Kinetic Passive Sampling: In Situ Calibration Using the Contaminant Mass Measured in Parallel Samplers with Different Thicknesses.

The use of single-phase passive samplers is a common method for sampling bioavailable concentrations of hydrophobic aquatic pollutants. Often such samplers are used in the kinetic stage, and in situ calibration is necessary. Most commonly, exchange kinetics are derived from the release rates of performance reference compounds (PRCs). In this study, a complementary calibration approach was developed, in which measuring the contaminant mass ratio (CMR) from two samplers with different thicknesses allows the dissolved concentrations to be determined. This new CMR calibration was tested (1) in a laboratory experiment with defined and constant concentrations and (2) in the field, at a storm water retention site. Silicone passive samplers with different thicknesses were used to sample a range of dissolved polycyclic aromatic hydrocarbons. In the laboratory study, the concentrations derived from the CMR calibration were compared with those from water extraction and passive dosing and differences below a factor 2 were found. In the field study, CMR-derived concentrations were compared to those from PRC calibration. Here, differences ranged by only a factor 1 to 3 between both methods. These findings indicate that the CMR calibration can be applied as a stand-alone or complementary calibration method for kinetic passive sampling.

Simultaneous exposure to low concentrations of dichlorodiphenyltrichloroethane, deltamethrin, nonylphenol and phytoestrogens has negative effects on the reproductive parameters in male Spraque-Dawley rats.

Many reports suggest that male reproductive health has deteriorated over the last decades, possibly due to environmental contaminants that act as endocrine disruptors. This hypothesis was tested in Sprague-Dawley rats using a modified Organization for Economic Cooperation and Development 415 one-generation test. Group A received cottonseed oil as control, and Groups B, C and D received deltamethrin (DM); DM and dichlorodiphenyltrichloroethane (DDT); and DM, DDT, phytoestrogens and p-nonylphenol, respectively. Rats were exposed in utero and then received the substances for 10 weeks. The seminal vesicle mass (Group B; P = 0.046) and sperm count [Groups C (P = 0.013) and D (P = 0.003)] were lower and the anogenital distance [Group B (P = 0.047) C (P = 0.045) and D (P = 0.002)] shorter compared with the control group. The seminiferous tubule diameter [Groups B (P = <0.001), C (P = <0.001) and D (P = <0.001)] and epithelium thickness [Groups B (P = 0.030), C (P = <0.001) and D (P = <0.001)] were smaller compared with the control. The histology of the testes showed signs of apical sloughing and vacuolisation. Liver weights [Groups C (P = 0.013) and D (P = 0.005)] and liver enzymes [Group D (P = 0.013)] were also affected. These findings may indicate that simultaneous exposure to endocrine disrupting compounds contributes to the deterioration observed in male reproductive health.

Evaluation in the baboon model of (99m)Tc-biguanide as a tracer for renal imaging.

Studies in various animal species have recently shown that (99m)Tc-BIG has practical and dosimetric benefits for renal imaging that could probably make it a good alternative to (99m)Tc-2, 3-dimercaptosuccinic acid ((99m)Tc-DMSA). In this study, using the baboon experimental model, the biodistribution of (99m)Tc-BIG and (99m)Tc-DMSA are compared. It is demonstrated that early good contrast imaging and more favourable dosimetry is possible with (99m)Tc-BIG compared to (99m)Tc-DMSA, confirming the quoted previous findings with small animals. Time-activity curves for kidneys and other organs support these findings, and MIRDOSE software provided the dosimetry.