Abstract

Pollen is an important component of bioaerosol and the distribution of pollen and its relationship with meteorological parameters can be analyzed to better prevent hay fever. Pollen assemblages can also provide basic data for analyzing the relationship between bioaerosol and PM. We collected 82 samples of airborne pollen using a TSP large flow pollen collector from June 1, 2015 to June 1, 2016, from central Zhanjiang city in South China. We also conducted a survey of the nearby vegetation at the same time, in order to characterize the major plant types and their flowering times. We then used data on daily temperature, relative humidity, precipitation, vapor pressure and wind speed from a meteorological station in the center of Zhanjiang City to assess the relationship between the distribution of airborne pollen and meteorological parameters. Our main findings and conclusions are as follows: (1) We identified 15 major pollen types, including Pinus, Castanopsis, Myrica, Euphorbiaceae, Compositae, Gramineae, Microlepia and Polypodiaceae. From the vegetation survey, we found that the pollen from these taxa represented more than 75% of local pollen, while the pollen of Podocarpus, Dacrydium and other regional pollen types represented less than 25%. (2) The pollen concentrations varied significantly in different seasons. The pollen concentrations were at a maximum in spring, consisting mainly of tree pollen; the pollen concentrations were at an intermediate level in autumn and winter, consisting mainly of herb pollen and fern spores; and the pollen concentrations in summer were the lowest, consisting mainly of fern spores. (3) Analysis of the relationship between airborne pollen concentrations and meteorological parameters showed that variations in the pollen concentrations were mainly affected by temperature and relative humidity. In addition, there were substantial differences in these relationships in different seasons. In spring, pollen concentrations were mainly affected by temperature; in summer, they were mainly affected by the direction of the maximum wind speed; in autumn, they were mainly affected by relative humidity and temperature; and in winter, they were mainly affected by relative humidity and wind speed. Temperature and relative humidity promote plant growth and flowering. Notably, the variable wind direction in summer and the increased wind speed in winter and spring are conductive to pollen transmission. (4) Of the 15 major pollen types, Moraceae, Artemisia and Gramineae are the main allergenic pollen types, with peaks in concentration during April-May, August-September, and October-December, respectively. (5) Atypical weather conditions have substantial effects on pollen dispersal. In South China, the pollen concentrations in the sunny day were usually significantly higher than that of the rainy day. The pollen concentrations increased in short rainy days, which usually came from the Herb and Fern pollen. The pollen concentrations decreased in continuous rainy days especially for the Tree and Shrub pollen. the pollen concentrations in the sunny days were usually significantly higher than that in the rainy days. The pollen concentrations increased in short and strong rainfall.

Highlights

  • Bioaerosol include pollen, fungi and bacteria, which have a small particle size (0.01–100μm) and can be inhaled and enter human lungs, posing a threat to human health

  • The spatiotemporal distribution of airborne pollen is affected by environmental factors to some extent, it is clear that the characteristics of airborne pollen assemblages reflect the local vegetation, with some degree of influence by the regional or extra regional vegetation [48,49]

  • The pollen types found in both vegetation survey and pollen assemblages are identified as pollen produced by local vegetation

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Summary

Introduction

Bioaerosol include pollen, fungi and bacteria, which have a small particle size (0.01–100μm) and can be inhaled and enter human lungs, posing a threat to human health. The source of bioaerosol, its spatial and temporal distribution, and its influencing factors have received extensive attention from the social and scientific communities, especially in countries with severe air pollution such as China and India [1]. With more and more air pollution, the relationship between the concentrations of bioaerosol (airborne pollen) and meteorological parameters had become more complex. SO2, O3 and PM affect the flowering times of several plant species; for example, the flowering time of Faxious and Populus was related to the concentration of O3 in atmospheric pollutants in Leon (Spain) [2]. Research on bioaerosol and meteorological parameters was only recently initiated and it mainly concentrated in Beijing, Qingdao, Xi’an and other large cities in the North [1,5,6]

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