Surface water pollution by herbicides from effluents of waste water treatment plants.

Herbicide loads of urban and rural waste water treatment plant effluents were calculated over a one-year period by measuring the herbicide concentrations in 14-day mixed samples. More than three quarters of the total herbicide load of the effluent of the rural waste water treatment plant consists of isoproturon. Particularly large amounts of this substance contribute to the total herbicide load during the main application in spring and in early autumn. The measured loads of atrazine and the increased ratio between atrazine and desethylatrazine in spring indicate that atrazine is still applied in Germany. More than 80% of the total herbicide load of the effluent of the urban waste water treatment plant consists of diuron which is mainly used in urban weed control. The results show that also effluents of urban waste water treatment plants contribute to a great extent to herbicide pollution of surface water.

Nitrophenols in precipitation.

From 1995 to 1998 the concentrations of 4-nitrophenol, 2-methyl-4-nitrophenol, 3-methyl-4-nitrophenol, dinitro-ortho-cresol (DNOC) and 2,4-di-nitrophenol were measured monthly by HPLC in precipitation at eight different locations in Bavaria (Germany). Samples were collected by purpose-constructed computerised rainwater samplers which record electronically various sensor data each hour and adjust the sample temperature to 4 degrees C. The highest nitrophenol (NP) concentrations were measured for 4-NP. The median at all locations is higher than 1 microg/l. The median of the other NPs ranges between 0.2 and 0.8 microg/l. Considering the rain amounts the highest depositions were calculated for the regions Spessart, Bayerischer Wald and Chiemgauer Alpen. The median of 4-NP depositions extents to 200 microg/(month m2). The highest medians of the other NP depositions reach approximately 50 microg/(month m2).

Biodegradation in laboratory activated sludge plants and aquatic toxicity of herbicides.

The biodegradation and the aquatic toxicity of four herbicides (isoproturon, terbuthylazine, mecoprop, metamitron) were investigated. Laboratory activated sludge plants were used for biodegradation experiments. The biodegradation of mecoprop reached nearly 100%, the other herbicides were not eliminated by biodegradation. The acute Daphnia magna 24-h assay, the algal 72-h inhibition test, and the recently developed lemna growth inhibition 7-d test were applied to evaluate the biological effects of herbicides as original substances. EC 50 and EC 10 values were determined. Algal and lemna test show that isoproturon and terbuthylazine are both much more toxic than mecoprop and metamitron. Daphnids are generally less sensitive against herbicides than plants. Biodegradation and toxicity test were coupled for mecoprop to assess biological long-term effects of possible biodegradation products of this herbicide. The effluents of the laboratory activated sludge units were used in toxicity tests (Daphnia magna 21-d reproduction test, lemna growth inhibition 7-d test). No inhibiting effect on the tested organisms was observed.

Geochemical evaluation of different groundwater-host rock systems for radioactive waste disposal.

The geochemical suitability of a deep bedrock repository for radioactive waste disposal is determined by the composition of geomatrix and groundwater. Both influence radionuclide solubility, chemical buffer capacity and radionuclide retention. They also determine the chemical compatibility of waste forms, containers and backfill materials. Evaluation of different groundwater-host rock systems is performed by modeling the geochemical environments and the resulting radionuclide concentrations. In order to demonstrate the evaluation method, model calculations are applied to data sets available for various geological formations such as granite, clay and rocksalt. The saturation state of the groundwater-geomatrix system is found to be fundamental for the evaluation process. Hence, calculations are performed to determine if groundwater is in equilibrium with mineral phases of the geological formation. In addition, corrosion of waste forms in different groundwater is examined by means of reaction path modeling. The corrosion reactions change the solution compositions and pH, resulting in significant changes of radionuclide solubilities. The results demonstrate that geochemical modeling of saturation state and compatibility of the host formation environment with the radioactive waste proves to be a feasible tool for evaluation of various sites considered as deep underground repositories.

Numerical modeling of humic colloid borne americium (III) migration in column experiments using the transport/speciation code K1D and the KICAM model.

The humic colloid borne Am(III) transport was investigated in column experiments for Gorleben groundwater/sand systems. It was found that the interaction of Am with humic colloids is kinetically controlled, which strongly influences the migration behavior of Am(III). These kinetic effects have to be taken into account for transport/speciation modeling. The kinetically controlled availability model (KICAM) was developed to describe actinide sorption and transport in laboratory batch and column experiments. Application of the KICAM requires a chemical transport/speciation code, which simultaneously models both kinetically controlled processes and equilibrium reactions. Therefore, the code K1D was developed as a flexible research code that allows the inclusion of kinetic data in addition to transport features and chemical equilibrium. This paper presents the verification of K1D and its application to model column experiments investigating unimpeded humic colloid borne Am migration. Parmeters for reactive transport simulations were determined for a Gorleben groundwater system of high humic colloid concentration (GoHy 2227). A single set of parameters was used to model a series of column experiments. Model results correspond well to experimental data for the unretarded humic borne Am breakthrough.

Selective trace analysis of diclofenac in surface and wastewater samples using solid-phase extraction with a new molecularly imprinted polymer.

A new molecularly imprinted polymer (MIP) for trace analysis of diclofenac in environmental water samples was prepared by a non-covalent protocol in which diclofenac was used as a template molecule. Diclofenac is a member of the class of drugs termed non-steroidal anti-inflammatory drugs (NSAIDs) which belong to the most frequently detected pharmaceuticals in the water-cycle in Europe. The MIP was synthesized using 2-vinylpyridine (2-VP) and ethylene glycol dimethacrylate (EGDMA) as a functional monomer and cross-linker, respectively, and bulk thermal polymerization method. (1)H NMR spectroscopy was used to study the interaction between diclofenac and 2-VP mixed in toluene-d(8) in pre-polymerization complex. Two non-covalent bonds were formed i.e. ionic interaction and hydrogen bonding. The binding characteristics of the MIP and diclofenac were evaluated using equilibrium binding experiments. Scatchard plot analysis revealed that two classes of binding sites were formed with dissociation constants of 55.6 micromol L(-1) and 1.43 mmol L(-1), respectively. Various parameters affecting the extraction efficiency of the polymers have been evaluated to achieve the selective preconcentration of diclofenac from aqueous samples and to reduce non-specific interactions. This resulted in an MISPE-LC/DAD method allowing the direct extraction of the analyte from sample matrix with a selective wash using dichloromethane/acetonitrile (94:6, v/v) followed by elution with dichloromethane/methanol (85:15, v/v). The recovery of a 100 ng diclofenac standard spiked into 200 mL of blank surface water was 96%, with good precision (RSD=3.3%, n=3). The MISPE was demonstrated to be applicable to the analysis of diclofenac in raw influent and final effluent wastewater samples from sewage treatment plant and revealed diclofenac concentrations of 1.31+/-0.055 microg L(-1) (n=3) and 1.60+/-0.049 microg L(-1) (n=3), respectively. Yielded results were in good agreement with the corresponding LC/TIS/MS/MS data obtained by an independent laboratory which were 1.40 and 1.50 microg L(-1) for influent and effluent samples.

Stomatocytosis of latex particles (0.26 micron) by rat erythrocytes by the electrical breakdown technique.

The uptake of macromolecules by erythrocytes can be achieved with the electrical breakdown technique [2, 4]. In this technique the erythrocyte membranes are subjected to a high external electrical field pulse for a short period. Local, reversible breakdowns of the cell membrane occur above a critical field strength which lead to a time-dependent increase in the permeability of the membrane. By this means, human erythrocyte membranes can be made permeable to DNA, pharmaceutical compounds, and latex particles following an electrical field pulse [1, 3, 5]. Larger particles should also be taken up by erythrocytes using this method. Vienken et al. [5] demonstrated the entrapment of latex particles with a diameter of 0.091 micron in human erythrocyte ghosts, although this was shown with only a single electron micrograph which does not prove that the ghost membrane was intact. In our experiments in order to entrap latex particles with a diameter of 0.26 micron rat erythrocytes were subjected to an electrical field pulse of 12 kV/cm with a decay time of 60 microseconds. Experiments using the electron microscope show that after such an electrical field pulse the uptake of latex particles by rat erythrocytes follows the stomatocytotic pathway. We show further that using electron microscopic techniques, a single section cannot demonstrate the completed uptake of a latex particle by the erythrocyte.