Zhongwen Wang

Arsenic on the hands of children after playing in playgrounds.

Increasing concerns over the use of wood treated with chromated copper arsenate (CCA) in playground structures arise from potential exposure to arsenic of children playing in these playgrounds. Limited data from previous studies analyzing arsenic levels in sand samples collected from CCA playgrounds are inconsistent and cannot be directly translated to the amount of children’s exposure to arsenic. The objective of this study was to determine the quantitative amounts of arsenic on the hands of children in contact with CCA-treated wood structures or sand in playgrounds. We compared arsenic levels on the hands of 66 children playing in eight CCA playgrounds with levels of arsenic found on the hands of 64 children playing in another eight playgrounds not constructed with CCA-treated wood. The children’s age and duration of playtime were recorded at each playground. After play, children’s hands were washed in a bag containing 150 mL of deionized water. Arsenic levels in the hand-washing water were quantified by inductively coupled plasma mass spectrometry. Our results show that the ages of the children sampled and the duration of play in the playgrounds were similar between the groups of CCA and non-CCA playgrounds. The mean amount of water-soluble arsenic on children’s hands from CCA playgrounds was 0.50 μg (range, 0.0078–3.5 μg). This was significantly higher (p < 0.001) than the mean amount of water-soluble arsenic on children’s hands from non-CCA playgrounds, which was 0.095 μg (range, 0.011–0.41 μg). There was no significant difference in the amount of sand on the children’s hands and the concentration of arsenic in the sand between the CCA and non-CCA groups. The higher values of arsenic on the hands of children playing in the CCA playgrounds are probably due to direct contact with CCA-treated wood. Washing hands after play would reduce the levels of potential exposure because most of the arsenic on children’s hands was washed off with water. The maximum amount of arsenic on children’s hands from the entire group of study participants was < 4 μg, which is lower than the average daily intake of arsenic from water and food.

Identification of reactive cysteines in a protein using arsenic labeling and collision-induced dissociation tandem mass spectrometry.

Trivalent arsenicals have high affinity for thiols (such as free cysteines) in proteins. We describe here the use of this property to develop a collision-induced dissociation (CID) tandem mass spectrometry (MS/MS) technique for the identification of reactive cysteines in proteins. A trivalent arsenic species, dimethylarsinous acid (DMA (III)), with a residue mass (103.9607) and mass defect distinct from the normal 20 amino acids, was used to selectively label reactive cysteine residues in proteins. The CID fragment ions of the arsenic-labeled sequences shifted away from the more abundant normal fragments that would otherwise overlap with the ions of interest. Along with the internal and immonium ions, the arsenic-labeled fragment ions served as MS/MS signatures for identification of the binding sites and for assessment of the relative reactivity of individual cysteine residues in a protein. Using this method, we have identified two highly reactive binding sites in rat hemoglobin (Hb): Cys-13alpha and Cys-125beta. Cys-13alpha was bound to DMA (III) in the Hb of rats fed with arsenic, and this binding was responsible for arsenic accumulation in rat blood, while Cys-125beta was found to bind to glutathione in rat blood. This study revealed the relative reactivity of the cysteines in rat Hb in the following decreasing order: Cys-13alpha >> Cys-111alpha > Cys-104alpha and Cys-13alpha >> Cys-125beta > Cys-93beta. Arsenic-labeling is easy and fast for identification of active binding sites without enzymatic digestion and acid hydrolysis, and useful for characterization and identification of metal binding sites in other proteins.

Chromium on the hands of children after playing in playgrounds built from chromated copper arsenate (CCA)-treated wood.

Children’s exposure to arsenic and chromium from playground equipment constructed with chromated copper arsenate (CCA)–treated wood is a potential concern because of children’s hand-to-mouth activity. However, there exists no direct measure of Cr levels on the hands of children after playing in such playgrounds. In this study we measured both soluble and total Cr on the hands of 139 children playing in playgrounds, eight of which were constructed with CCA-treated wood and eight of which were not. Children’s age and duration of play were recorded. The hands of each child were washed after play with 150 mL deionized water, which was collected in a bag and subsequently underwent analysis of Cr and 20 other elements, using inductively coupled plasma mass spectrometry. Total average Cr on the hands of 63 children who played in CCA playgrounds was 1,112 ± 1,089 ng (median, 688; range 78–5,875). Total average Cr on the hands of 64 children who played in non-CCA playgrounds was 652 ± 586 ng (median, 492; range 61–3,377). The difference between the two groups is statistically significant (p < 0.01). Cr levels were highly correlated to both Cu (r = 0.672) and As (r = 0.736) levels in CCA playgrounds (p ≤ 0.01), but not non-CCA playgrounds (r = 0.252 and 0.486 for Cu and As, respectively). Principal-component analysis indicates that Cr, Cu, and As are more closely grouped together in CCA than in non-CCA playgrounds. These results suggest that the elevated levels of Cr and As on children’s hands are due to direct contact with CCA wood.

The Effects of SELEX Conditions on the Resultant Aptamer Pools in the Selection of Aptamers Binding to Bacterial Cells

Aptamers of high affinity and specificity have a wide range of analytic and clinical applications. Selection of DNA or RNA aptamer molecules usually involves systematic evolution of ligands via exponential enrichment (SELEX), in which a random DNA or RNA library is incubated with a target molecule, and the oligonucleotides that bind the target are then separated from the nonbinders, PCR amplified, and used as refined libraries in the next round of selection. Conventional SELEX methodologies require the use of purified target molecules and their immobilization onto a solid support. However, purified targets from cells are not always available, and fixing the target to a support may alter its conformation. To overcome these problems, we have developed a SELEX technique using live bacterial cells in suspension as targets, for selecting DNA aptamers specific to cell-surface molecules. Through the selection of aptamers binding to Lactobacillus acidophilus and Streptococcus pyogenes, we report here optimization of this technique and show how varying selection conditions impact the characteristics of resultant aptamer pools, including the binding affinity, selectivity, and the secondary structures. We found that the use of larger starting library sequence diversity, gel purification of the subsequent pools, and the introduction of counter-selection resulted in a more efficient SELEX process and more selective aptamers. A SELEX protocol with lower starting sequence diversity, the use of heat denaturation, and the absence of counter-selection still resulted in high-affinity aptamer sequences specific to the target cell types; however, the SELEX process was inefficient, requiring 20 rounds, and the aptamers were not specific to the strain of the bacterial cells. Strikingly, two different SELEX methodologies yielded the same sequence that bound strongly to the target S. pyogenes cells, suggesting the robustness of the bacterial cell-SELEX technique.