Diversity of Aeromycoflora at Different Environmental Heights
Ajay Singh1*, Ragini Tiwari1, Prakriti
Singh1, Vinay Sagar
Verma2, Mukesh Sharma2,
Amit
Alexander2, Ajazuddin2
1GD Rungta College of Science and
Technology, Kurud, Bhilai
(Chhattisgarh) India
2Rungta College of Pharmaceutical Sciences and Research, Kurud, Bhilai (Chhattisgarh)
India
*Corresponding Author E-mail: mukesh.rcpsr@gmail.com
ABSTRACT:
An aeromycological study to identify and quantify
allergenic fungi and their fluctuations
was conducted at Bhilai city. The diversity of the aeromycoflora at different height in this study, based on
the recovery of fungal propagules by the air-exposing-PDA
plating method was conducted in rainy season. The study showed that the most
prevalent (major components) fungal spores in the air on different heights
(0-10feet,10-20and 20-40feets) in kohka-
Bhilai city were Aspergillus spp.
Alternaria spp. Curvularia spp.
Rhizopus spp. Penecillin spp. fusarium spp.
The abundant genera on different heights were Curvularia, Aspergillus, Alternaria. Curvularia spp. Aspergillus spp. were the most abundant fungal spore
type collected throughout the period of study on different height in kohka-bhilai
city.
KEYWORDS: Aeromycoflora, Allergenic fungi, Aspergillus , Alternaria, Curvularia.
INTRODUCTION:
Aerobiology is a
scientific discipline which deals with the studies of organisms or part of the
organisms present in the air. The term "aerobiology" came in the use
during 1930's as collective and other microorganisms. Aerobiological
investigations have been carried out with special reference to diseases on
crops, vegetable, fruits and human etc. Meir (1930) was the first aerobiologists who used the term aerobiology for the
studies of airborne fungal spores, pollen grains and other microorganisms.
Jacobs (1951) elaborated the term aerobiology for dispersion of fungal spores,
bacteria, insects and pollen grains population which become airborne and
transported partly or wholly by the environment and their impact on all life
belonging forms. Airborne fungi are considered to act as indicator of the level
of atmospheric bio-pollution. (Ianovici N,TudoricaD,2009) The fungal spores are liberated in air from
various sources in massive concentration and can remain airborne for a
longtime. Fungal spores are important source of various plants and animals
diseases. Airborne fungal spores are ubiquitous in nature (Burge, 1985). Much of
our knowledge on the behavior of airborne spores comes from various studies on the epidemiology of plants animals and human diseases, especially infections of the
respiratory tract and allergy (Comtois, 1990; Angulo-Romero et al., 1996). More than 80 genera of
fungi have been associated with respiratory tract allergy (Karlsson-Borga
et al., 1989; Horner et al., 1995).
Most of the
allergenic fungi are classified under Ascomycetes and
Deuteromycetes with a few in Basidiomycetes
(Kurup et al., 2000). Some genera of airborne
fungal spores such as Alternaria, Aspergillus, and Cladosporium
are found throughout the world (Vijay et al., 1999). The disease
expression is affected by the degree of exposure. Repeated exposures to large
concentrations of spores, mostly 1–5 μm in
diameter, may cause severe symptoms of respiratory allergy (Barui
Chandra and Chanda, 2000). The prevalence of
respiratory allergy to fungi is estimated at 20 to 30% among atopic
individuals and up to 6% in general population (Wuethrich,
1989). It is of the most importance that allergens, viable microbes, and other
noxious agents that prevail in any particular environment, or are induced by
changes in meteorologic conditions, be identified and
studied. These measures will not only help to monitor the levels of these
agents in the environment but also aid clinicians in advising and treating
patients as well as those at risk before they are exposed and sensitized (Zwick et al., 1991). Most of the researches have
dealt with fungi already settled on the rock surface and/or with “autochtonous mycoflora” (Saiz-Jimenez, 1995). Fungal airspora
are implicated in the damage of food commodities and in the deterioration of
organic materials and stored products (Pyrri and Kapsanaki-Gotsi, 2007).The presence of fungal propagules, volatiles and mycotoxins
in the air can cause a health hazard in all segments of the population (Kakde et al., 2001) Airborne fungi occur as single units,
spores and occasionally as hyphal fragments,
conidiophores, associated with inorganic particles or as “bioaerosol”
(Comtois, 1990). Number and type of fungi vary with
time of day, weather and seasonal fluctuation, condition of the surrounding
areas, climatic conditions and with the presence of a local source of spores (Pepeljnjak and Šegvić Klarić, 2003). The distribution of airborne fungi in
Europe may differ from that in North America and Japan because of differences
in climate, vegetation, and the structure of houses (Takahashi,
1997).Aerobiological investigations and survey of different outdoor environment
would provide significant and useful data. Sabariejo et.al (2000) reported the effect of meterological factors on the daily variation of the
airborne fungal spores in Granada, Southern Spain. Kulshreshta
and Chauhan (2000) studied aeromycoflora
of Agar city. Kakade et al. (2001) studied seasonal variation of fungal propegules in a fruit market environment Nagpur, India.
Singh and Singh (2009) observed incidence of airborne fungal spores in the air
of Ima market, Imphal West,
Manipur. The examination of common airborne fungi distribution in a particular
region can be helpful in: identifying association between fungal sensitisation and clinical diagnosis; and clinical
prevention of the seasonal allergic diseases (Wu et al.,
2000).Therefore, the purpose of our study was to determine variations in the
composition and concentration of the aeromycoflora in
Kohka-Bhilai on different heights.
MATERIALS
AND METHODS:
a) Sampling
Concentrations
of airborne fungal spores were measured from 7 August to 7 September (rainy
season) 2013S
using air-exposing-PDA plating method. Bhilai the
famous Steel –industry city and education center of Durg
District in the state of Chhattisgarh, India. The fungi to be
identified is collected from the different heights (ground level, middle
level and top level).
b) Isolation and
Identification
For isolation of
aeromycoflora, PDA culture media was used. Aaeromycoflora of the hostel building of GD Rungta College of Science and Technology Kohka –Bhilai was observed
by exposition petriplate containing PDA medium.
Then the petriplates
was brought in to laboratory and incubated at 270 c for 4 to 5 days.
This method also used by Tiwari et al. (2007) for survey of aeromycolfora.
At the end of incubation period fungal colonies are counted, isolated and
identified with the help of available literature and the percentage frequency
and percentage contribution of total fungal flora were assessed.
RESULTS AND
DISCUSSION:
The occurrence
of aeromycoflora in outdoor and indoor environments
as well as the fluctuations in their numbers and composition is receiving
increasingly attention within the framework of potential health hazards to both
flora and fauna, including humans. Airborne fungi have also been implicated as
the causal factor in various human diseases and as elicitors of allergic and/or
toxic responses. Great concern has been expressed about potential health
hazards to humans, with a special focus on allergenic or toxigenic
fungi and their association with air quality (Horner et al., 1995). The
objectives of the present study are to record the airborne fungi in an urban
environment during the rainy season using modern aerobiological sampling
technique. Measurements were made in August to September of 2012 because most
reports showed that higher concentrations of airborne fungi were recorded
during the rainy at different heights.
In
various percentages of fungi in outdoor air at different heights in the present
study are reported. The airborne fungal genera are listed in Table (1, 2 and 3)
as descending order based on their frequencies, which were calculated as
positive samples in the total number of samples. Airborne fungi were grouped
into “major” and “minor” components depending upon their frequency of appearance
and catch percentage in the air. Curvularia sp., Aspergillus sp. were included
as major components at each level. Minor components included two airborne
fungal genera found at middle and top level. Major components included most
frequently encountered genera such as Curvularia sp. while minor components included
less frequent and sporadic types. Curvularia sp., Aspergillus sp. Alternaria, Rhizopus, Penecillin, Fusarium, type
spores were trapped most frequently at different heights. Percentage frequency
of Curvularia spores was higher than
the Aspergillus
at ground level but at middle and top level Curvularia spores
percentage frequency moderate form and Percentage distribution varies
from Curvularia to other at different heights.
Our results
show the presence of a large number of fungal spore types at ground level. The
monitoring of fungal spores in Bhilai revealed the
rainy the most favorable season for curvularia and Aspergillus occurrence., Curvularia sp. (Ground
Floor), Aspergillus
sp. (Meddle Floor) Alternaria, (Topfloor) Rhizopus, Penecillin, Fusarium type
spores were trapped in greatest abundance. These represent a group of taxa of cosmopolitan fungi that can exploit virtually any
organic substrate (Ianovici, 2008).
The
genus Curvularia sp. Aspergillus
sp. predominated and it is
the most important genus in terms of defining variations in the total count.
The genus Alternaria is also a major
constituent of the fungal bioaerosol. The present study will contribute to our
knowledge of airborne spores in Bhilai at different
heights.
Observation Table
Table 1-Ground Floor (5 Feet)
|
S.No |
Species Name |
Percentage frequency |
Percentage contribution |
|
1 |
Aspergillus
sp.1 |
77.77 |
16.00 |
|
2 |
Aspergillus
sp.2 |
55.55 |
12.00 |
|
3 |
Aspergillus
sp.3 |
66.66 |
09.33 |
|
4 |
Aspergillus
sp.4 |
22.22 |
04.00 |
|
5 |
Curvularia
sp.1 |
88.88 |
13.33 |
|
6 |
Curvularia
sp.2 |
44.44 |
10.66 |
|
7 |
Curvularia
sp.3 |
11.11 |
02.66 |
|
8 |
Alternaria |
22.22 |
05.33 |
|
9 |
Rhizopus |
11.11 |
02.66 |
|
10 |
Penecillin |
33.33 |
06.66 |
|
11 |
Fusarium |
55.55 |
12.00 |
|
12 |
Others |
22.22 |
05.33 |
Graph 1:
Percentage frequency and Percentage Distribution at Ground Floor
Table 2-Middle Floor (15-20 Feet):
|
S.No |
Species Name |
Percentage frequency |
Percentage contribution |
|
1 |
Aspergillus
sp.1 |
77.77 |
17.39 |
|
2 |
Aspergillus
sp.2 |
33.33 |
06.52 |
|
3 |
Aspergillus
sp.3 |
22.22 |
08.69 |
|
4 |
Aspergillus
sp.4 |
00.00 |
00.00 |
|
5 |
Curvularia
sp.1 |
55.55 |
10.86 |
|
6 |
Curvularia
sp.2 |
44.44 |
13.04 |
|
7 |
Curvularia
sp.3 |
11.11 |
04.34 |
|
8 |
Alternaria |
22.22 |
08.69 |
|
9 |
Rhizopus |
11.11 |
02.17 |
|
10 |
Penecillin |
22.22 |
04.34 |
|
11 |
Fusarium |
66.66 |
17.39 |
|
12 |
Others |
44.44 |
06.52 |
Table 3-TOP Floor (40-45 Feet) :
|
S.No |
Species Name |
Percentage frequency |
Percentage contribution |
|
1 |
Aspergillus
sp.1 |
22.22 |
12.90 |
|
2 |
Aspergillus
sp.2 |
11.11 |
09.67 |
|
3 |
Aspergillus
sp.3 |
33.33 |
16.12 |
|
4 |
Aspergillus
sp.4 |
11.11 |
06.45 |
|
5 |
Curvularia
sp.1 |
22.22 |
12.90 |
|
6 |
Curvularia
sp.2 |
11.11 |
12.90 |
|
7 |
Curvularia
sp.3 |
11.11 |
09.67 |
|
8 |
Alternaria |
22.22 |
12.90 |
|
9 |
Rhizopus |
0.00 |
0.00 |
|
10 |
Penecillin |
11.11 |
03.22 |
|
11 |
Fusarium |
11.11 |
06.45 |
|
12 |
Others |
11.11 |
03.22 |
Graph
2: Percentage Frequency and Percentage Distribution at Middle Floor.
Graph 3: Percentage Frequency and Percentage Distribution at Top
Floor.
CONCLUSION:
Fungal
agents are responsible for a variety of respiratory and skin diseases in
humans, and animals. Aeromycoflora of different floor
environment in Kohka-Bhilai have been investigated. Spores of 75fungal
types were recorded from all different floor. The
spores of Curvularia sp. and Aspergillus
sp. were the largest contributors of the total airborne fungal
spores at each floor than Alternaria and Rhizopus. Curvularia sp. and Aspergillus was the most
prevalent fungal spore type during Aug-Sep. 2012 in the air samples from the
different floor in Kohka-Bhilai site. Monitoring of
airborne fungi can be helpful in prevention of fungal allergic diseases.
REFERENCE:
1.
Angulo-Romero, J., F. Infante-García-Pantaleon, E. Dominguez, M. Mediavilla-Molina and J. M. Caridad-Ocerín
(1996). Pathogenic and antigenic fungi in school dust of the south of Spain. p.
49-65, In: M. Muilenberg and H. Burge (Eds.).
Aerobiology. Lewis Publisher, New York.
2.
Burge, H. A.
(1985). Fungus allergens. Clin. Rev. Allergy 3:
319-329.
3.
Barui Chandra, N. and S. Chanda
(2000). Aeromycoflora in the Central Milk Dairy of
Calcutta, India, Aerobiologia 16: 367-372.
4.
Comtois, P. (1990). Indoor and mold aerosols. Aerobiologia 6: 165-176.
5.
Horner, W., E., A.
Helbling, J. E. Salvaggio
and S. B. Lehrer (1995). Fungal allergens. Clin. Microbiol. Rev. 8:161-179.
6.
Karlsson-Borga, A., P. Jonsson and W. Rolfsen (1989). Specific IgE
antibodies to 16 widespread mold genera in patients with suspected mold
allergy. Ann. Allergy 63:521-526.
7.
Kakde, U.
B., H. U. Kakde and A. A. Saoji
(2001). Seasonal variation of fungal propagules in a
fruit market environment, Nagpur (India). Aerobiologia,
17:177-182.
8.
Kulshrestha, A. and Chauhan, S. V. S.(2001). Aeromycoflora ofsome hospitals of Agra city. Indian J. Aerobiology. 14 (1and2):
P33-35.
9.
Kurup, V. P., B. Banerjee, K. J.
Kelly and J. N. Fink (2000). Molecular biology and immunology of fungal
allergens, Indian Journal of Clinical Biochemistry, 15(Suppl):31-42.
10.
Ianovici, N. (2008). Preliminary survey of airborne fungal
spores in urban environment, Scientific Conference “Durable Agriculture in the
context of Environmental changes”, University of Agricultural Sciences and
Veterinary Medicine, Faculty of Agriculture, Iasi, 16-18 October 2008.
11.
Ianovici N, Tudorica D, (2009) Aeromycoflora in Outdoor Environment of Timisoara City
(Romania) Notulae Scientia Biologicae 1
(1), 21-28.
12. Pepeljnjak, S. and M. Šegvić
Klarić (2003). Occurrence of fungi in air and on
plants in vegetation of different climatic regions in Croatia. Aerobiologia, 19:11-19.
13.
Pyrri, I.
and E. Kapsanaki-Gotsi (2007). A comparative study on
the airborne fungi in Athens, Greece, by viable and non-viable sampling
methods, Aerobiologia, 23:3-15.
14.
Saiz-Jimenez,
C. (1995). Microbial melanins in stone monuments.
Sci. Total Environ. 167:273-286.
15. Singh, Romesh Ksh and Singh Anilkumar N. 2009. Incidence
of airborne fungal spores in the air of Ima market (Khwairamb and Bazar), Imphal West, Manipur. Abstract, 15th Nat. Conf. on
Aerobiology and National Symposium on “Airspora-
Impact on Plant, Animal and Human Health”, M. U. Imphal.
16. APHC- 05: P16.
17. Takahashi, T. (1997). Airborne Fungal
Colony Forming Units in Outdoor and Indoor Environments in Yokohama, Japan, Mycopathologia 139:23–33.
18. Tiwari, K. L. and Saluja,
P. K.2007.Seasonal variation of aeromycoflora of Catharanthus roseus Linn.
Abstract 14th Nat. Conf. on Aerobiology, Pt. R. S. U. Raipur. A-1: P 5.
19.
Vijay,
H. M., A. J. Thaker, B. Banerjee
and V. P. Kurup (1999). Mold allergens. In: Allergens and Allergen
Immunotherapy, Eds. Lockey, R.F. and Bukantz S.C. Marcel Dekker, New York 133-154.
20.
Wuethrich,
B. (1989). Epidemiology of allergic diseases: Are they really on the increase.
Int. Arch. Allergy Appl. Immunol. 90:3-10.
21.
Wu, P.
C, H. J Su and C. Y. Lin (2000). Characteristics of indoor and outdoor airborne
fungi at suburban and urban homes in two seasons. Sci
Total Environ, 253:111-118.
22.
Zwick, H.,
W. Popp, S. Jager, C. Wagner, K. Reiser
and F. Horak (1991). Pollen sensitization and allergy
in children depend on the pollen load. Allergy:46:362-32.
Received on 27.11.2014
Accepted on 16.12.2014
© Asian Pharma
Press All Right Reserved
Asian J. Pharm. Tech.
2014; Vol. 4: Issue 4, Oct.-Dec., Pg 195-199