1. Introduction
The level of biological contamination of libraries and archives can be quite high and potentially dangerous not only for the stored materials that play the role of substrate for microorganism growth, but also for the occupants. In fact, the bioaerosol resulting from these contaminants can be inhaled in a passive way and/or breathed during the handling and the cleaning of dusty or mouldy books [
1,
2].
The microorganism number and type in libraries and archives depends on (i) the microclimatic conditions, i.e., the temperature and the air humidity, that may be affected by air recirculation and conditioning, (ii) the presence of macro- and micronutrients and (iii) the water activity (a
w) of the different substrates. Besides, the composition of the bioaerosol is strictly related to the microorganisms that colonize the surfaces and the stored material [
3].
The main paper biodeteriogenic microorganisms are xerophilic fungi able to tolerate dry environments, characterized by low values of water activity. In the first phase of colonization, bacteria are less relevant because they require high water activity values. Nevertheless, xerophilic fungi colonize the paper as pioneers, and in case the water activity value increases, the growth of other species, such as the cellulolytic fungi and bacteria, can also be sustained.
Both fungi and bacteria can persist on the library material for long periods, also for years, without producing biodeterioration phenomena. However, if the microclimatic conditions change, for example as a consequence of a flooding, favorable conditions are created for an increase in the microbial colonization and, consequently, for the decomposition of the organic matter [
4,
5]. In that case, the amounts and the type of the microorganisms or microbial metabolites can change: this can support the biodeterioration of the stored material, besides becoming a risk for the health of the library occupants [
6].
Fungal species such as
Aspergillus flavus,
A. parasiticus,
A. versicolor,
Penicillium chrysogenum,
P. expansum, and
Stachybotrys chartarum are commonly isolated in archives and in libraries, especially those characterized by high humidity; the presence of these fungi is probably associated with the production of mycotoxins or other volatile organic microbial compounds [
2]. Fungal species that need high values of water activity (a
w) to survive are commonly found in those rooms, destined to the paper material storage: these fungi can produce intense smell (es.
Trichoderma spp.), coloured mycelia (es.
Chaetomium spp. and
Epicoccum spp.), or toxic compounds (es.
Stachybotrys spp.) [
7].
The library and archive environments can become ideal also for cellulolytic fungi and other microbial species; the Ascomycetes (
Chaetomium spp.), the Phycomycetes (
Rhizopus and
Mucor spp.), and the Deuteromycetes (
Aspergillus,
Penicillium,
Trichoderma,
Stachybotrys,
Stemphylium,
Alternaria,
Mycothecium spp.) include fungal species which commonly biodegrade the cellulose in aerobic conditions. Among the bacteria,
Streptomyces,
Micromonospora,
Bacillus,
Cellulomonas, and
Cytophaga spp. can be listed [
8]. Two yeast genera (
Candida spp. and
Rhodotorula spp.) were isolated from photo on paper [
9].
Montanari et al. (2012) report, as a typical example of library contamination, the one that can occur in a compact storage shelving system [
5]. The presence of moulds and the signs of their growth can be evidenced on the binding of leather, parchment, or cotton fibre volumes. White and irregular fungal colonies are evident contamination signs on the exposed surfaces of the volumes located in the lower parts of the shelving blocks; commonly, the involved fungi belong to the genus
Aspergillus spp.
The occurrence of accidental events caused by water (i.e., rainstorm, flooding or fire extinction systems) unavoidably causes the growth of biodeteriogenic microorganisms on paper documents: currently, the freezing represents one of the most efficacious treatments to control biodeterioration of the flooded material. In fact, the frozen paper material can be stored for a very long time without negative consequences. In these cases, freeze-drying represents an interesting possibility for recovering the documents, since the first phase of the process, i.e., the freezing of the material, has already been carried out. Freeze-drying is a well-known technology, which can give excellent results avoiding further damages to paper material because the operating temperatures are very low and there is no presence of liquid water (during the process) that can displace soluble components present in the material, such as dyes and glues [
10,
11]. In the scientific literature, results of freeze-drying treatment on the viability of paper-born microorganisms are not univocal and are sometimes contradictory. As an example, according to the work by Troiano et al. (2013) [
12], lyophilization, in general, reduces significantly the microbial load present; on the contrary, Fissore et al. (2019) reported that growth of
R. mucilaginosa was stimulated [
13].
Few scientific papers on the effect of freeze-drying on biodeteriogenic microorganisms were published, probably due to the fact that microorganisms respond to the treatment in a species-dependent manner depending on the growth phase as well [
12]. In the work of Fissore et al. (2019) [
13], the effect of freezing and freeze-drying on microorganism survival and growth was separately evaluated and the necessity to control the paper-born microorganisms, after the lyophilization, appeared mandatory. In this framework, the possibility to control the biodeteriogenic and toxigenic microflora growth by using essential oils appears particularly interesting [
14].
Essential oils (EOs) are in fact well-known for their antimicrobial properties, and they were applied in several fields such as pharmaceutical and food industry. On the contrary, as reported by Díaz-Alonso et al. (2021) [
15], very few papers on the application of EO in the field of cultural heritage were published in the last decade [
16]. Therefore, the use of EOs as natural biocides in the control of biodeteriogenic microorganisms can still be considered a challenge. In the work of Díaz-Alonso et al. (2021) [
15], the effectiveness of
Melaleuca alternifolia (Tea tree) and
Thymus vulgaris (Thyme) EOs in reducing air bacterial and fungi contamination in unventilated indoor spaces was evaluated. The vaporization of tea tree EO showed the best results allowing an air contamination reduction equal to 77.3% and 95.0% for fungi and bacteria, respectively. Palla et al. (2020), in order to contrast the biodeterioration induced by
Aspergillus flavus or insect infestation (
Anobium punctatum), exposed wooden artworks to the volatile components of
Origanum vulgare or
Thymus vulgaris EOs [
17]. The authors concluded that these natural pesticides could be used as a valid alternative in the control of the biodeterioration processes avoiding any negative impact on the environment or operator health. The high antimicrobial activity of the wild thyme EO detected against
B. subtilis,
F. oxysporum and
A. niger, microorganisms, which quite frequently infest archives, libraries and historical art craft objects, was also reported by Casiglia et al. (2019) [
18].
The present study will thus be focused on the investigation of the effect of essential oils on contaminated paper considering two case studies, namely the contamination of paper that did not undergo any flooding and the contamination of freeze-dried paper, after flooding, as in this case, the response of the system may be different. The effect of freezing and drying on the survival of
S. epidermidis,
R. mucilaginosa and
A. alternata on flooded paper has already been described in a previous work [
13]. The process was not able to control the growth of
S. epidermidis and
R. mucilaginosa, while it inhibited
A. alternata. Thus, in the present work, a preliminary screening with
Thymus vulgaris and
Origanum vulgare leaf oils was performed, by means of “broth dilution methods”, on
S. epidermidis and
R. mucilaginosa. The effect of
Thymus vulgaris oil, vaporized immediately after the inoculum or at 24 h of incubation, was tested on the two unicellular microorganisms grown on agar media. Considering the positive effect of EO, the investigation was also extended to
A. alternata, chosen as representative of the filamentous fungi that can be found in archives. Finally, the treatment was extended on a real contaminated book. After that, a system was set up in which flooding and “artificial” contamination, followed by freezing or lyophilization process, at different time of growth, were realized; contaminated paper sheets, removed from the paper blocks, after lyophilization or freeze-thawing, were treated with the EO immediately or after 24 h of incubation. Finally, the treatment with
T. vulgaris oil was also applied on a real contaminated book.
2. Materials and Methods
The tested microorganisms (
Figure 1) were the Gram-positive bacterium,
S. epidermidis (LMG0474, BCCM, Belgium), the yeast
R. mucilaginosa and the filamentous fungus
A. alternata BNR, belonging to the private collection of the Biotechnological Laboratory of Politecnico di Torino. All the microorganisms have been described as paper biodeteriogens [
8,
9,
19,
20].
The media utilized for the maintenance and cultivation of S. epidermidis (incubated at 37 ± 0.5 °C), R. mucilaginosa, and A. alternata (both incubated at 30 ± 0.5 °C) were as follows, respectively: the Nutrient agar Oxoid CM003 (NA: yeast extract 2 g/L, peptone 5 g/L, NaCl 5 g/L, Lab-Lemco powder 1 g/L, and agar 15 g/L), the Malt Extract agar (MEA: malt extract 20 g/L, peptone 2 g/L, glucose 20 g/L, and agar 20 g/L), and the Czapeck agar (CZ: NaNO3 3 g/L, K2HPO4 1 g/L, MgSO4 0.5 g/L, KCl 0.5 g/L, FeSO4 0.01 g/L, glucose 30 g/L, and agar 20 g/L). The same media, without the agar, were applied for liquid medium studies. Sterile PE Petri dishes, without venting, 90 mm Ø, were utilized for the all experiments with solid media.
2.1. EO Screening in Liquid Medium: Broth Dilution Method
Thymus vulgaris OE0970 and
Origanum vulgare OE0375, both supplied by Witt Italia Spa, were the utilized essential oils (EOs); the EO suspensions were prepared, in sterile conditions, utilizing 1.5%
v/
v of polysorbate 20 (TEGO SML 20) as a diluent. A “96-well plate broth microdilution method” was applied to separately test the two EO antimicrobial susceptibility of
S. epidermidis and
R. mucilaginosa and to record the Minimum Inhibitory Concentration (MIC); with this purpose, the EUCAST protocols were followed with some modifications for bacteria and for fungi [
21,
22]. Two-fold serial dilutions of the EOs (0.75%, 0.375%, 0.1875%, 0.0938%, 0.0469%, 0.0234%, 0.0117%, and 0.0059%) were inoculated with standardized microbial inocula of each microorganism, prepared by means of the suspension of 3 colonies, grown for 24 h, in the appropriate medium as previously reported in
Section 2, to obtain a final well concentration in the range 1 × 10
5 ÷ 2.5 × 10
5 cfu/mL. Each well was filled with a total volume of 300 µL; samples, biotic and abiotic controls, together with controls prepared to check the possible influence of TEGO 1.5% (
v/
v) were set-up as indicated in
Table 1. Filled 96-well plates, sealed with Parafilm
®® and enveloped with PE transparent films to prevent EO losses, were incubated in static conditions, at the appropriate temperature, for 24 h. At the end of the incubation, the MIC was read as the lowest EO concentration that completely inhibits microbial growth by the naked eye. Moreover, to verify uncertain results, due to the turbidity and opacity of the EO suspensions, the viable count on agar plate was also carried out [
23]. A total of 10 µL were withdrawn from each sample well and spread over agar plates; after 24 h of incubation, the absence/or presence of microbial colonies was check to identify the MIC, as the lowest EO concentration that inhibit the microbial growth on agar medium.
The EO concentrations of 0.750%, 0.563%, and 0.375% (
v/
v) were tested with a “broth macrodilution method” in a dynamic system—in 10 mL sterile glass tubes, maintained in continuous agitation, on a rotator loopster, at 20 rpm, for 24 h. Each tube was filled with a total volume of 5.1 mL; sample, abiotic and biotic control samples were prepared maintaining the same proportions as indicated in
Table 1. At the end of the incubation, a withdrawal of 10 µL from each tube was spread over agar plates and incubated for 24 h. After that, the absence/or presence of microbial colonies was checked to identify the MIC.
2.2. EO Application on Solid Media and on Inoculated Paper Sheets
Considering the higher antimicrobial activity of
T. vulgaris (0.75%
v/
v), it was used for the following tests on microorganisms inoculated on agar plates or paper sheets. The suspension of 0.75%
Thymus vulgaris EO, diluted with 1.5% TEGO SML20, was used to directly treat
S. epidermidis and
R. mucilaginosa, inoculated to obtain separated colonies, and
A. alternata, nonsporulating mycelium, grown on solid media (for the description of the inocula refer to
Section 2.1). The EO treatment was carried out immediately after the inoculum or after 24 h of incubation; untreated samples were used as controls. The EO suspension was vaporized as described in the
Supplementary Material Section (Figure S1). The same EO treatment was also carried out on inoculated paper sheets after lyophilization or freeze thawing; the two paper sheets, contaminated either with
S. epidermidis,
R. mucilaginosa,
A. alternata, or with the mixed inoculum, were removed from the paper block (see
Section 2.4) and deposited on the appropriate agar medium. Moreover, in this case, the EO treatment was carried out immediately after the deposition in the Petri dish or after 24 h incubation, while untreated samples were used as controls. In order to prevent EO losses, all the Petri dishes were sealed with Parafilm
®® and enveloped with PE transparent films; after that, they all were incubated at the selected temperature and microbial growth was monitored for different incubation times depending on the microorganism.
Regarding the unicellular microorganisms, the possible increase in colony number was detected by the naked eye. In the specific case of
S. epidermidis, which is characterized by clear whitish colonies, not easily detectable, the replica plating of the paper sheet, inoculated and treated with the EO, was carried out after 72 h of incubation; after 1 h, the paper was removed and the agar plates were incubated. By this way, the bacterial colony detection resulted more accurately. The microbial growth was visually monitored every 24 h and for 5 days from the deposition of the contaminated paper sheets on the surface of the agar. Moreover, for
A. alternata colonies, at the same time, two perpendicular diameters of the colony were measured until the stop of the mycelium growth, or when the colony reached the edge of the Petri dishes. The mean diameter values were then used to calculate the inhibition percentage of mycelial growth (MGI%) as reported in Equation (1):
where d
c is the colony diameter in the control sheet and d
t is the colony diameter in the treated sheet.
2.3. EO Application on a Real Contaminated Book-Cover
The 0.75% (v/v) Thymus vulgaris EO suspension was also utilized to treat the contaminated cover of a real book. Before the EO treatment, the vitality of the microbial contaminants was checked by means of the replica plating of the colonies present on the cover. A sterile wooden stamp covered with sterile filter paper was applied, for 1 h, to the cover and then transferred to an MEA plate, hereafter incubated for 72 h at 30 °C. After that, pure colonies were isolated and treated with the EO treatment in three different ways: (a) the EO was directly nebulised on a contaminated area, delimited by means of a plastic mask (6 cm × 3 cm) (b) a paper sheet, impregnated with 0.75% EO, and was deposited on the contaminated cover for 2 h or for (c) 24 h. The treated book was placed in a box, completely sealed with PE transparent film, and incubated at 30 °C for 24 h; then, the EO treatments were repeated and the book incubated again for 72 h. The EO influence on the contaminant microorganisms was checked by the naked eye.
2.4. Simulation of Flooded Contaminated Books
In order to simulate real flooded contaminated books, the procedure described by Fissore et al. (2019) [
13] was applied, with some modifications. Microbial inocula were carried out on single sterile paper squares (60 mm × 60 mm of modern blank paper double A, 80 g cm
−2) deposited on the suitable agar medium.
S. epidermidis and
R. mucilaginosa were inoculated by means of replica plating of separated colonies, 1 ± 0.5 mm Ø, evenly grown on agar plates (to obtain separated colonies, 100 µL of a 1 × 10
5 microbial suspension was spread on solid medium and incubated for 24 h); paper sheets were then incubated for 48 h.
A. alternata was inoculated depositing, in the middle of the sheet, a mycelial plug, 5 mm Ø, withdrawn from a seven-day-old colony; the incubation was prolonged for 48 or 120 h to obtain, respectively, sporulating and nonsporulating mycelium. Moreover, mixed inocula of the three microorganisms (ratio 1:1:1) were also prepared depositing, in the middle of the paper sheet, a suspension, 30 µL, of hyphal fragments and cells, having an optical density at 650 nm (OD
650) of 0.8 ÷ 1. The mixed paper inoculum, deposited on MEA plates, where all the tested microorganisms showed an optimal growth, was incubated at 30 °C for 120 h.
Small blocks (60 mm × 60 mm, 10 ± 1 mm high) of modern paper were soaked in distilled water and then drained. After that, for each microorganism or for the mixed inoculum, two inoculated paper squares were respectively positioned on the surface (in the case of
A. alternata inoculated sheets, the mycelial plug was removed before composing the paper block) and in the middle of a soaked paper block. Set-up blocks were opportunely packed to be frozen or lyophilized as reported by Fissore et al. (2019) [
13]. Freeze drying was carried out in a lab-scale REVO freeze dryer (Millrock, Kingston, NY, USA) at 0 °C and 200 bar for 72 h, thus ensuring the total removal of frozen water. Freezing was carried out in a domestic freezer, whose temperature was set at (about) −20 °C. Although freezing could be carried out in the same equipment where the ice sublimation will take place (as it is generally done for pharmaceutical applications), in this part of the study, we aimed at mimicking the situation in which books are frozen immediately after flooding, and then drying is carried out. Additional tests were carried out considering the treatment of the paper material after a freeze-thawing test; this aimed at mimicking the situation where the soaked paper is frozen, to stop microbial deterioration, and then thawed to go on with traditional (hot) air drying. Moreover, in this case, freezing was carried out at −20 °C in a domestic apparatus.
4. Discussion
In the preliminary test (microbroth test in static conditions), both
O. vulgare and
T. vulgaris EOs exhibited an inhibition effect on the unicellular microorganisms; a higher activity for
T. vulgaris EO was observed. A MIC value was not obtained for
O. vulgare, notwithstanding an observed lower growth rate. The MIC for
T. vulgaris EO against
S. epidermidis was 7.5 µg/mL, in accordance with values reported in the literature (see
Table 3).
Results obtained in broth dilution method have been confirmed with tests carried out on agar plates, for which
A. alternata was considered together with unicellular microorganisms, using 0.75%
T. vulgaris. The inhibition on the growth of all the microorganisms was higher when the samples were treated at t(0) even if some inhibition effect were observed in the case of delayed treatments. As an example, in
R. mucilaginosa, a depigmentation was observed (
Figure 3), probably related to an influence of EO on the carotenoid synthesis pathway, as reported in a previous work for the fungicide naftifine [
26]. The same behavior was observed for all the microorganisms cultured on paper sheets (data not shown); in this case, the antimicrobial activity was higher, probably in relation to the absorption of the EO on paper which guarantees a longer contact time with the microorganism.
Finally, when the selected EO was applied on a real contaminated book cover, the inhibition was lower in the area where the EO was sprayed with respect to that obtained by means of contact sheets. In the last case, the presence of the paper probably reduces the evaporation rate of the volatile components of the oil (see
Section 3.3 and
Figure 5). Therefore, when moving to a real case, a suitable dispersion system has to be designed to cope with this issue.
Concerning the EO treatment after flooding and lyophilization, it has to be pointed out that the lyophilization process did not control the growth of
R. mucilaginosa, as previously reported by Fissore et al. (2019) [
13]. Considering the effect of
T. vulgaris EO (0.75%), when the contaminated sheets were treated immediately after lyophilization t(0), the microbial growth was lower than that observed for the sheets treated later t(24). Additionally, for
S. epidermidis, the major inhibition effect also was observed when the contaminated sheets were treated immediately after the freeze-drying process (see
Figure 7).
The not sporulated mycelium of
A. alternata was inhibited by the lyophilization for a double time with respect to the sporulated one due to a higher spore resistance to thermal shock and to low a
w values, as reported by Troiano et al. (2013) and Lucchese (2019) [
12,
27]. In the present work, the results reported by Salehi et al. (2018), Tullio et al. (2007), and Soylu et al. (2015) [
24,
28,
29] on the efficacy of
T. vulgaris oil on
A. alternata, were confirmed.
Thymus vulgaris EO (0.75%) was also demonstrated to be effective on paper sheets with mixed contamination, after freezing and after freeze-drying. The EO was able to inhibit the microbial growth, independently from the treatment process, i.e., after freeze and thaw or after lyophilization. Comparing the results obtained for
A. alternata growth, it was confirmed that lyophilization was more effective than the sole freezing in the control of microbial growth (see
Figure 10 and
Figure 11), as previously reported [
13].
In conclusion, the treatment with
T. vulgaris EO represents a real opportunity to control the growth of microorganisms involved in paper biodeterioration. With this in mind, the obtained results were exploited in the risk-based decision-making process for the safety of librarian heritage, adopting EOs as prevention measures but also for protection after accidental events, as discussed in [
30].