RESEARCH ARTICLE / ARAŞTIRMA MAKALESİ



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ANADOLU ÜNİVERSİTESİ BİLİM VE TEKNOLOJİ DERGİSİ ANADOLU UNIVERSITY JOURNAL OF SCIENCE AND TECHNOLOGY Cilt/Vol.:7-Sayı/No: 2 : 357-362 (2006) RESEARCH ARTICLE / ARAŞTIRMA MAKALESİ SEASONAL VARIATIONS IN AIRBORNE CLADOSPORIUM AND ALTERNARIA SPP. CONIDIA IN ESKİŞEHİR Kıymet GÜVEN 1, Tuncay SÖYLEMEZ 2 ABSTRACT The conidia of allergenic Cladosporium and Alternaria spp. were counted by using a Durham sampler at five sampling points during one year and the relationship between the numbers of conidia and meteorological data was investigated. The conidia of these fungi were present in the air of Eskişehir-Anatolia throughout the year. Temperature favoured conidial release for both species of Cladosporium and Alternaria. Rain precipitation was negatively correlated with conidial numbers of Cladosporium and Alternaria while no significant correlation was obtained with wind velocity. Keywords: Cladosporium and Alternaria, Conidia, Seasonal variations ESKİŞEHİR HAVASINDAKİ CLADOSPORIUM VE ALTERNARIA SPP. KONİDİALARININ MEVSİMSEL DEĞİŞİMİ ÖZ Allerjenik Cladosporium ve Alternaria spp. konidiası beş farklı örnekleme noktasında 1 yıl boyunca Durham örnekleyicisi kullanılarak sayılmış ve konidia sayıları ile meterolojik veriler arasındaki ilişki araştırılmıştır. Eskişehir havasında bu funguslara ait konidia yıl boyunca mevcut olarak tesbit edilmiştir. Sıcaklığın hem Cladosporium hem de Alternaria spp. türlerinin konidial salınımını arttırdığı saptanmıştır. Yağmur ile Cladosporium ve Alternaria spp. konidia sayısı arasında negatif etkileşim gözlenirken, rüzgar ile konidia sayıları arasında dikkate değer bir ilişki saptanamamıştır. Anahtar Kelimeler: Cladosporium ve Alternaria, Konidia, Mevsimsel değişim 1, Department of Biology, Faculty of Science, Anadolu University TR-26470 Eskişehir-Turkey. Fax: +90 222 3353616, e-mail: kguven@anadolu.edu.tr 2, Samsun Milli Eğitim Müdürlüğü. Recieved: 24 December 2004; Revised(I): 31 August 2005; Revised(II): 10 February 2006; Accepted: 27 March 2006

358 1. INTRODUCTION Airborne fungal conidia are important and of considerable economic significance because many species are pathogenic and can cause some diseases in humans, animals and plants. It has been known that inhalation of the conidia of moulds produce numerous allergies (Palmas and Cosentino, 1990). The species present and their concentrations in the air are dependent on several factors: geographical location, time of day, temperature, relative humidity, rainfall, wind velocity, seasonal climate factors, type of vegetation and human activities. Many investigations have been carried out on the airospora in many parts of the world (Abdel-Hafez and El-Said, 1989; Li and Kendrick, 1994; Lyon et al., 1984; Nussbaum, 1991, Çolakoğlu, 1996 a, b, c; Şen and Asan, 2001, Al-Subai, 2002) In most aerobiological surveys, Cladosporium and Alternaria spp. have been reported to form the majority of airborne conidia in the temperate zones. They live as saprophytes or as parasites on many kinds of plants (Hjelmroos, 1993). Eskişehir is an Anatolian city. Its altitude is 720 m and it has dry summers and cold winters. Rainfall occurs mainly in the springs. The city has a steppe vegetation and it is surrounded by agricultural areas producing cereals, chiefly wheat and barley. Because of its prevalent agricultural economy represents a particularly favourable environment for mould growth and dispersal. Atik and Tamer (1994) first studied the airborne microbial flora in Eskişehir by sedimentation method and they recorded that Penicillium spp., Cladosporium spp., Aspergillus spp., Alternaria spp., were the most prevalent fungi. Harmancı et al., (2000) examined 105 asthma patients living in Eskişehir using skin tests. They reported that Cladosporium and Alternaria spp. were common allergens. Therefore, this study was designed to give basic information on the seasonal variation of Cladosporium and Alternaria spp. in Eskişehir. 2. MATERIALS AND METHODS 2.1 Study area The study was performed over a 12-month period, from February 1999 to January 2000 at five sampling points in the city of Eskişehir. Two of the sampling sites were located in the center of the city, and three were in its rural regions. 2.2 Sampling Method Durham or gravity slide samplers (Ogden et al., 1974) was used in five sampling point to trap the conidia. The traps were installed 1.5 m above the ground level. The slides were coated with glycerinjelly and then positioned on the samplers. The slides were removed from the samplers at weekly intervals. The numbers of conidia of the Cladosporium and Alternaria spp. were counted under a light microscope. Identification of the conidia was based on microscopic Anadolu Üniversitesi Bilim ve Teknoloji Dergisi, 7(2) morphology, using the mycologic literature (Hasenekoğlu, 1991a,b). Weekly conidial counts/cm 2 were converted to montly mean values for each sampling site and then a mean Cladosporium and Alternaria spp. conidial numbers were determined. Daily meteorological data were obtained from the city s Meteorological Office and the meteorological data were processed as montly averages. 2.3 Statistical Analysis Regression analysis was made by Statview, by using Cladosporium and Alternaria conidial counts and weather variables (mean temperature, mean wind velocity and mean precipitation) recorded at the time of sampling. 3. RESULTS AND DISCUSSION Our survey revealed that both the Cladosporium and Alternaria spp. were present in the air of Eskişehir throughout the year. Table 1 gives the montly average number of conidia. The conidia of the Cladosporium spp. appeared were dominant through out the year. Table 1. Monthly average conidial numbers (conidia/cm 2 ) of the Cladosporium and Alternaria spp. Months Conidial Number (conidia/cm 2 ) Cladosporium spp. Alternaria spp. February 1999 119 111 March 220 206 April 453 341 May 612 423 June 942 614 July 813 563 August 663 568 September 584 497 October 574 455 November 436 308 December 444 246 January 2000 310 195 The maximum average temperature (C o ) was recorded in June and July while the minimum average temperature was in December and January. The average precipitation (mm) was highest in January and lowest in Aprily and the summer months. The wind velocity (m/s) was high in May and June and was the lowest in September (Figure 1-a). The number of conidia increased in parallel with temperature and the wind velocity. The peak values for both Cladosporium and Alternaria spp. were found in June and July. Rain precipitation was high in February and March but the Cladosporium and Alternaria conidial numbers were lower (Figure 1-b). The smallest conidial counts for both the Cladosporium and Alternaria spp. were recorded in February 1999 although the precipitation had the highest value (Figure 1-a).

Anadolu University Journal of Science and Technology, 7 (2) 359 a o Average Temparature ( C), Average Precipitation (mm), Average Wind-Velacity (m/s ) 25 20 15 10 5 0-5 -10 January February March April May June July August September October November December Average Temparature Average Precipitation Average Wind-velacity Months b spore/cm2 1000 900 800 700 600 500 400 300 200 Cladosporium Alternaria 100 0 January February March April May June July August September October November December Months Figure 1. Comparison of conidial numbers of Cladosporium and Alternaria spp.and the meteorological data for one year ( a) meteorological data b) conidial numbers). Coefficients of determination (r 2, F and p) calculated for conidial deposits of Cladosporium and Alternaria against the meteorological variables (mean temperature, mean wind velocity and mean precipitation) are shown in Table 2. Average temperature was significantly correlated with the concentrations of Cladosporium and Alternaria conidia. Average precipitation was negatively correlated with the conidial numbers of Cladosporium and Alternaria while no significant correlation was obtained between the average wind velocity and the conidial numbers. When comparing results of aerobiological surveys, the difference in methods being applied by various authors leads to problems in the interpretation of results. Many different types of conidial traps have been used, each with its specific advantages and disadvantages (Ebner and Haselwandter, 1989). The Durham sampler has been one of the standards recommended by the American Academy of Allergy for many years (Ogden et al., 1974).

360 Anadolu Üniversitesi Bilim ve Teknoloji Dergisi, 7(2) Table 2. Statistical determinants obtained in regression analysis of conidial concentration data against meteorological data. Regression Coefficient Constant Determinative Coefficients A 1 A 0 r 2 F p Wind-Alternaria 36,95 254,86 0.02 0.21 0.654 Temp.- Alternaria 22.87 110.22 0.92 119.72 0.0001* Precip.- Alternaria -149.41 513.66 0.50 10.16 0.0097* Wind-Cladosporium 81.04 245.66 0.503 0.52 0.4836 Temp.- Cladosporium 29.53 169.36 0.76 33.35 0.0002* Precip.- Cladosporium -219.63 714.61 0.54 11.96 0.0061* *the level of significance=0.05. Wind:average wind velocity, Temp.:average temperature, Precip.: average precipitation Lyon et al. (1984) studied the vertical variation of airconidial concentrations in the atmosphere and found that Cladosporium conidial numbers were significantly more than at the 9 or 30 m heights while the Alternaria spp. did not exhibit a correspondingly larger number. In our study we placed the Durham samplers at the 1.5 m level which is an average nose level. Many surveys of the occurrence of Cladosporium spores in different regions of the world clearly show their dominance in comparison with other spores (Tamer et al., 1994; Çolakoğlu, 1996 b; Şimşekli et al., 1997; Stepalska et al., 1999; Şen and Asan, 2001; Al-Subai, 2002). The conidia of the Cladosporium spp. appeared were dominant through out the year in our survey in agreement with above studies. Fungal airoconidia are known to incite respiratory allergic reactions in sensitized indiviuals. The most common moulds implicated in fungal allergies include Cladosporium, Alternaria, Aspergillus, Helminthosporium, Epicoccum, Fusarium, Penicillium, Geotrichum, Rhizopus, Mucor and numerous ascomycete and basidiomycete. The species of these genera are among the most common and most cosmopolitan contributors to airoconidia. Therefore, understanding the microenvironments that produce these moulds, noting their diurnal periodicities, and becoming aware of weather conditions that promote their abundance may assist patients and clinicians in their attempts to lessen the severity of respiratory allergies (Nussbaum, 1991). Cladosporium species live, like those of Alternaria, as saprophytes or as parasites on many kinds of plants. Species of Cladosporium and Alternaria are considered to be the most prevalent of aeroallergens (Çolakoğlu, 1996 b). Alternaria spp. are often found growing together with Cladosporium spp. (Ebner and Haselwandter, 1989; Hjelmroos, 1993). Cladosporium conidia was the most frequent airborne conidia at low altitudes (582-827 m) of alpine sites. Alternaria conidia were also present in the air throughout the year. We also recorded both Cladosporium and Alternaria throughout the year. Meteorological conditions clearly have profound influences on the production, dispersal and deposition of fungal conidia. Rain, wind speed, wind direction, humidity temperature and flora and fauna in the testing area are among the major factors that affect the concentration of airborne fungal conidia. The influence of meteorological factors on the airborne fungal conidial concentration appears to be additive and not independent (Li and Kendrick, 1994). Low temperatures were found to depress conidium release in Cladosporium and Alternaria spp. (Halwagy, 1989; Li and Kendrick, 1994). It was reported that winter in temperate and cold regions is a dormant season for most fungi. We also found maximum conidial counts of both moulds at high temperatures in the summer months. Various factors, such as the type of collection medium, the identification process, the period of the day in which the collection of fungi takes place, the sampling frequency and duration influence the airborne fungi monitoring (Takahashi, 1997). However, we are in agreement with Atik (1993) who recorded that Cladosporium spp. was the most prevalent in summer months in Eskişehir by sedimentation method. The effect of rain on airborne conidial concentrations can be simultaneously positive and negative, and is related more on droplet size and droplet frequency than amounts (Stephen and Dowding, 1990). We found that precipitation was significantly negatively correlated with conidial counts of Cladosporium and Alternaria spp. in Eskişehir. Similar findings were reported in Sanluri, Italy (Palmas and Cosentino, 1990). Wind is the most unpredictible agent in the dispersal of fungal conidia and Cladosporium and Alternaria conidia are released by wind (Li and Kendrick, 1994). We, however did not find any significant correlation between wind velocity and conidial numbers. This preliminary study gives the information that Cladosporium and Alternaria spp. were present in the air of Eskişehir throughout the year giving peaks in June and the summer months. A long term study involving different sampling techniques should be carried out to provide a detailed conidial calender for the allergy sufferers in this area.

Anadolu University Journal of Science and Technology, 7 (2) 361 REFERENCES Abdel-Hafez, S. I. I. & El-Said, A. H. M. (1989). Seasonal variations of airborne fungi in Wadi Qena, Eastern Desert, Egypt. Grana 28, 193-203. Al-Subai, A. A. T. (2002). Air-borne fungi at Doha, Qatar. Aerobiologia 18, 175-183. Atik, S. (1993). Eskişehir Merkez İlçesinde Hava Kirliliği. Yüksek Lisans Tezi. Anadolu Üniversitesi Fen Bilimleri Enstitüsü, s. 76, Eskişehir. Atik S. & Tamer, A. Ü. (1994). Eskişehir merkez ilçede mikrobiyal hava kirliliği. Ege Üniv. Fen Fak. Dergisi Seri B, 16, 227-238. Çolakoğlu, G. (1996 a). Fungal spore concentrations in the atmosphere at the Anatolia quarter of Istanbul, Turkey. J. Basic Microbiol. 36, 155-162. Çolakoğlu, G. (1996 b). Mould counts in the atmosphere at the Europe quarter of Istanbul, Turkey. J. Basic Microbiol. 36, 389-392. Çolakoğlu, G. (1996 c). The variability of fungal flora in the air during morning and evening in 1994. J. Basic Microbiol. 36, 393-398. Ebner, M. R. & Haselwandter, K. (1989). Seasonal fluctations of airborne fungal allergens.mycol. Res. 92(2), 170-176. Halwagy, M. H. (1989). Seasonal airspora at three sites in Kuwait 1977-1982. Mycol. Res. 93, 208-213. Harmancı, E., Metintaş, M. & Erginel, S. (2000). L Allergie Respiratoire Aux Moisissures Chez Les Adultes En Eskişehir (Anatolie), Turquie. Allergie et Immunologie. XXXII-2, 49-51 Hasenekoğlu, İ. (1991a). Cladosporium. In:Toprak Mikrofungusları Cilt II., Atatürk Üniversitesi Yayınları No:689. Kazım Karabekir Eğitim Fakültesi Yayınları No:11, Erzurum, ss. 339-374. Hasenekoğlu, İ. (1991b). Alternaria. In:Toprak Mikrofungusları Cilt I., Atatürk Üniversitesi Yayınları No:689. Kazım Karabekir Eğitim Fakültesi Yayınları No:11, Erzurum, 104-151. Li, D. & Kendrick, B. (1994). Functional relationships between airborne fungal spores and environmental factors in Kitchener-Waterloo, Ontario, as detected by Canonical correspondance analysis. Grana 33, 166-176. Lyon, F. L., Kramer, C. L. & Eversmeyer, M. G. (1984). Vertical variation of airspora concentrations in the atmosphere. Grana 23, 123-125. Nussbaum, F. (1991). Variation in the airborne fungal spore population of the Tuscarawas Valley II. Mycopathol. 116, 181-198. Ogden, E. C., Raynor, G. S., Hayes, J. V., Lewis, D. M. & Haines, J. H. (1974). Manual for sampling airborne pollen, p.180. Hafner Press, NewYork. Palmas, F. & Cosentino, S. (1990). Comparison between fungal airspore concentration at two different sites in the south of Sardinia. Grana 29, 87-95. Stepalska, D., Harmata, K., Kaspryzk, I., Myszkowska, D. and Stach, A. (1999). Occurrence of airborne Cladosporium and Alternaria spores in Southern and Central Poland in 1995-1996. Aerobiologia 15, 39-47. Stephen, E. R. & Dowding, A. E. (1990).Forecasting spore concentrations: A time series approach. Int. J. Biometeorol. 34, 87-89. Şen, B. & Asan, A. (2001). Airborne fungi in vegetable growing areas of Edirne, Turkey. Aerobiologia 17, 69-75. Şimşekli, Y., Gücin, F., Dülger, B. and Sapan, N. (1997). Bursa evdışı havasında bulunan fungal sporlar. Tr. J. Biology 21, 359-365. Takahashi T. 1997. Airborne fungal colony-forming units in outdoor and indoor environments in Yokohama, Japan. Mycopathol., 139, 23-33. Tamer, A. Ü., Ay, G. and Şahin, N. (1994). Manisa (merkez ilçe) atmosferindeki bazı allerjen fungus sporlarının belirlenmesi (1990-1991). XII. Ulusal Biyoloji Kongresi (6-8 Temmuz 1994). Botanik Seksiyonu, Cilt: I, ss. 291-295. Hjelmroos, M. (1993). Relationships between airborne fungal spore presence and weather variables Cladosporium and Alternaria. Grana 32, 40-47.

362 Anadolu Üniversitesi Bilim ve Teknoloji Dergisi, 7(2) Kıymet Güven, Anadolu Üniversitesi, Fen-Edebiyat Fakültesi, Biyoloji Bölümü nden 1986 yılında mezun oldu. 1988 yılında yüksek lisansını tamamladı. Doktorasını mikrobiyoloji alanında East Anglia Üniversitesi (İngiltere) 1992 yılında bitirdi. 2000 yılında doçent, 2005 yılında ise profesör ünvanını aldı. Tuncay Söylemez, Dumlupınar Üniversitesi, Fen-Edebiyat Fakültesi, Biyoloji Bölümünden 1998 yılında mezun oldu. Yüksek Lisansını Anadolu Üniversitesi Fen Bilimleri Enstitüsü nde 2001 yılında tamamladı. 2005 yılına dek Bitlis Milli Eğitim Müdürlüğü ne bağlı olarak öğretmenlik yaptı. Görevine Samsun Milli Eğitim Müdürlüğü nde devam etmektedir.