Jin-A Park
Current Organizations / Institutes
The organizations/institutes from the scholar's latest article
Research Subjects
Jin-A Park has a total of 5 co-authors. Here are the top co-authors by number of shared publications:
- Hyo-Jae Seo
Department of Rural Construction Engineering, College of Agriculture & Life Sciences, Jeonbuk National University, Jeonju 54896, Republic of Korea
1 shared publication - Il-Hwan Seo
Department of Rural Construction Engineering, College of Agriculture & Life Sciences, Jeonbuk National University, Jeonju 54896, Republic of Korea
1 shared publication - Jin-Ho Kim
Climate Change Division, National Institute of Agricultural Sciences, Rural Development Administration (RDA), Wanju 55365, Republic of Korea
1 shared publication - Minwook Kim
Climate Change Division, National Institute of Agricultural Sciences, Rural Development Administration (RDA), Wanju 55365, Republic of Korea
1 shared publication - Yun-Sik Shin
Climate Change Division, National Institute of Agricultural Sciences, Rural Development Administration (RDA), Wanju 55365, Republic of Korea
1 shared publication
Latest Publications
- Open Access
- 23 October 2026
- Published by MDPI AG in Agriculture
- Vol. 16 (21) , 2316
Characteristics of Air-Pollutant Concentration Variations Across Rice Cultivation Stages at Four Paddy Sites in Korea
Agricultural activities emit ammonia (NH3) and particulate matter (PM), yet Korean air-quality monitoring is concentrated in urban areas. We analyzed daily PM10, PM2.5, NO2, SO2, and NH3 at four rice-paddy sites (March 2023–June 2025) across five calendar-defined cultivation stages, which are confounded with season. We therefore separated winter from early spring, calculated increments relative to paired urban stations, and compared recorded operation days with other days of the same month. PM10 was highest in the preparation stage (46.08 vs. 23.97 μg/m3 in growth management; η2 = 0.092), and the March–April maximum persisted after winter was separated and after meteorological adjustment. However, at the three sites without a persistent local coarse-particle source, the early-spring PM10 increment over urban stations was the lowest of all periods (−7.62 μg/m3), while local PM10 and PM2.5 increments peaked in July–September. In exploratory contrasts, the PM2.5 increment was 2.3 μg/m3 higher on tillage/leveling days (p = 0.005; q = 0.063). NH3 was governed mainly by site (partial η2: site 0.256, site × stage 0.145, stage 0.033; site means 8.6–37.0 ppb). The calendar-stage PM contrast largely reflects the regional seasonal cycle, whereas agricultural influences appear as operation day and warm-season local increments and as site-specific NH3 levels.
- 23 October 2026
- Published by MDPI AG in Agriculture
- Vol. 16 (21) , 2316
Open AccessCharacteristics of Air-Pollutant Concentration Variations Across Rice Cultivation Stages at Four Paddy Sites in Korea
Agricultural activities emit ammonia (NH3) and particulate matter (PM), yet Korean air-quality monitoring is concentrated in urban areas. We analyzed daily PM10, PM2.5, NO2, SO2, and NH3 at four rice-paddy sites (March 2023–June 2025) across five calendar-defined cultivation stages, which are confounded with season. We therefore separated winter from early spring, calculated increments relative to paired urban stations, and compared recorded operation days with other days of the same month. PM10 was highest in the preparation stage (46.08 vs. 23.97 μg/m3 in growth management; η2 = 0.092), and the March–April maximum persisted after winter was separated and after meteorological adjustment. However, at the three sites without a persistent local coarse-particle source, the early-spring PM10 increment over urban stations was the lowest of all periods (−7.62 μg/m3), while local PM10 and PM2.5 increments peaked in July–September. In exploratory contrasts, the PM2.5 increment was 2.3 μg/m3 higher on tillage/leveling days (p = 0.005; q = 0.063). NH3 was governed mainly by site (partial η2: site 0.256, site × stage 0.145, stage 0.033; site means 8.6–37.0 ppb). The calendar-stage PM contrast largely reflects the regional seasonal cycle, whereas agricultural influences appear as operation day and warm-season local increments and as site-specific NH3 levels.