A new heterobifunctional linker containing an aldehyde-reactive aminooxy group and a thiol-reactive maleimide group, namely N-[4-(aminooxy)butyl]maleimide, was synthesized as a stable HCl salt by O-alkylation of either N-hydroxyphthalimide or N-(4-monomethoxytrityl)hydroxylamine, followed by N-alkylation of maleimide, in an overall yield of 18% (seven steps) or 29% (five steps), respectively. This heterobifunctional linker allowed a simple and efficient synthesis of a maleimide-containing thiol-reactive (18)F-labeling agent. Thus, N-[4-[(4-[(18)F]fluorobenzylidene)aminooxy]butyl]maleimide (specific activity: approximately 3000 Ci/mmol at end of synthesis) was synthesized in two steps involving the preparation of 4-[(18)F]fluorobenzaldehyde, followed by its aminooxy-aldehyde coupling reaction to the heterobifunctional linker, with an overall radiochemical yield of approximately 35% (decay corrected) within approximately 60 min from end of bombardment. Initial (18)F-labeling experiments were carried out using a thiol-containing tripeptide glutathione (GSH) and a 5'-thiol-functionalized oligodeoxynucleotide (5'-S-ODN) in phosphate-buffered saline (PBS, pH 7.5). After standing at room temperature for 10 min, the (18)F-labeled GSH and 5'-S-ODN were obtained in (18)F-labeling yields of approximately 70% and approximately 5% (decay-corrected), respectively. The heterobifunctional linker is easy to synthesize and provides a facile access to the maleimide-containing thiol-reactive (18)F-labeling agent, which could be advantageously employed in the development of (18)F-labeled biomomolecules for use with positron emission tomography.

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One recognized cause of cardiorespiratory diseases is air pollution. Older adults (OA) are one of the most vulnerable groups that suffer from its adverse effects. The objective of the study was to analyze the association between exposure to air pollution and changes in cardiorespiratory variables in OA. Observational prospective cohort study. Health questionnaires, blood pressure (BP) measurements, lung functions, respiratory symptoms, physical activity levels, and physical fitness in high and low exposure to air pollution were all methods used in evaluating OAs in communes with high contamination rates. Linear and logistic models were created to adjust for variables of interest. A total of 92 OA participated in this study. 73.9% of the subjects were women with 72.3 ± 5.6 years. 46.7% were obese, while 12.1% consumed tobacco. The most prevalent diseases found were hypertension, diabetes, and cardiovascular disease. Adjusted linear models maintained an increase for systolic BP of 6.77 mmHg (95% CI: 1.04-12.51), and diastolic of 3.51 mmHg (95% CI: 0.72-6.29), during the period of high exposure to air pollution. The adjusted logistic regression model indicated that, during the period of high exposure to air pollution increase the respiratory symptoms 4 times more (OR: 4.43, 95% CI: 2.07-10.04) in the OA. The results are consistent with an adverse effect on cardiorespiratory variables in periods of high exposure to air pollution in the OA population.