Mathematical modelling was used to investigate the effectiveness of creatinine adjustment for each element. The elements selected were chosen for their relevance to both current environmental and occupational exposures and future potential uses. Anonymous ERK inhibitor urine samples (n = 280, from 132 individuals) were collected from staff at the Health and Safety Laboratory (Buxton, Derbyshire, UK) and their friends/relatives. The samples came from locations over a 400 mile distance (from Glasgow to Southampton) but the majority of the samples were collected from people residing within a 50 mile radius of Buxton. All participating volunteers provided

informed consent, in accordance with HSG 167 ( Health and Safety Executive, 1997). Participants provided their initials, date of birth Epigenetics Compound Library research buy and information such as gender, smoking status, and the date and time of sample collection. Urine samples were externally posted

or hand-collected at HSL. There was no standardised time duration between collection of sample and lab receipt/freezing but typically this was less than a week. Samples were collected in 30 mL polystyrene urine collection bottles (Sterilin, Newport, UK), and were frozen at ∼−20 °C until they were analysed for creatinine and for the 61 elements of interest. Ultra purity acids supplied by Romil Ltd., Cambridge, UK. EDTA (diaminoethanetetracetic acid), and Primar 100 mg/L multi-elemental ICP–MS standard supplied by Fisher Scientific, Loughborough, UK. Rare earths were all supplied in a 10 mg/L multi-element standard ‘multi element solution 1’ SPEX Certiprep, Metuchen, NJ, USA. All single standards (including those used as internal standards) were ICP–MS standards from VWR International, Lutterworth, UK. Urine samples were defrosted at room temperature and mixed on a rotary mixer for a minimum of 20 min. All urine samples and urine quality control (QC) samples were diluted either 1 in 20 or 1 in 10 with find more the specific diluents and analysed for different

elements using each of the six methods (described in Table 1). The internal standards were made at the concentrations stated in Table 1 in the different 1 L acid diluents described and then added to each sample to dilute accordingly. All sample analysis was undertaken using inductively coupled plasma–mass spectrometry (ICP–MS). All elements besides beryllium were determined using an XSERIES 2 ICP–MS (Thermo Fisher Scientific, Hemel Hempstead, UK). Beryllium was determined on an ICAP-Q ICP–MS (Thermo Fisher Scientific, Hemel Hempstead, UK). The 61 elements were not all measured in the same analysis. The reason for this is that elements can all react differently in certain acid solutions or in certain inductively coupled plasma conditions and so compatible elements were analysed together under an optimised set of conditions.