Occurrence of the Toxin-Producing Aspergillus versicolor Tiraboschi in Residential Buildings

Abstract

In an area representative of a moderate climate zone (Lubuskie Province in Poland), mycological tests in over 270 flats demonstrated the occurrence of 82 species of moulds. Aspergillus versicolor Tiraboschi was often encountered on building partitions (frequency 4: frequently). The ability to synthesize the carcinogenic sterigmatocystin (ST) means that it poses a risk to humans and animals. Biotoxicological tests of biomasses of A. versicolor were conducted in the Microbiological and Toxicological Laboratory, using the planarians Dugesia tigrina (Girard). The obtained results of the tests covered a broad range of toxicity levels of isolated strains: from weakly toxic (100–1000 mg·L⁻³) to potently toxic (1–10 mg·L⁻³). The high-performance liquid chromatography (HPLC) physicochemical method confirmed the ability of A. versicolor strains to synthesize sterigmatocystin. All of the samples of the air-dry biomasses of the fungi contained ST in the range between 0.03 and 534.38 mg·kg⁻¹. In the bio-safety level (BSL) classification A. versicolor belongs to category 1. Additionally, A. versicolor is an allergenic mould.

1. Introduction

The problem with the occurrence of moulds in buildings is not only the biodeterioration of technical materials, but also the deterioration of the sanitary condition of the indoor air [1,2]. This real risk to the health of residents of infected rooms occurs due to the ability of the majority of species of moulds to synthesize secondary metabolites—mycotoxins. The problem is known and has become more and more serious in recent years, not only in Poland [3,4,5,6]. Based on tests conducted in a residential environment, greatest attention is paid to the presence, development, and forecasting of the development of xero- and hydrophilic moulds, including mycotoxigenic ones, with such dangerous species as Aspergillus versicolor and Stachybotrys chartarum [7,8,9,10]. Bloom et al. [11] showed that several mycotoxins synthesized by S. chartarum (macrocyclic trichothecenes, trichodermin, and satratoxin G) and A. versicolor (sterigmatocystin) may be present in the majority of samples coming from the building materials of damp flats or from samples of settled dust.

Aspergillus versicolor is a saprotrophic fungus, which is widespread in nature. It is often present in soil (rotting plants, litter, straw, and the rhizosphere of many plants), on many rotting food products (cheese, peanuts, dry meat products, flour), and on cereals. It produces proteolytic enzymes and often appears on fats and their derivatives, as well as on bread. It also tolerates a very broad pH range, including an alkaline environment. The optimum temperature for its growth amounts to 20 °C–30 °C (min. 4 °C, max. 40 °C). Conidia germinate at temperatures between 12 °C–37 °C [12,13,14]. The fungus is pathogenic (BSL 1) and causes aspergillosis in pet animals [15]. Spores of A. versicolor are easily inhalable [16,17]. Their diameters range between 2 and 3.5 µm [14]. They are often detected in lung tissues during an autopsy [17].

Aspergillus versicolor is a primary coloniser capable of growing at a_w > 0.65–0.70 [14,18,19]. This causes this species to be one of the moulds which is most frequently found on building materials inside premises [20,21,22,23,24,25]. Additionally, it is frequently present in the air in substantial quantities. It colonises air-conditioning equipment and is present in the carpet dust of damp, confined premises. The mould often occurs (frequency 4) in buildings in the Lubuskie province [22], and its proven ability to synthesize sterigmatocystin on building materials was the reason for the initiation of the toxicological tests [10,26].

Aspergillus versicolor synthesises important toxic metabolites: 5–methoxysterigmatocystin and dihydroxy–sterigmatocystin, 5,6-dimethoxysterigmatocystin (with cytotoxic properties), averufin, deoxyaverufin, cyclopiazonic acid, nidulotoxin, versicolorin A, B, and C (cytotoxic, mutagenic, and teratogenic), versiconol (with low toxicity), and sterigmatocystin (ST) (ST is the precursor of AFB₁ and, just like aflatoxin, it is characterised by toxicity and carcinogenicity) [13,17,27,28,29,30]. ST in test animals causes liver necrosis at doses ranging between 18 and 100 mg·kg⁻¹ of body weight, and kidney damage at higher doses. Although sterigmatocystin may initiate liver cancer in rats and cause the development of tumours at the site of its administration, its carcinogenic effect is ten times smaller than that of AFB₁. The toxic effect is also smaller [17]. A. versicolor consistently produces carcinogenic sterigmatocystin on the majority of laboratory media. It synthesises substantial quantities of ST and 5 methoxy-sterigmatocystin on building materials [31]. The tests conducted on isolates of A. versicolor from the air inside the rooms proved that these strains produced ST in laboratory cultures, and the extracts of the cultures demonstrated cytotoxicity. It was determined that conidia of two strains of A. versicolor comprised 0.375 and 1.060 pg (10⁻¹² g) of ST in the spore [17]. In laboratory conditions, the strains isolated from the building materials and surface finishes from damp buildings produced ST on gypsum boards, chipboards, and especially large quantities on wall papers [32]. Other strains produced 5 methoxy-sterigmatocystin. The lethal concentrations (LC 50) of ST for shrimp larvae (Artemia salina) are 5.95 mg·L⁻³ and 0.54 mg·L⁻³ [33], respectively. The toxicity of ST for the test animals expressed in lethal doses (LD 50 in mg·kg⁻¹) amounts to: ducklings, 1.0; albino rats, 166 (males, p.o.); albino rats, 60 (males, i.p.); albino rats, 120 (females, p.o.); albino rats, 65 (females i.p.); male monkeys, 32 (i.p.) [34].

Volatile metabolites (MVOCs) produced by A. versicolor include 2-ethyl-1-hexanol, 1-octen-3-ol, 3-octanone, 2-heptanone, 2-pentanone, 2-hexanone, and 2-methylfuran. Isolates produce pronounced earthy volatiles [35].

2. Materials and Methods

The paper presents the results of research conducted for many years (more than 20 years), with regards to the occurrence of moulds in residential housing, as well as the assessment of potential risks (allergies, mycoses, mycotoxicoses) and real risks (synthesis of sterigmatocystin, Aspergillus versicolor, and also the results of biotests from extracts of A. versicolor biomasses), which indirectly confirm the health risk for people living in mouldy premises. The research was conducted in the area of the Lubuskie province in Poland. The area is representative of many buildings erected within the moderate climate zone. Collection of the big number of results (82 mould species, over 270 buildings) allowed the establishment of the frequency of occurrence of the respective taxons on building partitions, as well as the indication of 10 species which colonise walls most frequently. The results, after taking into consideration the potential risks gathered on the basis of many different published references, constituted the grounds for the selection of the species (out of 10 species on the list) for mycotoxicological tests (high-performance liquid chromatography (HPLC) and biotests). Aspergillus versicolor became our choice as it is often present in residential housing and consequently synthesises sterigmatocystin, which is a carcinogenic substance from category 2B (according to International Agency for Research of Cancer (IARC) [36]), on the walls.

Forty-five air-dry biomasses of A. versicolor obtained in laboratory cultures and coming from buildings were subjected to toxicity tests. The biotoxicological testing of methanol extracts from mould biomasses was carried out using Dugesia tigrina (Girard). Forty-five mould samples were analysed for the presence of sterigmatocystin (ST) in the Department of Pharmacology and Toxicology of the National Veterinary Research Institute in Puławy, using HPLC. Mycological and mycotoxicological tests have been carried out in the Microbiological and Toxicological Laboratory at the Department of Applied Ecology, Institute of Environmental Engineering, University of Zielona Góra (Poland).

2.1. Mycological Tests—Collection of Samples from Buildings, Method of Culturing Moulds

Moulds were collected in over 270 buildings from the inner surfaces of building partitions with visible mould. The partitions were made of plasterboard, bricks, and breeze blocks, and the finishing materials included plaster, acrylic paint, wallpaper, and others. The samples were collected directly at the site of occurrence and transferred onto Petri dishes, which contained such media as malt extract agar (MEA), Merck and Czapek–Dox (Cz), and Merck. Mycological analysis was performed in accordance with the methodology established by CBS (Centraalbureau voor Schimmelcultures) [14]. The direct plating method was used. According to this method, small fragments of the material infected with moulds are transferred or spread onto the Petri dishes containing the culture media [37]. The samples were incubated in a cultivation room, covered with white linen, at room temperature, between 18 °C and 22 °C, maintaining the circadian rhythm of day and night. Pure (axenic) cultures were isolated from mixed starter cultures by their passaging on the media: Cz and MEA. The time of plating, cultivation and observation for an isolated single species was 21 days [38,39]. The isolated strains were subjected to identification tests using keys for taxonomic identifiers: [12,14,15,19,26,40,41,42,43,44,45,46]. Bacteria grew out in the colonies and were not the subject of research.

2.2. Acarological Analysis—Collection of Samples from Buildings, Method of Culturing Mites

Samples of mites (Acari) were taken directly from the place where moulds were present onto surfaces with two media (Cz and MEA), using Petri dishes. Mites were mounted in a Hoyer medium on slides, and the species and life stages were determined with the aid of an Axioscope 2 Zeiss compound microscope (Carl Zeiss Inc., Oberkochen, Germany). Solarz [47] conducted acarological analysis in Department of Parasitology, Medical University of Silesia in Katowice, Sosnowiec, Poland.

2.3. Cultures of Aspergillus versicolor

Mass cultures of A. versicolor were established for biotoxicological and physicochemical testing of isolated strains. Five millilitres of MEA was poured out on ø 9 cm Petri dishes. The samples were incubated at temperature, between 18 °C and 22 °C, maintaining the circadian rhythm of day and night. The cultivation time for an isolated culture was three months. This is the time required for growth, sporulation, and regrowth until a large area of the Petri dish is covered, and also strain aging and drying of the mycelium with the medium to an air-dry state. According to Piontek [10], the method of the cultivation of the moulds constitutes the simulated environmental conditions prevailing in the various seasons of the year on building partitions in residential housing. The air-dry moulds with the media were collected from the dishes by means of a scalpel, then they were weighed and placed in glass jars closed with a ground stopper. The material prepared in this way served the purpose of the preparation of methanol extracts for biotoxicological tests, as well as test portions for chromatographic analyses with reference to the presence of sterigmatocystin.

2.4. Methanol Extracts for Biotoxicological Tests

In order to carry out 45 toxicity analyses of A. versicolor using D. tigrina as the test organism, methanol extracts from the culture of strains isolated in the residential housing were prepared. Mycotoxins were extracted from the mould biomass using the method developed by Piontek [10,38,39]. One-gram air-dry samples of mould biomass were extracted over 96 h in 100 cm³ of 80% methanol (analytical grade) before their filtration through Whatman 4 blotting paper placed on a filter flask. In the applied procedure, 1 mL of extract is obtained from 10.0 mg of sample (mould plus medium).

2.5. Biotoxicological Tests Using Dugesia Tigrina

The toxicity of 45 strains of A. versicolor isolated from flats was investigated. For all of them, toxicological tests using Dugesia tigrina were carried out. The obtained results were the basis for the calculations of a lethal concentration LC 50, (mg·L⁻³) for test organisms. The method of the cultivation of the planarians for toxicological tests was developed by Piontek [48]. The toxicological tests were performed in a laboratory at temperatures ranging between 18 °C and 22 °C. A series of concentrations was prepared. Test solutions with volumes of 40 cm³ were poured into beakers with capacities of 50 cm³. 10 cut specimens were introduced into each beaker [10,49,50,51,52]. The determinations were carried out in three repetitions including control tests. Thirty planarians were kept in each concentration of the toxicant. After 240 h, the mortality of the planarians was checked. The obtained results constituted the basis for the calculation of a lethal concentration (240 h LC 50). The graphic interpretation method (probit analysis) was used to calculate the value of the concentrations—LC 50. The obtained results were subjected to the test of compliance of experimental distribution with a normal distribution. The χ² test was used in the calculations. The tested distributions were considered sufficiently convergent with the normal distribution, if the likelihood in the χ² test was higher than 0.7 [53]. The obtained results of the biotoxicological tests of substances for the planarians were evaluated in terms of the degree of their toxicity based on the Liebmann classification [54] (see Table 1).

Table 1. Toxicity classes of poisonous substances [54].

Quantity of Poison—Result of Toxicity Test (mg·L−3)	Toxicity Classes	Classes
<1	highly toxic	I
1–10	potently toxic	II
10–100	medium toxic	III
100–1000	weakly toxic	IV
>1000	barely toxic	V

2.6. The Determination of Sterigmatocistin Concentration by HPLC

Forty-five air-dry biomasses of A. versicolor were tested in the Department of Pharmacology and Toxicology of the National Veterinary Research Institute in Puławy, using HPLC for the presence of sterigmatocystin (ST). The determination of the content of sterigmatocystin in fodder and mycelium was conducted by means of high-performance liquid chromatography (ZFT/PB/06-12/edition 1, date of issue 2011.04.28) [55]. A detailed description of the HPLC method is presented in the Piontek’s paper [38,39].

The toxicity of ST was evaluated based on the classification established by Chełkowski [13,33], (Table 2).

Table 2. Toxicity classes of mould biomasses [13,33].

Quantity of Important Mycotoxins—Result of Chromatographic Analysis (mg·kg−1)	Toxicity Classes
≤1 mg·kg−1	non toxic
>1–10 mg·kg−1	weakly toxic
>10–100 mg·kg−1	potently toxic
>100 mg·kg−1	highly toxic

3. Results

3.1. Results of Mycological Tests

In the mycological tests conducted in over 270 flats, 82 species of moulds (Table 3) were isolated from walls with visible mould.

Table 3. Species of moulds isolated from building partitions in the area of the Lubuskie Province.

Types and Species of Moulds		Frequency in Flats *
Absidia	corymbifera Sacc. et Trotter	1
	glauca Hagem	1
Acremonium	bacillisporum W. Gams	1
	charticola W. Gams	1
	murorum W. Gams	1
	strictum W. Gams	3
Alternaria	alternata Keissler	2
	tenuissima Wiltshire	1
Arthrinium	phaeospermum M.B. Ellis	1
Aspergillus	carbonarius Thom	1
	clavatus Desmazieres	1
	flavus Link	3
	fumigatus Fressenius	1
	niger van Tieghem	3
	terreus Thom	1
	ustus Thom et Church	2
	versicolor Tiraboschi	4
Aureobasidium	pullulans Arnaud	1
Beauveria	bassiana Vuillemin	1
Botrytis	cinerea Persoon ex Fries	1
Botryotrichum	piluliferum Sacc. et Marchal	1
Chaetomium	elongatum Czerepanova	2
	torulosum Bainier	1
Chromelosporium	sp.	1
Cladosporium	cladosporioides de Vries	2
	herbarum Link ex Gray	5
	macrocarpum Preuss	3
	sphaerospermum Penzig	1
Doratomyces	stemonitis Pers.	1
Epicoccum	nigrum Link	1
Fusarium	aquaeductum Lagerheim	1
	culmorum Saccardo	1
	equiseti Saccardo	1
	oxysporum Schlechtendal ex Fries	1
	sambucinum Fuckel	1
	solani Saccardo	1
	sporotrichioides Sherbakoff	1
	verticillioides Nirenberg	1
Geotrichum	candidum Link	1
Gilmaniella	humicola Barron	1
Humicola	brevis Gilman et Abbott	1
	fuscoatra Traaen	1
Monocillium	indicum S. B. Saksena	1
Moniliella	acetobutens Stolk & Dakin	1
Mucor	circinelloides van Tieghem	1
	globosus Fischer	1
	hiemalis Wehmer	1
	mucedo Fresenius	1
	piriformis Fischer	1
	plumbeus Bonorden	1
	racemosus Fresenius	5
Paecilomyces	farinosus Brown et Smith	1
	marquandii Hughes	1
	variotii Bainier	1
Penicillium	aurantiogriseum Dierckx	1
	brevicompactum Dierckx	1
	chrysogenum Thom	5
	expansum Link ex Gray	1
	funiculosum Thom	1
	glabrum Westling	1
	janthinellum Biourge	1
	lanosum Westling	3
	thomii Maire	1
	viridicatum Westling	1
	vulpinum Seifert et Samson	1
	waksmanii Zaleski	1
Phoma	glomerata (Corda) Wollenw.	1
Rhizomucor	pusillus Schipper	1
Rhizopus	stolonifer Lind.	2
Scopulariopsis	brevicaulis Bainier	1
	candida Vuill.	1
Stachybotrys	chartarum Hughes	1
Thamnidium	elegans Link	2
Trichoderma	koningii Oudemans	1
	viride Persoon ex Gray	2
Trichothecium	roseum Link ex Gray	2
Tritirachium	oryzae (Vincens) de Hoog	1
Ulocladium	botrytis Preuss	2
	chartarum Simmons	4
	consortiale Simmons	1
Verticillium	lecanii Viégas	1
	luteoalbum Subramanian	2

* Frequency in flats: >0%–5% (1, sporadically), >5%–10% (2, individually), >10%–15% (3, fairly frequently), >15%–20% (4, frequently), >20% (5, very frequently) according to Piontek [22].

The presence of two or more species of moulds in one sample was confirmed in reference to all of the tested samples. As well as the moulds, the presence of numerous bacteria and allergenic mites (Acari), belonging to Tyrophagus putrescentiae was found [10,47,56]. For isolated species of moulds the frequency of their occurrence on the building partitions was determined. Scale 1–5: >0%–5% (1, sporadically), >5%–10% (2, individually), >10%–15% (3, fairly frequently), >15%–20% (4, frequently), >20% (5, very frequently) according to Piontek [22].

The following species of moulds were present with the highest frequency: Cladosporium herbarum, Mucor racemosus, and Penicillium chrysogenum (frequency 5, very frequently). Two species were present frequently: Ulocladium chartarum and Aspergillus versicolor (frequency 4, frequently).

3.2. Toxicological (Biotoxicological and Physicochemical) Tests

The specification of the obtained results of physicochemical and biotoxicological tests is presented in Table 4.

Table 4. Specification of the results of toxicological tests from biomasses of A. versicolor.

No.	Quantity of ST (mg·kg−1)	Classification According to Chełkowski [13,33]	LC 50 for Dugesia tigrina (mg·L−3)	Classification According to Liebmann [54]
1	<0.03	non toxic	n.t *	class IV (weakly toxic)
2	<0.03		n.t
3	<0.03		n.t
4	0.07		n.t
5	1.28	weakly toxic	603
6	1.30		399
7	1.50		104.71
8	2.69		150
9	2.89		122
10	6.48		132
11	6.12		107
12	7.20		105
13	8.31		102
14	13.6	potently toxic	70.9	class III (medium toxic)
15	15.1		25.1
16	18.5		72.4
17	28.2		26.8
18	48.0		40.7
19	54.2		20.7
20	58.2		27.5
21	63.2		67.6
22	63.4		53.7
23	63.5		51.3
24	63.8		50.1
25	63.9		10.9
26	65.0		23.4
27	78.3		18.0
28	68.7		36.3
29	84.0		29.0
30	84.5		22.9
31	85.7		20.8
32	86.8		19.9
33	88.9		31.0
34	90.2		12.9
35	94.1		10.7
36	99.7		39.9
37	107	highly toxic	28.0
38	112		19.2
39	120		19.7
40	132		9.6	class II (potently toxic)
41	137		9.9
42	148		9.1
43	149		9.0
44	273		9.1
45	534		8.2

* n.t—non toxic.

As the obtained results of the biotoxicological tests indicate, 30% of the strains of A. versicolor were weakly toxic (Class IV, according to Liebmann’s classification), 26 strains (58%) belonged to Class III (medium toxic), for which the LC 50 ranged between 10 and 100 mg·L⁻³, and six strains (13%) were potently toxic (Class II). At the National Veterinary Research Institute in Puławy, the analysis was performed based on 45 biomasses of A. versicolor (Table 4). The quantity of sterigmatocystin contained in the tested biomasses ranged between 0.03 and 534 mg·kg⁻¹ (Table 4). D. tigrina turned out to be a sensitive bio-indicator for the presence of ST, which is confirmed by the quantity tests performed using the HPLC method. Nine tested biomasses demonstrated the presence of ST above 100 mg·kg⁻¹ (24%), which classifies these strains as very potently toxic, 51% of biomasses were potently toxic (the quantity of ST ranged between 13.6 and 99.7 mg·kg⁻¹). 20% of biomasses were weakly toxic, whereas four biomasses of A. versicolor with the quantity of sterigmatocystin below 1 mg·kg⁻¹ were non-toxic (n.t.).

4. Discussion

In the presented test results, as well as results presented by other authors in papers concerning this subject, it has been proved that the moulds synthesise mycotoxins (secondary metabolites) on building materials [21,27,31,32]. The more relevant ones for the selected species of moulds occurring with high frequency in the residential housing in the area of the Lubuskie province are listed in Table 5.

Table 5. Mycotoxins synthesised by selected moulds isolated from building partitions of analysed residential housing.

Species	Produced Mycotoxins [10,14,34] *
Aspergillus versicolor	cyclopiazonic acid, sterigmatocystin, 5–methoxysterigmatocystin, dihydroxy–sterigmatocystin, nidulotoxin, averufin, versiconol, versicolorin A, B, C
Penicillium chrysogenum	penicillic acid, rokefortin C, meleagrin, fusigen, xantocilin, 6–amino–penicillic acid, negapilin, penicillin G, sideramin, chryzogin

* The important toxic metabolites are specified in bold.

The risk of the release of mycotoxins may occur when spores and fragments of moulds, as well as particles containing mycotoxins such as dust or mouldy substances, are inhaled and swallowed. Therefore, the most important issue is to determine which, as well as how often and how many, mycotoxins are present naturally in mouldy building partitions in residential housing [10]. The toxigenicity trait of moulds is not a stable phenomenon [57]. It is a fact that certain species have mycotoxin-positive strains, and others do not have the ability to synthesise mycotoxins. Therefore, after the isolation of moulds from the building materials, they must be tested in terms of their ability to synthesise mycotoxins by performing an analysis of the biomasses of isolates obtained from laboratory culture on microbiological media [10,38,39].

A. versicolor is the main producer of carcinogenic sterigmatocystin with nephrotoxic, hepatocarcinogenic and immune-suppressive properties. The tests performed in the Microbiological and Toxicological Laboratory confirm that A. versicolor is a species of mould which may constitute a risk to residents of infected rooms. It is often present on the building partitions of buildings located in the areas representative of a moderate climate (Table 3). The toxicological tests for D. tigrina demonstrated the occurrence of potently toxic strains (13%), which means that the biological methods are applicable for the evaluation of the mycotoxic risk in buildings (Table 4). The various quantities of ST, including nine strains which produced more than 100 mg·kg⁻¹ of it (highly toxic strains according to Chełkowski) justifies the need to conduct research on this species. Chemical analysis unfriendly to the environment could be replaced by biological one. Physicochemical analysis (HPLC) should be conducted in the case of a high toxicity level of the sample.

Tests of dust from damp residential premises conducted in Germany demonstrated the occurrence of the species of mould called A. versicolor. The majority of the strains (98%) of A. versicolor isolated from the dust was able to synthesise ST in vitro [23]. Mycological tests conducted in Denmark show that the mould most frequently occurring on building partitions is Penicillium chrysogenum, and among Aspergillus, Aspergillus versicolor [17]. This fact is confirmed by tests conducted in this paper.

On the basis of the mycological tests performed, it is possible, based on literature on the subject, to determine the potential hazard for humans inside the infected rooms. In 1996, a list was drawn up under the auspices of the European Confederation of Medical Mycology, which specified the classification of biosafety levels (BSL) for the respective species of fungi (BSL 1/3) [15].

According to this list, it is possible to specify species of moulds occurring in residential housing, which are pathogenic for humans and animals and which were most frequently present on building partitions in the Lubuskie province (Table 6).

Table 6. Classification of biosafety levels of selected moulds potentially pathogenic for humans and animals [15].

Species of Mould	BSL *
Aspergillus versicolor	1
Cladosporium herbarum	1
Mucor racemosus	1
Penicillium chrysogenum	1
Ulocladium chartarum	1

* BSL1—infections are superficial, non-invasive or benign. * BSL2—in patients with severe immunological disorders, moulds can cause deep opportunistic infections. * BSL3—pathogens potentially capable of inducing severe deep fungal infections in apparently healthy people [15].

The isolated moulds, including A. versicolor, are classified into the BSL1 category. This means that infections which may be caused by these species are most frequently benign, superficial, and non-invasive. In the rooms subjected to the tests, the most threatening pathogens were not present on the walls (BSL 3).

Moulds are the cause of many allergic diseases [15,16,17,58,59]. Allergens of moulds congested in badly ventilated rooms constitute a real threat for people with atopy [60]. It is known that the spores of Aspergillus, Cladosporium, and Penicillium present in damp buildings may cause asthma and/or rhinitis among atopic residents. It has been proved that raw extracts including A. versicolor may cause the release of histamines without the mediation of IgE in human cells of the mucous membranes from lungs in vitro [32]. Allergic reactions may be caused both by the spores and the fragments of mycelium. They are caused mainly by proteins, components of walls of moulds (β-(1-3)-d-glucans), microbial volatile organic compounds (MVOC) and mycotoxins, as well as other organisms which occur together with the moulds, such as mites (Acari) [10,61,62]. The respiratory system allergies are caused mainly by Aspergillus and Penicillium [16,17].

Aspergillus versicolor may cause allergic diseases. Among 82 species of moulds occurring in residential housing in the Lubuskie province, the other allergenic fungi include: Penicillium chrysogenum, Aspergillus niger, Cladosporium herbarum, Alternaria alternata, and Aspergillus flavus. The moulds which may occur with lower frequency in buildings, but still may cause allergic diseases, include Penicillium glabrum, Aspergillus fumigatus, and Aureobasidium pullulans (present paper).

At present, the time of exposure and the concentration of mycotoxins which may have a negative impact on the human health of residents is not known [63]. However, the presence of the moulds on building partitions may not be tolerated. It is necessary to carry out defungusing work in such rooms after the prior performance of mycological tests and structural surveys.

5. Conclusions

The results of the toxicological research demonstrated that in order to assess the mycotoxic risk, it is possible to apply biotests, using the planarian Dugesia tigrina Girard instead of the costly physicochemical analysis by means of HPLC, which is additionally not friendly to the natural environment. This was confirmed by the results of the analyses carried out by means of HPLC. Strains of A. versicolor, which have the biological abilities to synthesise sterigmatocystin, occur on building partitions. However the number of highly mycotoxigenic strains in laboratory conditions is small. All of the research results presented in the paper are innovative as, owing to consequent complementation (the number of statistically significant tests), they led to valuable conclusions. The paper includes quotations from our own 17 research publications which were continued until our own two tables presented in this paper were drawn up (Table 3 and Table 4).

The mycological tests demonstrated the frequent occurrence of Aspergillus versicolor on inner building partitions (frequency 4). The conducted toxicological tests proved that Aspergillus versicolor is the most dangerous species for humans and animals in infected rooms owing to the synthesis of toxic and carcinogenic sterigmatocystin ST (category 2 B according to International Agency for Research of Cancer) in various quantities. All of the samples of air-dry mould biomass with the laboratory medium contained sterigmatocystin. A. versicolor is an allergenic species which may cause benign fungal infections. Biotoxicological tests of extracts from the biomasses of A. versicolor are necessary for the evaluation of the mycotoxic risk in buildings.