• 沒有找到結果。

We used Burkard seven-day volumetric spore trap to monitor daily ambient fungal

spores in Taipei from January to December during 2015, and investigate the distributions

and characteristics of ambient fungal spores. We found the temporal distribution of fungal

spores in Taipei. Concentration of fungal spores were affected by the meteorological

parameters and air pollutants. In summer, the higher temperature and humidity, the higher

level in concentration. While there were the heavy rainfall and strong wind, the

concentration decreased. Most air pollutants bind with fungal spores. When the

concentration of pollutants were higher, it found higher concentration of fungal spores.

This study is baseline of concentration of ambient fungal spores in Taipei. Further study

can utilize it to investigate the health outcome.

Reference

Adhikari A, Reponen T, Grinshpun SA, Martuzevicius D , LeMasters G : Correlation of

ambient inhalable bioaerosols with particulate matter and ozone: A two-year study.

Environmental Pollution 140 (2006) 16e28

Almaguer M & Aira MJ & Rodríguez-Rajo FJ & Rojas TI : Temporal dynamics of

airborne fungi in Havana (Cuba) during dry and rainy seasons: influence of

meteorological parameters. Int J Biometeorol (2014) 58:1459–1470

Babich H and Stotzky G : Influence of pH on inhibition of Bacteria, Fungi, and

Coliphages by Bisulfite and Sulfite. Environmental research 15, 405-417 (1978)

Boundless (2016). Boundless Biology. Retrieved from

https://www.boundless.com/biology/textbooks/boundless-biology-textbook/fungi-24/characteristics-of-fungi-149/fungi-reproduction-591-11810/

Burch M ·Levetin E : Effects of meteorological conditions on spore plumes. Int J

Biometeorol (2002) 46:107–117

Burge HA and Rogers CA : Outdoor Allergens. Environmental Health Perspectives Vol

108, Supplement 4 (2000).

Chao HJ & Chan CC & Rao CY & Lee CT & Chuang YC & Chiu YH & Hsu HH & Wu

YH : The effects of transported Asian dust on the composition and concentration of

ambient fungi in Taiwan. Int J Biometeorol (2012) 56:211–219

Chao, HJ; Lee, MF : Characteristics and health impacts of ambient bioparticles in

Northern Taiwan (2013)

Favero-Longo SE, Sandrone S , Matteucci E , Appolonia L , Piervittori R : Spores of

lichen-forming fungi in the mycoaerosol and their relationships with climate factors.

Science of the Total Environment 466–467 (2014) 26–33

Carris, LM, Little CR, and Stiles CM : Introduction to Fungi. 2012. The Plant Health

Instructor. DOI:10.1094/PHI-I-2012-0426-01. Retrieved from

http://www.apsnet.org/edcenter/intropp/pathogengroups/pages/introfungi.aspx

Centers for Disease Control and Prevention : Fungal diseases. 2016

Grinn-Gofron A. : Airborne Aspergillus and Penicillium in the atmosphere

of Szczecin, (Poland) (2004–2009). Aerobiologia (2011) 27:67–76

Grinn-Gofroń A & Strzelczak A : The effects of meteorological factors on the

occurrence of Ganoderma sp. spores in the air. Int J Biometeorol (2011) 55:235–241

Dadachova E, Bryan RA , Huang X, Moadel T , Schweitzer AD , Aisen P , Nosanchuk

JD, Casadevall A : Ionizing Radiation Changes the Electronic Properties of Melanin and

Enhances the Growth of Melanized Fungi. PLoS ONE, 2007 | Issue 5 | e457

Grinn-Gofron´ A •Bosiacka B : Effects of meteorological factors on the composition of

selected fungal spores in the air. Aerobiologia (2015)

Ho HM, Rao CY, Hsu HH, Chiuc YH, Liud CM, Chao HJ : Characteristics and

determinants of ambient fungal spores in Hualien, Taiwan. Atmospheric Environment

39 (2005) 5839–5850

Jones AM, Roy M. Harrison. : The effects of meteorological factors on atmospheric

bioaerosol concentrations—a review. Science of the Total Environment 326 (2004) 151–

180

Kochar S, Ahlawat M, Dahiya P.,and Chaudhary D.: Assessment of allergenicity to

fungal allergens of Rohtak city, Haryana, India. Allergy Rhinol (2014)

Kasprzyk I . Kaszewski BM . Weryszko-Chmielewska E . Nowak M . Sulborska A

Kaczmarek J . Szymanska A . Haratym W . Jedryczka M : Warm and dry weather

accelerates and elongates Cladosporium spore seasons in Poland. Aerobiologia (2016)

32:109–126

Li, D.-W. : Release and dispersal of basidiospores from Amanita muscaria var. alba and

their infiltration to a residence. Mycol. Res. 109:1235-1242 (2005).

Levetin E, Horner WE, and Scott JA, ARMCCM : Taxonomy of Allergenic Fungi. 2016

American Academy of Allergy, Asthma & Immunology (J Allergy Clin Immunol Pract

(2016)

Moore D : fungus. (2016). In Encyclopædia Britannica. Retrieved from

https://global.britannica.com/science/fungus

Murdoch LE, Mckenzie K, Maclean M, Macgregor SJ, Anderson JG : Lethal effects of

high-intensity violet 405-nm light on Saccharomyces cerevisiae, Candida albicans, and

on dormant and germinating spores of Aspergillus niger. Fungal biology 117 (2013) 519

e527

Newsham K, Frankland JC, Boddy L and Ineson P : Effects of dry-deposited sulphur

dioxide on fungal decomposition of angiosperm tree leaf litter I. Changes in

communities of fungal saprotrophs. New Phytol. (1992), 122, 97-110

Oh SY, Fong JJ, Park MS, Chang L, and Lim YW : Identifying Airborne Fungi in Seoul,

Korea Using Metagenomics. Journal of Microbiology (2014) Vol. 52, No. 6, pp. 465–

472

Rodríguez-Rajo FJ, Iglesias I and Jato V : Variation assessment of airborne Alternaria

and Cladosporium spores at different bioclimatical conditions. Mycol. Res. 109 (4):

497–507 (April 2005).

Stennett PJ ·Beggs PJ : Alternaria spores in the atmosphere of Sydney, Australia,

and relationships with meteorological factors. Int J Biometeorol (2004) 49:98–105

Sousa SIV, Martins FG, Pereira MC, Alvim-Ferraz MCM, Ribeiro H,

Oliveira M, Abreu I : Influence of atmospheric ozone, PM10 and meteorological factors

on the concentration of airborne pollen and fungal spores. Atmospheric Environment 42

(2008) 7452–7464

Sivasakthivel S, Nandini. N : Seasonal Distribution of Ambient Fungal Spore in

Bengaluru, Karnataka, India. 2015 IJSRSET | Volume 1 | Issue 4 |

Tiedemann AV , Firsching KH : Interactive effects of elevated ozone and carbon dioxide

on growth and yield of leaf rust-infected versus non-infected wheat. Environmental

Pollution 108 (2000) 357±363

Tosi S . Onofri ES. Brusoni EM . Zucconi EL. Vishniac H : Response of Antarctic soil

fungal assemblages to experimental warming and reduction of UV radiation. Polar Biol

(2005) 28: 470–482

University of Sydney. : FUNGAL BIOLOGY .2004. Retrieved from

http://bugs.bio.usyd.edu.au/learning/resources/Mycology/contents.shtml

Wu PC, Tsai JC, Li FC, Lung SC, Su HJ : Increased levels of ambient fungal spores in

Taiwan are associated with dust events from China. Atmospheric Environment 38

(2004) 4879–4886

Wiley J & Hoboken : Sampling and analysis of indoor microorganisms (2007).

Table 1a. Descriptive statistics for ambient fungal concentrations (#/M3) in Taipei in 2015. (N=309)

Fungal categories Freq(%) Mean Median SD Min Max IQR

Total spores 100.00 4448.08 2838.89 4187.03 155.56 18950.56 5281.11 Ascospores 100.00 1850.47 1170.56 1890.24 31.11 9601.67 2080.56 Aspergillus/Penicillium 100.00 372.62 221.67 432.04 11.67 4281.67 423.89 Basidiospores 99.68 1500.68 758.33 1747.74 0.00 8458.33 2080.56 Cladosporium 99.68 529.19 326.67 589.07 0.00 3780.00 544.44

Drechslera/Helminthosporium 11.00 0.79 0.00 3.77 0.00 50.56 0.00

Peronospora 9.71 0.94 0.00 4.47 0.00 58.33 0.00

Freq-frequency; SD-standard deviation; Min-minimum; Max-maximum; IQR-inter-quartile range

*Frequency was the percentage of samples (total n=309) with presence of that specific fungal category.

Table 1b. Descriptive statistics for environmental parameters in Taipei in 2015. (N=309)

Variables Mean Median SD Min Max IQR

Temperature (°C) 23.86 24.80 5.38 11.30 32.20 9.50

Td (°C) 19.15 20.80 5.18 5.10 25.40 8.20

RH (%) 75.76 76.00 7.57 51.00 93.00 12.00

WS (m/s) 2.30 2.10 1.20 0.50 9.60 1.80

Rainfall (mm) 7.58 0.00 25.58 0.00 306.70 4.00

Solar radiation (MJ/m2) 12.51 12.80 7.43 0.00 27.81 12.88

CO (ppm) 0.53 0.49 0.17 0.13 1.21 0.22

NO2 (ppb) 19.49 18.90 5.64 2.38 41.38 6.23

O3(ppb) 25.19 25.10 7.80 6.86 55.13 9.38

PM2.5 (μg/ m3) 17.08 14.58 11.26 0.00 68.91 11.14

PM2.5-10 (μg/ m3) 27.61 27.33 7.57 -5.04 57.04 8.12

SO2 (ppb) 2.87 2.66 1.28 1.09 9.88 1.42

SD-standard deviation; Min-minimum; Max-maximum; IQR-inter-quartile range

Table 2 Spearman’s correlation coefficients between the concentrations of major ambient fungal spores and environmental parameters in 2015.

Variables Ascospores Aspergillus/Penicillium Arthrinium Basidiospores Cladosporium Smuts Total spores

Temperature (°C) 0.748*** 0.737*** 0.339*** 0.784*** 0.423*** 0.701*** 0.789***

Td (°C) 0.789*** 0.726*** 0.285*** 0.787*** 0.371*** 0.680*** 0.799***

RH (%) 0.049 -0.183** -0.298*** -0.066 -0.218*** -0.183* -0.068

WS (m/s) -0.483*** -0.429*** -0.320*** -0.523*** -0.493*** -0.411*** -0.554***

Rainfall (mm) 0.142* -0.069 -0.254*** -0.095 -0.273*** -0.133* -0.028

Solar radiation (MJ/m2) 0.430*** 0.506*** 0.338*** 0.529*** 0.462*** 0.488*** 0.534***

CO (ppm) 0.186** 0.135* 0.283*** 0.218*** 0.390*** 0.157** 0.263***

NO2 (ppb) 0.090 0.015 0.145* 0.132* 0.268*** 0.020 0.150**

O3(ppb) -0.251*** -0.189*** -0.175** -0.222*** -0.174** -0.188** -0.259***

PM2.5 (μg/ m3) -0.093 -0.086 0.208*** -0.051 0.330*** 0.053 -0.007

PM2.5-10 (μg/ m3) 0.014 0.201*** 0.242*** 0.137* 0.218*** 0.226*** 0.128*

SO2 (ppb) 0.143* 0.216*** 0.253*** 0.291*** 0.440*** 0.273*** 0.277***

*p<0.05; **P<0.01; ***P<0.001

Note: Temp-temperature ; Td-dew point temperature ; RH-relative humidity ; WS-wind speed ; O3-ozone ; CO-carbon monoxide;SO2-sulfur dioxide;NO2

-nitrogen dioxide

Table 3 Multiple regression for major fungal spores and 0- , 1- and 2-day-lag 0-day-lag WS*** -0.072 (-0.104, -0.040)

0-day-lag Solar radiation*** 0.007 (0.002, 0.011) 0-day-lag CO*** 0.322 (0.107, 0.538) Ascospores

0-day-lag Td*** 0.068 (0.062, 0.075) 0.680 0-day-lag WS*** -0.088 (-0.115, -0.060)

Aspergillus/Penicillium

0-day-lag Temp*** 0.041 (0.029, 0.054) 0.582 0-day-lag WS*** -0.072 (-0.105, -0.039)

2-day-lag Td*** 0.023 (0.011, 0.036) 0-day-lag PM2.5-10*** 0.009 (0.004, 0.014) Arthrinium

0-day-lag Temp*** 0.024 (0.015, 0.033) 0.309 0-day-lag RH*** -0.022 (-0.029, -0.016)

0-day-lag CO*** 0.916 (0.622, 1.210) 1-day-lag O3*** -0.015 (-0.021, -0.008) Basidiospores

0-day-lag Td*** 0.122 (0.113, 0.131) 0.752 1-day-lag WS*** -0.091 (-0.129, -0.052)

2-day-lag RH*** 0.016 (0.010, 0.021) 0-day-lag NO2*** 0.024 (0.016, 0.032) 0-day-lag O3*** 0.017 (0.011, 0.023) Cladosporium

0-day-lag WS*** -0.154 (-0.194, -0.113) 0.332 0-day-lag Solar radiation*** 0.020 (0.013, 0.026)

0-day-lag PM2.5-10*** 0.012 (0.006, 0.018) Smuts

0-day-lag Temp*** 0.067 (0.059, 0.078) 0.579 0-day-lag WS*** -0.076 (-0.112, -0.040)

2-day-lag Rainfall*** -0.002 (-0.004, -0.001) 0-day-lag PM2.5-10*** 0.011 (0.006, 0.017)

**P<0.01; ***P<0.001

Note: Temp-temperature ; Td-dew point temperature ; RH-relative humidity ;

WS-wind speed ; O3-ozone ; CO-carbon monoxide;SO2-sulfur dioxide;NO2-nitrogen

dioxide

Figure 1. Temporal trend for daily concentration of total spores (spore m-3) in Taipei during 2015.

0 2000 4000 6000 8000 10000 12000 14000 16000 18000 20000

2015/1/8 2015/2/8 2015/3/8 2015/4/8 2015/5/8 2015/6/8 2015/7/8 2015/8/8 2015/9/8 2015/10/8 2015/11/8 2015/12/8 Fungal spores conc. (spore m-3)

Day

Total spores

Figure 1a. Temporal trend for monthly concentration of Ascospores, Aspergillus/Penicillium, Basidiospores, Cladosporium (spore m-3) in Taipei

Figure 1b. Temporal trend for monthly concentration of Smuts, Arthrinium, Nigrospora, Periconia (spore m-3) in Taipei during 2015.

-50

Figure 1c. Temporal trend for monthly concentration of Curvularia, Bortrytis, Torula (spore m-3) in Taipei during 2015.

-5

Figure 2. Monthly averages of meteorological parameters (Temperature, Dew point temperature, Wind speed, Relative humidity) in Taipei

Figure 3. Monthly averages of meteorological parameters (Solar radiation, Rainfall) in Taipei during 2015.

0 10 20 30 40

mm

Month

Rainfall

0 5 10 15 20 25

MJ/m2

Month

Solar radiation

Figure 4. Monthly averages of air pollutants (CO, NO2, O3, SO2, PM2.5, PM2.5-10) in

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