Objective To assess the health risks of gaseous pollutants in the indoor air of hair and beauty salons in Jinan, and to provide technical support for strengthening the hygiene management of hair and beauty salons in Jinan and promoting the improvement of conditions. Methods Every year, indoor air samples were collected from 10-16 selected hair salons and beauty salons in Jinan, and relevant information on practitioners was also collected. According to the ^“Technical Guidelines for Environmental Health Risk Assessment of Chemicals^”, an assessment was conducted on the carcinogenic and non-carcinogenic risks of inhalation pathways of gaseous pollutants in the indoor air of hair salons and beauty salons. Results Benzene, toluene, xylene, formaldehyde, and ammonia were detected in the indoor air of hair salons and beauty salons. Formaldehyde, benzene, and ammonia all exceeded the standard in hair salons and beauty salons. The median risk values of formaldehyde and benzene for carcinogenesis in hair salons and beauty salons were both greater than 10^-6, with maximum values higher than 10^-4. The median chronic non-carcinogenic risk value of formaldehyde in the indoor air of hair salons and beauty salons was greater than 1. The median chronic non-carcinogenic risk values for benzene and ammonia were both less than 1, but the maximum risk value was greater than 1. Conclusion Benzene and formaldehyde in the indoor air of hair salons and beauty salons in Jinan City have carcinogenic and non-carcinogenic risks, while ammonia has non-carcinogenic risks, which should be paid attention to.

Background Ozone (O₃), a key air pollutant, significantly contributes to cardiovascular disease (CVD)-related mortality, with particularly pronounced effects in the elderly. Objective To explore the association between acute O₃ exposure and mortality from CVD and its subtypes in the elderly population in Jinan, and to investigate the modifying effects of gender,age, and seasonal factors on O₃-related effects, as well as to clarify the interaction with other air pollutants. Methods Daily mortality data for CVD, air pollutants, and meteorological parameters were collected in Jinan from 2015 to 2023. Generalized additive models (GAM) combined with distributed lag nonlinear models (DLNM) were used to analyze the lag effects of acute O₃ exposure on mortalities from CVD, ischemic heart disease (IHD), and stroke in elderly individuals aged ≥60 years. Subgroup analyses were conducted to explore effect differences by gender (male vs. female), age (non-high-aged elderly<80 years vs. high-aged elderly ≥80 years), and season (warm season: April–September vs. cold season: October–March of the following year). Relative excess risk due to interaction (RERI), attributable proportion of interaction (API), and Synergy index (SI) were used to assess the interactions of O₃ with PM_2.5 and NO₂. Results During the study period, the mean daily concentration of ozone reached (105.01 ± 54.18) μg·m⁻³, exceeding the Grade I limit value specified in Ambient Air Quality Standard (GB 3095–2012). Among the 203834 CVD deaths, IHD (53.07%) and stroke (33.33%) were the predominant mortality subtypes. The single-day lag analysis revealed peak excess risk (ER) for CVD mortality at lag0 (ER=0.64%, 95%CI: 0.29%, 1.00%) per 10 μg·m⁻³ O₃ increase. The cumulative effects peaked at lag04 (ER=1.61%, 95%CI: 0.77%, 2.46%). The subtype-specific analyses showed the maximal single-day effects at lag0 were identified for both IHD (ER=0.61%, 95%CI: 0.20%, 1.03%) and stroke (ER=0.65%, 95%CI: 0.19%, 1.11%), while the cumulative risks peaked at lag04 for IHD (ER=1.54%, 95%CI: 0.56%, 2.54%) and lag03 for stroke (ER=1.74%, 95%CI: 0.76%, 2.73%). The gender subgroup analyses suggested that both male and female subgroups showed the most significant impact on CVD mortality at lag0, with ER values of 0.53% (95%CI: 0.11%, 0.95%) and 0.75% (95%CI: 0.33%, 1.18%), respectively, but the differences were not statistically significant (P>0.05). No statistically significant difference in effect values was found between high-aged and non-high-aged elderly (P>0.05) after age subgroup analyses. The seasonal subgroup analyses indicated that the effects of O₃ on CVD and its subtypes in the warm season were significantly higher than those in the cold season (P<0.05). At lag0 in the warm season, the ER values for CVD, IHD, and stroke mortality were 0.86% (95%CI: 0.57%, 1.14%), 0.84% (95%CI: 0.49%, 1.19%), and 0.84% (95%CI: 0.43%, 1.26%), respectively. The interaction analyses revealed an antagonistic effect between O₃ and PM_2.5 on stroke mortality in the elderly [RERI=−4.64% (95%CI: −9.27%, −0.01%), API=−4.39% (95%CI: −8.77%, −0.01%), SI=0.55 (95%CI: 0.26, 0.84)]. The O₃ effect remained robust in the multi-pollutant models (P<0.05). Conclusion Acute O₃ exposure increases the risk of mortality from CVD and its subtypes in the elderly, and this effect is amplified in the warm season. Additionally, O₃ and PM_2.5 have an antagonistic effect on stroke mortality in the elderly.