Purpose: This study investigated the effects of aroma inhalation on sleep quality, professional quality of life (QoL), and near-misses in medication errors during night shifts among emergency room nurses. Methods: A randomized crossover experimental design was used to determine the effects of this intervention. The research participants included 55 nurses (29 in group 1 and 26 in group 2) who worked as nurses in the emergency room at a tertiary general hospital in Chungcheongbuk-do, South Korea. Aroma inhalation was conducted on the night shift. Sleep quality, professional QoL, and near-misses in medication were measured before and after inhalation of the aroma. Data was analyzed using the independent t-test, the chi-square test, and a linear mixed-effects model. Results: The aroma treatment group had significantly better sleep quality than the non-treatment group (p < .010), and the sleep time on the third day of aroma treatment was longer than that of the non-treatment group (p = .008). However, there were no signs of improvement in professional QoL or near-misses in medication errors in response to aroma treatment. Conclusion Aroma inhalation effectively improved sleep quality and increased sleep duration in emergency room nurses. Therefore, aroma inhalation is suggested as an intervention to improve the sleep quality of emergency room nurses who work night shifts. Follow-up studies are needed to build a more robust evidence base to inform strategies for improving nurses' professional QoL and patient safety during medication management.

Purpose: This study investigated the effects of aroma inhalation on sleep quality, professional quality of life (QoL), and near-misses in medication errors during night shifts among emergency room nurses. Methods: A randomized crossover experimental design was used to determine the effects of this intervention. The research participants included 55 nurses (29 in group 1 and 26 in group 2) who worked as nurses in the emergency room at a tertiary general hospital in Chungcheongbuk-do, South Korea. Aroma inhalation was conducted on the night shift. Sleep quality, professional QoL, and near-misses in medication were measured before and after inhalation of the aroma. Data was analyzed using the independent t-test, the chi-square test, and a linear mixed-effects model. Results: The aroma treatment group had significantly better sleep quality than the non-treatment group (p < .010), and the sleep time on the third day of aroma treatment was longer than that of the non-treatment group (p = .008). However, there were no signs of improvement in professional QoL or near-misses in medication errors in response to aroma treatment. Conclusion Aroma inhalation effectively improved sleep quality and increased sleep duration in emergency room nurses. Therefore, aroma inhalation is suggested as an intervention to improve the sleep quality of emergency room nurses who work night shifts. Follow-up studies are needed to build a more robust evidence base to inform strategies for improving nurses' professional QoL and patient safety during medication management.

Purpose: This study investigated the effects of aroma inhalation on sleep quality, professional quality of life (QoL), and near-misses in medication errors during night shifts among emergency room nurses. Methods: A randomized crossover experimental design was used to determine the effects of this intervention. The research participants included 55 nurses (29 in group 1 and 26 in group 2) who worked as nurses in the emergency room at a tertiary general hospital in Chungcheongbuk-do, South Korea. Aroma inhalation was conducted on the night shift. Sleep quality, professional QoL, and near-misses in medication were measured before and after inhalation of the aroma. Data was analyzed using the independent t-test, the chi-square test, and a linear mixed-effects model. Results: The aroma treatment group had significantly better sleep quality than the non-treatment group (p < .010), and the sleep time on the third day of aroma treatment was longer than that of the non-treatment group (p = .008). However, there were no signs of improvement in professional QoL or near-misses in medication errors in response to aroma treatment. Conclusion Aroma inhalation effectively improved sleep quality and increased sleep duration in emergency room nurses. Therefore, aroma inhalation is suggested as an intervention to improve the sleep quality of emergency room nurses who work night shifts. Follow-up studies are needed to build a more robust evidence base to inform strategies for improving nurses' professional QoL and patient safety during medication management.

Purpose: This study investigated the effects of aroma inhalation on sleep quality, professional quality of life (QoL), and near-misses in medication errors during night shifts among emergency room nurses. Methods: A randomized crossover experimental design was used to determine the effects of this intervention. The research participants included 55 nurses (29 in group 1 and 26 in group 2) who worked as nurses in the emergency room at a tertiary general hospital in Chungcheongbuk-do, South Korea. Aroma inhalation was conducted on the night shift. Sleep quality, professional QoL, and near-misses in medication were measured before and after inhalation of the aroma. Data was analyzed using the independent t-test, the chi-square test, and a linear mixed-effects model. Results: The aroma treatment group had significantly better sleep quality than the non-treatment group (p < .010), and the sleep time on the third day of aroma treatment was longer than that of the non-treatment group (p = .008). However, there were no signs of improvement in professional QoL or near-misses in medication errors in response to aroma treatment. Conclusion Aroma inhalation effectively improved sleep quality and increased sleep duration in emergency room nurses. Therefore, aroma inhalation is suggested as an intervention to improve the sleep quality of emergency room nurses who work night shifts. Follow-up studies are needed to build a more robust evidence base to inform strategies for improving nurses' professional QoL and patient safety during medication management.

Children face the excitement of a changing world but also encounter environmental threats to their health that were neither known nor suspected several decades ago. Children are at particular risk of exposure to pollutants that are widely dispersed in the air, water, and food. Children and adolescents are exposed to chemical, physical, and biological risks at home, in school, and elsewhere. Actions are needed to reduce these risks for children exposed to a series of environmental hazards. Exposure to a number of persistent environmental pollutants including air pollutants, endocrine disruptors, noise, electromagnetic waves (EMWs), tobacco and other noxious substances, heavy metals, and microplastics, is linked to damage to the nervous and immune systems and affects reproductive function and development. Exposure to environmental hazards is responsible for several acute and chronic diseases that have replaced infectious diseases as the principal cause of illnesses and death during childhood. Children are disproportionately exposed to environmental toxicities. Children drink more water, eat more food, and breathe more frequently than adults. As a result, children have a substantially heavier exposure to toxins present in water, food, or air than adults. In addition, their hand-to-mouth behaviors and the fact that they live and play close to the ground make them more vulnerable than adults. Children undergo rapid growth and development processes that are easily disrupted. These systems are very delicate and cannot adequately repair thetional development in children’s environmental health was the Declaration of the Environment Leaders of the Eight on Children’s Environmental Health by the Group of Eight. In 2002, the World Health Organization launched an initiative to improve children’s environmental protection effort. Here, we review major environmental pollutants and related hazards among children and adolescents.

Children face the excitement of a changing world but also encounter environmental threats to their health that were neither known nor suspected several decades ago. Children are at particular risk of exposure to pollutants that are widely dispersed in the air, water, and food. Children and adolescents are exposed to chemical, physical, and biological risks at home, in school, and elsewhere. Actions are needed to reduce these risks for children exposed to a series of environmental hazards. Exposure to a number of persistent environmental pollutants including air pollutants, endocrine disruptors, noise, electromagnetic waves (EMWs), tobacco and other noxious substances, heavy metals, and microplastics, is linked to damage to the nervous and immune systems and affects reproductive function and development. Exposure to environmental hazards is responsible for several acute and chronic diseases that have replaced infectious diseases as the principal cause of illnesses and death during childhood. Children are disproportionately exposed to environmental toxicities. Children drink more water, eat more food, and breathe more frequently than adults. As a result, children have a substantially heavier exposure to toxins present in water, food, or air than adults. In addition, their hand-to-mouth behaviors and the fact that they live and play close to the ground make them more vulnerable than adults. Children undergo rapid growth and development processes that are easily disrupted. These systems are very delicate and cannot adequately repair thetional development in children’s environmental health was the Declaration of the Environment Leaders of the Eight on Children’s Environmental Health by the Group of Eight. In 2002, the World Health Organization launched an initiative to improve children’s environmental protection effort. Here, we review major environmental pollutants and related hazards among children and adolescents.

Children face the excitement of a changing world but also encounter environmental threats to their health that were neither known nor suspected several decades ago. Children are at particular risk of exposure to pollutants that are widely dispersed in the air, water, and food. Children and adolescents are exposed to chemical, physical, and biological risks at home, in school, and elsewhere. Actions are needed to reduce these risks for children exposed to a series of environmental hazards. Exposure to a number of persistent environmental pollutants including air pollutants, endocrine disruptors, noise, electromagnetic waves (EMWs), tobacco and other noxious substances, heavy metals, and microplastics, is linked to damage to the nervous and immune systems and affects reproductive function and development. Exposure to environmental hazards is responsible for several acute and chronic diseases that have replaced infectious diseases as the principal cause of illnesses and death during childhood. Children are disproportionately exposed to environmental toxicities. Children drink more water, eat more food, and breathe more frequently than adults. As a result, children have a substantially heavier exposure to toxins present in water, food, or air than adults. In addition, their hand-to-mouth behaviors and the fact that they live and play close to the ground make them more vulnerable than adults. Children undergo rapid growth and development processes that are easily disrupted. These systems are very delicate and cannot adequately repair thetional development in children’s environmental health was the Declaration of the Environment Leaders of the Eight on Children’s Environmental Health by the Group of Eight. In 2002, the World Health Organization launched an initiative to improve children’s environmental protection effort. Here, we review major environmental pollutants and related hazards among children and adolescents.

Children face the excitement of a changing world but also encounter environmental threats to their health that were neither known nor suspected several decades ago. Children are at particular risk of exposure to pollutants that are widely dispersed in the air, water, and food. Children and adolescents are exposed to chemical, physical, and biological risks at home, in school, and elsewhere. Actions are needed to reduce these risks for children exposed to a series of environmental hazards. Exposure to a number of persistent environmental pollutants including air pollutants, endocrine disruptors, noise, electromagnetic waves (EMWs), tobacco and other noxious substances, heavy metals, and microplastics, is linked to damage to the nervous and immune systems and affects reproductive function and development. Exposure to environmental hazards is responsible for several acute and chronic diseases that have replaced infectious diseases as the principal cause of illnesses and death during childhood. Children are disproportionately exposed to environmental toxicities. Children drink more water, eat more food, and breathe more frequently than adults. As a result, children have a substantially heavier exposure to toxins present in water, food, or air than adults. In addition, their hand-to-mouth behaviors and the fact that they live and play close to the ground make them more vulnerable than adults. Children undergo rapid growth and development processes that are easily disrupted. These systems are very delicate and cannot adequately repair thetional development in children’s environmental health was the Declaration of the Environment Leaders of the Eight on Children’s Environmental Health by the Group of Eight. In 2002, the World Health Organization launched an initiative to improve children’s environmental protection effort. Here, we review major environmental pollutants and related hazards among children and adolescents.

This study aimed to compare the pharmacokinetic (PK) and safety profiles of 2 fenofibric acid formulations under fasting and fed conditions. The reference was a 135 mg capsule, while the test was a 110 mg enteric-coated tablet. This randomized, open-label, two-sequence, two-period crossover phase 1 clinical trial was conducted in healthy Korean men. Sixty participants were enrolled in each of the fasting and feeding groups. Blood samples were collected 72 hours after drug administration. PK parameters were calculated using a noncompartmental method with Phoenix WinNonlin ® . A total of 53 and 51 participants from the fasting and feeding groups, respectively, completed the study. The geometric mean ratio and 90% confidence intervals of the maximum concentration (C max ) and area under the concentration-time curve to the last measurable plasma concentration were 0.9195 (0.8795–0.9614) and 0.8630 (0.8472–0.8791) in the fasting study and 1.0926 (1.0102–1.1818) and 0.9998 (0.9675–1.0332) in the fed study, respectively. The time to reach C max of the enteric-coated tablet compared to that of the capsule was extended by 1 and 3 hours under fasting and fed conditions, respectively. In conclusion, enteric-coated tablets have a higher bioavailability than capsules. In addition, the enteric-coated tablet was smaller than the capsule, making it easier for patients to swallow.

Background: In Korea, the birth rate is declining at an alarming pace. This study aimed to investigate the changes and trends in the population count, number of births, and birth rate in Korea, in the past and future. Methods: Data regarding the total number of births, crude birth rate, and total fertility rate were collected from the “Statistics Korea Census” of the national statistical portal, census report, and Statistics Korea’s “2020 Population Trend Survey for 1981–2020, provisional results of birth and death statistics.” We used the Organisation for Economic Co-operation and Development 2019 Family Database for the TFR. To develop a better understanding of the data in this study, we classified it according to the modern history of Korea. Results: The changes and trends in the number of births and fertility rate in Korea, after liberation, were due to the birth control policy that restricted births. In Korea’s low fertility society, which began in the mid-2000s, the fertility rate dropped to below 0.84 in 2020, despite policies to improve the quality of the population. The death toll has reached 300,000, entering an era of population decline. Conclusion As we enter the era of population decline, we are in a direction that will cause various socioeconomic problems, from demographic problems to future population decline.