高速公路收费站附近栎林森林结构改变后颗粒物浓度及气象变量的变化

IF 1.8 Q2 FORESTRY
Sumin Choi, S. Yoo, Jaeho Yeo, C. Park
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引用次数: 1

摘要

摘要栎树是阔叶林的主要优势树种,但对森林结构改变后颗粒物浓度变化的研究较少。本研究分析了公路污染源附近栎林结构变化对落叶后气象因子和大气颗粒物(PM)浓度变化的影响。2019年6月,在江原道高城郡美色岭收费站附近的橡树林CFS中,砍伐了33%的树木。为了解处理地(TRS为改变森林结构的样地)与对照地(CS)叶片出苗的变化情况,于2019年12月和2020年6月对不同树高的叶高剖面(FHP, %)进行了调查。结果表明:2个月TRS的FHP(%)均低于CS,且TRS后中层冠层FHP增加,上层冠层FHP降低;与3月气温(p < 0.01)和6月风速(p < 0.01)呈极显著相关,说明CFS改善了气流。3月份CS (PM10: 37.7µg/m3, PM2.5: 21.1µg/m3)与TRS (PM10: 37.5µg/m3, PM2.5: 20.8µg/m3)的PM浓度无显著差异;但6月份TRS的PM浓度(PM10: 65.0µg/m3, PM2.5: 26.2µg/m3)低于CS (PM10: 73.9µg/m3, PM2.5: 29.1µg/m3)。6月份TRS中PM减少率(%)(PM10: 11.3%, PM2.5: 10.0%)高于3月份(PM10: 2.3%, PM2.5: 4.0%)。6月PM浓度较低可能与叶片出芽有关。结果表明,林内各气象因子和PM浓度在落叶后发生了变化,温度和风速与PM浓度有较强的相关性。这些结果表明,CFS可以改变森林结构和橡树林的气流,PM可以流动并沉降到森林内部收费站附近的污染源中。研究结果为了解高速公路污染源附近以橡树为主的落叶林中CFS对PM的减少效果提供了基础信息。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Changes in particulate matter concentration and meteorological variables after changing forest structure in oak-dominated forests nearby highway tollgate
Abstract Oak species are the major dominant tree species of deciduous forests, but the little study was conducted to understand the change of particulate matter concentration after changing the forest structure. This study analyzed the effects of changing forest structure (CFS) on the changes in meteorological factors and air particulate matter (PM) concentration after leaf emergence in oak-dominated forests nearby highway pollutants’ sources. In June 2019, 33% of the total trees were removed from the CFS of oak forests in the vicinity of the tollgate of Misiryeong in Goseong-gun, Gangwon-do, Korea. To understand the changes in leaf emergence between the treatment site (TRS is the site changing forest structure) and control site (CS), we investigated the foliage height profile (FHP, %) at each class of tree height in December 2019 and June 2020. The results showed that FHP (%) was lower in TRS than in CS in both months, and the FHP of the middle canopy class increased after TRS while that of the upper canopy class decreased. The correlation was significant with temperature in March (p < 0.01) and with wind speed in June (p < 0.01), indicating that CFS improved the airflow. There was no significant difference in the PM concentration between CS (PM10: 37.7 µg/m3, PM2.5: 21.1 µg/m3) and TRS (PM10: 37.5 µg/m3, PM2.5: 20.8 µg/m3) in March; however, the PM concentration in TRS (PM10: 65.0 µg/m3, PM2.5: 26.2 µg/m3) was lower than that in CS (PM10: 73.9 µg/m3, PM2.5: 29.1 µg/m3) in June. The rate of PM reduction (%) in TRS was higher in June (PM10: 11.3%, PM2.5: 10.0%) than in March (PM10: 2.3%, PM2.5: 4.0%). The low value of PM concentration in June could be related to the leaf emergence. Overall, the results indicated that meteorological factors and PM concentrations had changed in the inner part of the forest after leaf emergence and that the temperature and wind speed were strongly correlated with the PM concentration. These results suggest that CFS can change the forest structure and the airflow in oak-dominated forests, which PM can flow and settle down into the inner forest's nearby pollutants sources of a tollgate. The results provide basic information for understanding the reduction effect of PM by CFS in oak-dominated deciduous forests nearby highway pollutants source.
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来源期刊
CiteScore
3.30
自引率
5.30%
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审稿时长
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