The spatiotemporal variation characteristics of SO2 concentration inside and outside urban forests during the heating season in Beijing in 2015
To explore the heating season inside and outside urban forests ρ Based on the data from the air quality monitoring station in Xishan National Forest Park and the real-time data from the botanical garden monitoring station of the Beijing Environmental Protection Monitoring Center, the dynamic changes and differences of (SO2) were analyzed for the 2015 heating season in and out of urban forests ρ Changes and influencing factors of (SO2). The results indicate that: inside and outside the forest ρ The daily variation of (SO2) shows a double peak and double valley pattern, reaching its peak around 09:00 to 11:00 and 20:00 to 22:00; Sampling period ρ The monthly variation of (SO2) shows an insignificant 'V' pattern, with the highest value appearing in January. The values inside and outside the forest are (25.8 ± 9.2) and (31.7 ± 23.4), respectively μ G/m3, with the lowest value appearing in November, and the values inside and outside the forest are (19.0 ± 5.2) and (13.0 ± 11.2), respectively μ G/m3. In the forest ρ (SO2) is lower than outside the forest from January to March, higher than outside the forest from November to December, and within the forest ρ The change of SO2 is relatively gentle outside the forest; Meteorological conditions affecting urban forests during the heating season ρ Changes in (SO2) have a significant impact: precipitation has a significant impact on ρ (SO2) has a significant reduction effect, with strong winds having the effect of dispersing SO2 and being influenced by wind direction; ρ The relationship between (SO2) and temperature is not significant (P=0.05, R<0.40), but there is a significant linear relationship with relative humidity of the air( α= 0.05, Sig=0.00), the impact of meteorological factors inside the forest is lower than that outside the forest. Research has shown that urban forests have a certain buffering, resistance, and absorption capacity for gaseous pollutants. Therefore, attention should be paid to the development of urban forest ecosystems, and their ecological benefits should be fully utilized to improve the quality of urban atmospheric environment