Literature DB >> 22211164

The revised edition of korean calendar for allergenic pollens.

Jae-Won Oh1, Ha-Baik Lee, Im-Joo Kang, Seong-Won Kim, Kang-Seo Park, Myung-Hee Kook, Bong-Seong Kim, Hey-Sung Baek, Joo-Hwa Kim, Ja-Kyung Kim, Dong-Jin Lee, Kyu-Rang Kim, Young-Jin Choi.   

Abstract

The old calendar of pollens did not reflect current pollen distribution and concentrations that can be influenced by changes of weather and environment of each region in South Korea. A new pollen calendar of allergenic pollens was made based on the data on pollen concentrations obtained in eight regions nationwide between 1997 and 2009. The distribution of pollen was assessed every day at 8 areas (Seoul, Guri, Busan, Daegu, Jeonju, Kwangju, Kangneung, and Jeju) for 12 years between July 1, 1997 and June 30, 2009. Pollens were collected by using Burkard 7-day sampler (Burkard Manufacturing Co Ltd, UK). Pollens which were stained with Calberla's fuchsin staining solution were identified and counted. Pine became the highest pollen in May, and the pollen concentrations of oak and birch also became high. Ragweed appeared in the middle of August and showed the highest pollen concentration in the middles of September. Japanese hop showed a high concentration between the middle of August and the end of September, and mugwort appeared in the middles of August and its concentration increased up until early September. In Kangneung, birch appeared earlier, pine showed a higher pollen concentration than in the other areas. In Daegu, Oriental thuja and alder produced a large concentration of pollens. Pine produced a large concentration of pollens between the middle of April and the end of May. Weeds showed higher concentrations in September and mugwort appeared earlier than ragweed. In Busan the time of flowering is relatively early, and alder and Oriental thuja appeared earliest among all areas. In Kwangju, Oriental thuja and hazelnut appeared in early February. Japanese cedar showed the highest pollen concentration in March in Jeju. In conclusion, update information on pollen calendar in South Korea should be provided for allergic patients through the website to manage and prevent the pollinosis.

Entities:  

Keywords:  Allergens; pollen

Year:  2011        PMID: 22211164      PMCID: PMC3242062          DOI: 10.4168/aair.2012.4.1.5

Source DB:  PubMed          Journal:  Allergy Asthma Immunol Res        ISSN: 2092-7355            Impact factor:   5.764


INTRODUCTION

Allergic diseases related to pollen grains are called pollinoses and include allergic rhinitis, allergic conjunctivitis, asthma, and atopic dermatitis. Recently, numerous studies of allergic plants have been conducted in the United States and Europe, and the resulting information about allergic plants has been provided to allergy patients and the general public.1-3 Bostöck reported that pollen grains may cause diseases in humans.4 In the United States and Europe, epidemiological studies of airborne pollens have been continuously performed since the 1960s,5,6 and close relationships between pollens and allergic or pulmonary diseases have been reported since 1980. Information about clinical skin test reactions to various pollen grains has recently been provided to allergic patients and the general public through a website. In Korea, allergic pollen grains were studied in the early 1980s.7 Recently, the frequency of pollinosis, including allergic rhinitis, has increased in children, and many studies have investigated the relationships between the concentrations of allergic pollens and the clinical manifestations of allergic diseases.8 Thus, there is a necessity for pollen forecasting or a pollen calendar for Korea in order to prevent or reduce the prevalence of pollinosis.9-11 Pollen grains are produced by various plants, but not all pollen grains cause allergic diseases. Plants can be classified as anemophilous or entomophilous according to their pollination process. Entomophilous flowers produce heavy pollen grains that are transported by insects, so these pollens are produced in small amounts and rarely cause allergic diseases. In particular, entomophilous pollens have clinical implications in cases involving gardeners or horticulturists. In contrast, because light anemophilons pollen grains are transmitted by the wind, they are produced in large amounts. These grains are associated with allergic diseases because they contain special apparatuses, such as air sacs, and can travel great distances in the air. The size of pollen grains is closely related to the development of allergic diseases, and most of the pollen grains which can induce allergic diseases have sizes of 20 to 60 µm.12 Because the diameter of bronchioles is 3 to 5 µm, pollen grains with diameters smaller than 5 µm can reach the bronchioles. Asthma induced by pollens may be explained by the mechanism in which aeroallergens are inhaled, mix with sputum, and adhere to the respiratory mucosa. Another plausible mechanism is that some grains dissolve in airway mucus before being swallowed and entering the gastrointestinal tract.1-18

Collection and identification of pollen grains

The distribution of airborne pollen grains was assessed daily at eight locations nationwide between July 1, 1997 and June 30, 2009. A Burkard 7-day sampler (Burkard Manufacturing Co Ltd, Hertfordshire, UK) was installed at a height of 1.5 meters above sea level. The pollen collection areas were (1) Hanyang University Seoul Hospital and Seoul Meteorological Station in the Seoul metropolitan area, (2) Hanyang University Guri Hospital in the north-central region of South Korea, (3) Kangneung Asan Hospital and (4) Kangwon National University Chuncheon Hospital in the north-east, (5) Daejeon Meteorological Station in the central, (6) Kwangju Veterans Hospital and (7) Jeonju Jesus Hospital in the south-west, (8) Daegu Fatima Hospital in the south-east, (9) Busan St. Maria Hospital and (10) Ulsan Dongkang University in the far south-east, and (11) Jeju University Hospital on Jeju Island, the most distant of the southern islands (Fig. 1). Airborne pollens were collected every day from all samplers at all collection sites. The samples were sent every week to Hanyang University Guri Hospital, which was responsible for determining pollen concentrations. After each glycerin adhesive plastic was stained with Calberla's fuchsin staining solution (glycerin 10 mL, 95% alcohol 20 mL, distilled water 30 mL, and basic fuchsin 0.2 mL), the number of pollen grains per m3 was calculated at a magnification of ×400.19 Pollens were morphologically identified and classified by their size, color, pore shape, and surface pattern, with reference to the distribution of nationwide allergy-related plants such as trees, grasses, and weeds.20 Weather conditions on each collection day were recorded throughout the collection period and their associations with pollen distribution were assessed.
Fig. 1

The eight pollen collection stations in South Korea used in this study.

Classification of pollens that cause allergic disease in Korea

Trees

Gymnosperms

Cypresses: The pollen size ranges from 20 to 30 µm. This pollen appears from the middle of February and is well known to induce allergic rhinitis. Juniper, cypress, and cedar belong to the Cypresses. Pinus: The pollen ranges in size from 45 to 65 µm. This pollen has two sacs, and it rarely causes allergic diseases. Pines and spruces belong to Pinus (Fig. 2A).
Fig. 2

Common allergic pollens that cause pollinosis in Korea. (A) Pine, (B) alder, (C),hazel, (D) birch, (E) oak, (F) willow, (G) mugwort, (H) ragweed, and (I) pigweed.

Angiosperms

Most allergenic trees belong to this group. Betulaceae: This pollen appears in late February (early spring) and has a strong potential to induce allergic diseases. The pollen size ranges in size from 20 to 30 µm. This pollen has three pores and a thin exine. Alder (Fig. 2B), hazelnut (Fig. 2C), and birch (Fig. 2D) belong to this family. Fagaceae: This is an insect-borne pollen. This pollen appears in late March and is a representative of those allergens that induce pollinosis. It has a diameter of approximately 40 µm and has an irregular exine and three characteristic furrows. Beech and oak (Fig. 2E) belong to this family. Salicaceae: Most of the Salicaceae pollens are insect-borne, although poplar is airborne. This pollen has a strong allergenicity. It has a diameter of 20 to 34 µm and has a thick intine. It appears between May and June. It has many pistils and stamens, which do not usually induce allergic diseases, although they sometimes induce contact hypersensitivity reactions. Willow (Fig. 2F) and poplar belong to this family. Ulmaceae: This pollen induces pollinosis between May and June. It has a diameter of 30 to 40 µm and has five furrows and a thick, wave-like exine.

Grasses

Grasses related to allergic diseases belong to the order Graminales. Their pollen has a diameter of 20 to 25 µm and has one pore or furrow and a relatively thick intine. These pollens are airborne between the end of April and November, and have a strong allergenicity, partly because these plants are cultivated in densely-populated areas, leading to a high prevalence of pollinosis. Tens of different species are found in Korea. Although individual pollens are difficult to discriminate by light microscopy, this has no clinical implications because they cause similar allergic reactions. Korean lawn grass, timothy grass, Bermuda grass, and orchard grass are frequently found in Korea.

Weeds

Weeds are not usually cultivated and are distributed on the roadside or in creeks near the homes of many people. These pollens become airborne in late summer and are the main cause of pollinosis in the autumn. Asteraceae: These are most commonly found in Korea during the autumn. Sagebrushes (Artemisia) and ragweeds (Ambrosia) are representative pollinosis-causing weeds. Tribe Asteraceae: This pollen has a diameter of 20 to 30 µm and has three furrows and a relatively thick exine. This is the main plant that causes pollinosis in the autumn (Fig. 2G). Tribe Ambrosiae: This is a common cause of pollinosis in the autumn. It was imported from the United States in 1970, and became an important allergic pollen in the early 1980s. It is currently reported as a representative pollinosis-causing pollen nationwide. Ambrosia trifida (giant ragweed) and Ambrosia integrifolia, which has a stalk of 1-2.5 m, as well as Ambrosia artemisiifolia (short ragweed), which has a stalk of approximately 1 m, are representative of this species. This pollen has a diameter of 15 to 20 µm and has a multiple-thorned, ball-shaped, thick exine (Fig. 2H). Amaranthaceae and Chenopodiaceae: After mugwort and ragweed, these are the most frequently detected pollens. They are important causes of autumn pollinosis. They have a golf ball-like appearance, which allows for easy identification, and have a diameter of 20 to 30 µm. It is difficult to discriminate between these two families using light microscopy, so they are designated as Chenopod-Amaranth in airborne pollen surveys (Fig. 2I). Cannabaceae: This long-lived plant family includes voluble, diclinous, and annual plants and blossoms between August and September. It grows nationwide in fields, empty lots, and near creeks. It is found ubiquitously in embankments and apartment walls in cities and their suburbs. It grows wild in the Seoul metropolitan area where it is an important cause of autumn pollinosis. Japanese hop belongs to this family.

Characteristics of pollen distribution in Korea

Pollens are spores derived from stamens and can be divided into trees, grasses, and weeds. In Korea, allergenic pollens appear at temperatures ≥10℃ between February and November. The peak seasons are spring and fall; thereafter concentrations of these pollens decrease abruptly. Tree pollens are mainly observed between March and May, grass pollens between May and September, and weed pollens between August and October. Trees include pine, oak, alder, and birch, of which pine accounts for 70% of all tree pollens. Grass pollens are difficult to discriminate from other pollens using light microscopy; detailed classification of these species can be accomplished using electron microscopy. Japanese hop, mugwort and ragweed belong to this family.

Pollen concentrations and weather conditions

Pollen concentrations are closely related to general weather conditions, such as temperature and rainfall. Temperature and rainfall are particularly important determinants of pollen concentration. Pollens are heavily concentrated at 10-30℃, which is the most suitable temperature for plant growth (Fig. 3). High concentrations of pollen occur on days without rainfall. More pollen grains are airborne when the atmospheric temperature rises immediately after rainfall.
Fig. 3

Correlation between allergic pollen concentrations and air temperature. Pollens were collected at air temperatures ≥10℃.

Climate changes and increased pollen concentrations

Since the 1900s, remarkable climate changes have occurred due to rapid industrialization. Atmospheric temperature has increased due to the greenhouse effect secondary to the increased atmospheric CO2 concentration. Weather conditions, including CO2 concentration, rainfall, atmospheric temperature, humidity, wind speed, and wind direction may alter the concentrations of plant pollens and other allergens, which can subsequently influence the occurrence of asthma or allergic rhinitis. Many studies have demonstrated that CO2 concentration and increased atmospheric temperature increase pollen concentration. Ziska et al.21,22 reported that the atmosphere contains high levels of CO2 concentration due to rapid industrialization. They also predicted that pollen levels would rise due to increased CO2 concentration. Previous studies have demonstrated a significant relationship between pollen level and elevated atmospheric temperatures, and that pollen concentrations are higher in cities that have both a high atmospheric temperature and a high CO2 concentration than rural areas.23,24

Climate changes and pollen characteristics

A characteristic of climate change is that flowers blossom earlier and fall later, subsequently extending the duration of pollen production. For this reason, the annual amount of pollen has increased. It is well known that the distribution of plants, as well as the allergenicity of their pollen, have continuously changed. When subjects are sensitized to airborne pollens and are exposed to increased air pollution, allergic disease activity increases and clinical symptoms are aggravated. Such changes represent a serious global public health concern. To minimize the occurrence of clinical manifestations in allergic patients, a pollen calendar for Korea was developed between 1997 and 2002 (Fig. 4). However, because this calendar was based on the mean concentration of pollen nationwide, it did not reflect the regional characteristics of pollens and may be inaccurate due to recent changes in the climate. Therefore, it was necessary to develop a new calendar that included the geographic and monthly distribution of pollens and included data obtained after 2004.25 The old calendars were also modified by deleting data that did not match the dates of pollen distribution as reported in previous research.
Fig. 4

A calendar of allergic pollen used nationwide since 2004 which uses pollen data collected from 1997-2002.

Pollen calendar

A new pollen calendar was developed based on the pollen concentration data obtained in the eight locations listed above between 1997 and 2009. Briefly, pine was the most common source of tree pollens. Overall, tree pollens were detected at higher concentrations than grass or weed pollens. Pine, alder, oak, and birch produced higher pollen concentrations between April and May. Japanese cedar and common sorrel produced higher concentrations of pollens on Jeju, which is isolated from the mainland of the Korean Peninsula. In terms of regional variation, alder, birch, cedars, and oriental thuja began to produce pollens in February, after which their concentrations increased. In Seoul and Guri, pine pollen concentration was very high in May, when the concentrations of oak and birch pollen were also high. Common ragweed appeared at 5/m3/day in the middle of July; its concentration was highest in the middle of September. Japanese hop pollen levels were highest between the middle of August and the end of September. Mugwort pollen appeared in the middle of August and its concentration increased up until early September (Fig. 5). Birch pollen appeared earlier (early February) in Kangneung than in the other areas; pine pollen also appeared at higher concentrations in Kangneung than in other areas (Fig. 6). However there is not enough data to make a pollen calendar in Chuncheon because pollens were collected since 2010. In the Daegu area, oriental thuja, alder, and juniper produced a large amount of pollens in March. Pine produced a large amount of pollen between the middle of April and the end of May. Weed pollen concentrations were higher in September as in the other areas, and mugwort pollen was produced earlier than common ragweed pollen (Fig. 7). In Busan, flowering occurred relatively early, and alder and oriental thuja pollens appeared here before they did in other areas (early February) (Fig. 8). However there is not enough data to make a pollen calendar in Ulsan because pollens were collected since 2010. In Daejeon, birch and alder produced pollens earlier than in the other areas. Pine pollen was present at high levels between the beginning of April and the end of May (Fig. 9). In the Kwangju, oriental thuja and hazelnut pollens appeared in early February (Fig. 10). But there is not enough data to make a calendar in Jeonju because pollens were collected since 2009. In the Jeju area, Japanese cedar pollen appeared at higher concentrations than in other areas in March and peaked between the middle of February and March. Additionally, common sorrel pollen appeared at high levels between May and June. These results reflect the characteristics of Jeju (Fig. 11).
Fig. 5

An allergic pollen calendar for Seoul and Guri.

Fig. 6

An allergic pollen calendar for Kangneung.

Fig. 7

An allergic pollen calendar for Daegu.

Fig. 8

An allergic pollen calendar for Busan.

Fig. 9

An allergic pollen calendar for Daejeon.

Fig. 10

An allergic pollen calendar for Kwangju.

Fig. 11

An allergic pollen calendar for Jeju.

In conclusion, the pollen calendar in South Korea made between 1997 and 2002 does not reflect current pollen distribution and concentrations, because these have been altered by changes in the weather and environment. Therefore, updated information on pollen distribution and concentration in each region should be provided to the general public and allergy patients through a website in order to manage and prevent pollinosis.
  11 in total

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Journal:  Acta Allergol       Date:  1973-07

3.  Allergenic airborne pollen and spores in Anchorage, Alaska.

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Journal:  Ann Allergy       Date:  1985-05

4.  Cities as harbingers of climate change: common ragweed, urbanization, and public health.

Authors:  Lewis H Ziska; Dennis E Gebhard; David A Frenz; Shaun Faulkner; Benjamin D Singer; James G Straka
Journal:  J Allergy Clin Immunol       Date:  2003-02       Impact factor: 10.793

5.  Allergy epidemiology in the St. Louis, Missouri, area: II grasses.

Authors:  W H Lewis; W E Imber
Journal:  Ann Allergy       Date:  1975-07

6.  Production of allergenic pollen by ragweed (Ambrosia artemisiifolia L.) is increased in CO2-enriched atmospheres.

Authors:  Peter Wayne; Susannah Foster; John Connolly; Fakhri Bazzaz; Paul Epstein
Journal:  Ann Allergy Asthma Immunol       Date:  2002-03       Impact factor: 6.347

7.  Clinical characteristics according to sensitized allergens in adult korean patients with bronchial asthma.

Authors:  Jae Woo Jung; Jae Chol Choi; Jong Wook Shin; Jae Yeol Kim; In Won Park; Byoung Whui Choi
Journal:  Allergy Asthma Immunol Res       Date:  2010-03-24       Impact factor: 5.764

8.  The pathophysiology, diagnosis and treatment of allergic rhinitis.

Authors:  Yang-Gi Min
Journal:  Allergy Asthma Immunol Res       Date:  2010-03-24       Impact factor: 5.764

9.  Immunochemical quantitation of airborne short ragweed, Alternaria, antigen E, and Alt-I allergens: a two-year prospective study.

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Journal:  J Allergy Clin Immunol       Date:  1983-07       Impact factor: 10.793

10.  Allergen carriage by atmospheric aerosol. I. Ragweed pollen determinants in smaller micronic fractions.

Authors:  W R Solomon; H A Burge; M L Muilenberg
Journal:  J Allergy Clin Immunol       Date:  1983-11       Impact factor: 10.793

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2.  A glossary for biometeorology.

Authors:  Simon N Gosling; Erin K Bryce; P Grady Dixon; Katharina M A Gabriel; Elaine Y Gosling; Jonathan M Hanes; David M Hondula; Liang Liang; Priscilla Ayleen Bustos Mac Lean; Stefan Muthers; Sheila Tavares Nascimento; Martina Petralli; Jennifer K Vanos; Eva R Wanka
Journal:  Int J Biometeorol       Date:  2014-02-19       Impact factor: 3.787

3.  A biology-driven receptor model for daily pollen allergy risk in Korea based on Weibull probability density function.

Authors:  Kyu Rang Kim; Mijin Kim; Ho-Seong Choe; Mae Ja Han; Hye-Rim Lee; Jae-Won Oh; Baek-Jo Kim
Journal:  Int J Biometeorol       Date:  2016-07-07       Impact factor: 3.787

4.  Does the increase in ambient CO2 concentration elevate allergy risks posed by oak pollen?

Authors:  Kyu Rang Kim; Jae-Won Oh; Su-Young Woo; Yun Am Seo; Young-Jin Choi; Hyun Seok Kim; Wi Young Lee; Baek-Jo Kim
Journal:  Int J Biometeorol       Date:  2018-05-10       Impact factor: 3.787

5.  Meteorological conditions, climate change, new emerging factors, and asthma and related allergic disorders. A statement of the World Allergy Organization.

Authors:  Gennaro D'Amato; Stephen T Holgate; Ruby Pawankar; Dennis K Ledford; Lorenzo Cecchi; Mona Al-Ahmad; Fatma Al-Enezi; Saleh Al-Muhsen; Ignacio Ansotegui; Carlos E Baena-Cagnani; David J Baker; Hasan Bayram; Karl Christian Bergmann; Louis-Philippe Boulet; Jeroen T M Buters; Maria D'Amato; Sofia Dorsano; Jeroen Douwes; Sarah Elise Finlay; Donata Garrasi; Maximiliano Gómez; Tari Haahtela; Rabih Halwani; Youssouf Hassani; Basam Mahboub; Guy Marks; Paola Michelozzi; Marcello Montagni; Carlos Nunes; Jay Jae-Won Oh; Todor A Popov; Jay Portnoy; Erminia Ridolo; Nelson Rosário; Menachem Rottem; Mario Sánchez-Borges; Elopy Sibanda; Juan José Sienra-Monge; Carolina Vitale; Isabella Annesi-Maesano
Journal:  World Allergy Organ J       Date:  2015-07-14       Impact factor: 4.084

6.  Ratio of leukotriene e(4) to exhaled nitric oxide and the therapeutic response in children with exercise-induced bronchoconstriction.

Authors:  Hey-Sung Baek; Juhwan Cho; Joo-Hwa Kim; Jae-Won Oh; Ha-Baik Lee
Journal:  Allergy Asthma Immunol Res       Date:  2012-10-10       Impact factor: 5.764

7.  Changes in sensitization rate to weed allergens in children with increased weeds pollen counts in Seoul metropolitan area.

Authors:  Joo-Hwa Kim; Jae-Won Oh; Ha-Baik Lee; Seong-Won Kim; Im-Joo Kang; Myung-Hee Kook; Bong-Seong Kim; Kang-Seo Park; Hey-Sung Baek; Kyu-Rang Kim; Young-Jean Choi
Journal:  J Korean Med Sci       Date:  2012-03-21       Impact factor: 2.153

8.  Bee Pollen-Induced Anaphylaxis: A Case Report and Literature Review.

Authors:  Jeong Hee Choi; Young Sook Jang; Jae Won Oh; Cheol Hong Kim; In Gyu Hyun
Journal:  Allergy Asthma Immunol Res       Date:  2014-10-15       Impact factor: 5.764

9.  Seasonal variation in skin sensitivity to aeroallergens.

Authors:  Inseon S Choi; Seung-Sin Lee; Eun Myeong; Jeong-Won Lee; Woo-Jin Kim; Joon Jin
Journal:  Allergy Asthma Immunol Res       Date:  2013-08-07       Impact factor: 5.764

10.  The allergenic potency of Japanese hop pollen is increasing with environmental changes in Korea.

Authors:  Hyun Jung Jin; Gil Soon Choi; Yoo-Seob Shin; Joo-Hee Kim; Jeong-Eun Kim; Young-Min Ye; Hae-Sim Park
Journal:  Allergy Asthma Immunol Res       Date:  2013-07-19       Impact factor: 5.764

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