled using Hydrus-1D to infer transport and reaction parameters. Tracer and sulfonamide breakthrough curves were well explained by a model concept based on physical nonequilibrium transport, equilibrium sorption, and first-order dissipation kinetics. Sorption of the antibiotics was low ( K₄ ≤ 0.7 L kg) and only weakly influenced by pH and manure. However, sulfonamide attenuation was significantly affected by both pH and manure. The mass recovery of sulfonamides decreased with decreasing pH, e.g., for sulfamethoxazole from 77 (pH 8.5) to 56% (pH 5). The sulfonamides were highly mobile under the studied conditions, but manure application increased their attenuation substantially. The observed attenuation was most likely caused by a combination of microbial transformation and irreversible sorption to the soil matrix.

Fate of the antibiotic sulfamethoxazole and its two major human metabolites in a water sediment test

Sulfonamide antibiotics are widely used in human and veterinary medicine. After their application, they are excreted in unchanged as well as in metabolized form. Due to incomplete elimination in wastewater treatment plants, they can be emitted into surface water. The environmental fate of both parent compounds and metabolites is currently unknown. The aim of this study was to determine the biodegradation potential of river sediment for the sulfonamide sulfamethoxazole (SMX) and its two major human metabolites N4-acetyl-SMX and SMX-N1-glucuronide using a water sediment test system. Each compound was tested in a separate series together with sterile and "water only" controls. All three compounds were efficiently removed from the test system by biodegradation in the sediment. Only for SMX-N1-glucuronide, a substantial removal in the absence of sediment was determined. Dissipation times from the aqueous phase (DT50) between 8.5 and 17.2 days were measured. Sorption to sediment was of minor importance due to the slightly basic pH of the test system. By the application of a mathematical model, biodegradation half-lives in sediment between 3.3 and 25.6 h were calculated for SMX and its metabolites. The results of this study highlight the capability of native river sediment for degrading sulfonamide antibiotics, but also the potential of human metabolites to retransform into parent SMX under environmental conditions. Based on this study, it is unlikely that SMX or its metabolites will persist or accumulate in river sediments under pH conditions where sorption is of minor importance.