Katarzyna Styszko

Combined method of solid-phase extraction and GC-MS for determination of acidic, neutral, and basic emerging contaminants in wastewater (Poland)

In this study an analytical procedure of solid-phase extraction (SPE) followed by gas chromatography mass spectrometry (GC-MS) was elaborated and validated for simultaneous determination of 11 acidic, neutral and basic emerging contaminants in wastewater. The most frequently used pharmaceuticals were studied, i.e. five anti-inflammatory drugs – ibuprofen, diclofenac, ketoprofen, naproxen and salicylic acid, an antiepileptic drug carbamazepine, clofibric acid, antibacterial triclosan, a plasticiser bisphenol A and two β-blockers – propranolol and metoprolol. Sample enrichment was performed using Oasis HLB sorbent. Sample pH and sorbent washing step during the solid-phase extraction were optimised on real wastewater samples. Recoveries of the most polar acidic compounds diminished substantially when the alkalinity of the sample loaded into the cartridge increased. Thus finally wastewater was extracted at pH 2.0. Before elution, sorbent was washed subsequently with 5% methanol in water and n-hexane, which resulted in best recoveries of most of the target compounds and reduced a co-elution phenomena with respect to β-blockers. The optimised method was successfully applied to influent and effluent samples from wastewater treatment plant, Krakow, Poland. All target compounds except propranolol were identified in wastewater at a concentration up to 12.8 µg L−1.

Desorption of biocides from renders modified with acrylate and silicone

Biocides are used in the building industry to prevent algal, bacterial and fungal growth on polymericrenders and thus to protect buildings. However, these biocides are leached into the environment. To better understand this leaching, the sorption/desorption of biocides in polymeric renders was assessed. In this study the desorption constants of cybutryn, carbendazim, iodocarb, isoproturon, diuron, dichloro-N-octylisothiazolinone and tebuconazole towards acrylate and silicone based renders were assessed at different pH values. At pH 9.5 (porewater) the constants for an acrylate based render varied between 8 (isoproturon) and 9634 (iodocarb) and 3750 (dichloro-N-octylisothiazolinone), respectively. The values changed drastically with pH value. The results for the silicone based renders were in a similar range and usually the compounds with high sorption constants for one polymer also had high values for the other polymer. Comparison of the octanol water partitioning constants (Kow) with the render/water partitioning constants (Kd) revealed similarities, but no strong correlation. Adding higher amounts of polymer to the render material changed the equilibria for dichloro-N-octylisothiazolinone, tebuconazole, cybutryn, carbendazim but not for isoproturon and diuron.

Leaching of biocides from polymer renders under wet/dry cycles – Rates and mechanisms

In this study it was tested, which mechanism for the transport of biocides in polymeric renders is more relevant: (1) evaporative transports (meaning there is a flow of water through the material due to evaporation on the surface), which transports also the biocides to the surface, (2) transport through the polymer and (3) transport through water filled pores. It turned out that under the experimental conditions evaporative transport was not relevant, while transport through soaked (constantly wetted) renders was considerably faster than by other means. Additionally it turned out that also the equilibria were influenced by the water content. Differences in equilibria can be up to factor 10 between constantly wetted (soaked) and un-wetted materials. The two tested materials (one silicone and one acrylate render) had significantly different leaching behavior concerning equilibria and dynamics of mass flows, but for both the pre-wetted materials leached most.