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ARTICLE IN PRESS<br />

International Biodeterioration & Biodegradation 56 (2005) 58–68<br />

www.elsevier.com/locate/ibiod<br />

<strong>Isolation</strong> <strong>and</strong> <strong>identification</strong> <strong>of</strong> <strong>bacteria</strong> <strong>and</strong> <strong>fungi</strong> <strong>from</strong><br />

cinematographic films<br />

C.Abrusci a , A.Martín-Gonza´ lez a , A.Del Amo b , F.Catalina c, , J.Collado d , G.Platas d<br />

a Departamento de Microbiología III, Facultad de Biología, Universidad Complutense de Madrid, José Antonio Novais, 2, 28040-Madrid, Spain<br />

b Filmoteca Española, Magdalena 10, 28012-Madrid, Spain<br />

c Departamento de Fotoquímica de Polímeros, Instituto de Ciencia y Tecnología de Polímeros, C.S.I.C, Juan de la Cierva 3, 28006-Madrid, Spain<br />

d Centro de Investigación Básica, Merck Research Laboratories, Merck Sharp <strong>and</strong> Dohme de España, Josefa Valcárcel, 38, 28027 Madrid, Spain<br />

Received 22 December 2004; received in revised form 15 April 2005; accepted 5 May 2005<br />

Abstract<br />

Bacteria <strong>and</strong> <strong>fungi</strong> present in black <strong>and</strong> white cinematographic film samples <strong>from</strong> Spanish archives in Madrid, Barcelona <strong>and</strong><br />

Gran Canaria were isolated <strong>and</strong> identified.All samples studied were contaminated.Fourteen strains <strong>of</strong> <strong>bacteria</strong> were isolated.<br />

Preliminary characterization was carried out by morphological <strong>and</strong> biochemical-physiological methods, using different commercial<br />

assays depending on the <strong>bacteria</strong>l nature.Five species <strong>of</strong> Staphylococcus, viz. S. epidermidis, S. hominis, S. lentus, S. haemolyticus<br />

<strong>and</strong> S. lugdunensis, <strong>and</strong> five species <strong>of</strong> Bacillus, viz. B. amyloliquefaciens, B. subtilis, B. megaterium, B. pichinotyi <strong>and</strong> B. pumilus, were<br />

identified, together with Sphingomonas paucimobilis, Kocuria kristinae <strong>and</strong> Pasteurella haemolytica.Seventeen strains <strong>of</strong> filamentous<br />

<strong>fungi</strong> <strong>and</strong> one yeast, Cryptococcus albidus, were isolated <strong>and</strong> identified by microsatellite-primed PCR <strong>and</strong> rDNA sequencing.The<br />

fungal strains present in the films consisted <strong>of</strong> four strains <strong>of</strong> Aspergillus viz. A. ustus, A. nidulans var.nidulans, A. versicolor, seven<br />

Penicillium chrysogenum strains, as well as, Alternaria alternata, Cladosporium cladosporioides, Mucor racemosus, Phoma glomerata<br />

<strong>and</strong> Trichoderma longibrachiatum.Only seven <strong>bacteria</strong>l strains were able to degrade gelatin (binder in photographic emulsions), in<br />

contrast to the fungal isolates, all <strong>of</strong> which liquefied gelatin, with the exception <strong>of</strong> the yeast Cryptococcus albidus.Most <strong>of</strong> the<br />

microorganisms that were found colonizing the cinematographic films show resistance to adverse environmental conditions.<br />

r 2005 Elsevier Ltd.All rights reserved.<br />

Keywords: Cinematographic film; Fungi; Bacteria; Biodeterioration; Biodegradation; Historic <strong>and</strong> cultural heritage; Film preservation<br />

1. Introduction<br />

Cinematographic films form an important part <strong>of</strong> the<br />

historic <strong>and</strong> cultural heritage, since they have particular<br />

artistic, historical <strong>and</strong> ethnological values conferred by<br />

our society.Like other more traditional works <strong>of</strong> art,<br />

such as, paintings, sculptures, masonry, books, etc.,<br />

cinematographic materials require adequate conservation<br />

conditions in order to prevent their biodeterioration.<br />

A photographic film is composed <strong>of</strong> three generic<br />

components: a plastic support, an image-forming<br />

Corresponding author.Tel.: +34 91 5622900; fax: +34 91 5644853.<br />

E-mail address: fcatalina@<strong>ictp</strong>.csic.es (F. Catalina).<br />

material (black <strong>and</strong> white images are formed by metallic<br />

silver particles <strong>and</strong> colour images are made <strong>of</strong> colour<br />

dyes) <strong>and</strong> a binder that is commonly based on gelatin.<br />

The last two components are the main materials <strong>of</strong> the<br />

photographic emulsion layer.During cinematographic<br />

history, several supports have been used to manufacture<br />

pr<strong>of</strong>essional motion-picture films: cellulose nitrate (CN,<br />

<strong>from</strong> 1889 to 1950), cellulose triacetate (CTA, <strong>from</strong> 1948<br />

to 2000) <strong>and</strong> polyethylene tereftalate (<strong>from</strong> 1990s to the<br />

present), so that cellulose triacetate constitutes the bulk<br />

<strong>of</strong> the film collections today.It is estimated that there<br />

are approx.1.5 million roll-cans in Spain, including<br />

those held in private laboratories <strong>and</strong> cinematographic<br />

companies <strong>and</strong> in national <strong>and</strong> regional public archives.<br />

Filmoteca Espan˜ ola has the responsibility for the<br />

0964-8305/$ - see front matter r 2005 Elsevier Ltd.All rights reserved.<br />

doi:10.1016/j.ibiod.2005.05.004


ARTICLE IN PRESS<br />

C. Abrusci et al. / International Biodeterioration & Biodegradation 56 (2005) 58–68 59<br />

conservation <strong>and</strong> preservation <strong>of</strong> 430,000 roll-cans that<br />

constitute an important <strong>and</strong> irreplaceable historical <strong>and</strong><br />

cultural heritage.<br />

The image stability depends on both intrinsic factors,<br />

e.g. the nature <strong>of</strong> the polymer base, <strong>and</strong> extrinsic factors,<br />

e.g. environmental conditions. Archivists have encountered<br />

the problem <strong>of</strong> film deterioration caused by<br />

inappropriate storage conditions <strong>of</strong> temperature <strong>and</strong><br />

moisture.Many efforts have focused on the decrease <strong>of</strong><br />

the physical damage caused by the ‘‘vinegar syndrome’’<br />

in cellulose acetate-based films (Catalina <strong>and</strong> Del Amo,<br />

1999) <strong>and</strong> the fading <strong>of</strong> colour dyes.In contrast, there is<br />

a lack <strong>of</strong> knowledge about the contamination by<br />

<strong>bacteria</strong> <strong>and</strong> <strong>fungi</strong> in cinematographic archives <strong>and</strong> its<br />

influence on film stability.Studies on microbial contamination<br />

<strong>of</strong> cinematographic films stored in archives<br />

are scant <strong>and</strong> have been reviewed by Abrusci et al.<br />

(2004a).The main work has been done by Opela (1992)<br />

<strong>and</strong> involved the analysis <strong>of</strong> cellular concentration <strong>and</strong><br />

the <strong>identification</strong> <strong>of</strong> the principal fungal contaminants in<br />

the air, on floors, in cans <strong>and</strong> on cinematographic films<br />

in two different archives <strong>of</strong> the Slovak Republic.As in<br />

other studies <strong>of</strong> indoor habitats, the results indicated<br />

that certain environmental conditions, such as, air flow,<br />

temperature, movement <strong>of</strong> personnel, etc., had a crucial<br />

effect on microbial concentrations in the diverse places<br />

analyzed.The fungal biodiversity was higher in the air<br />

than in the surface <strong>of</strong> the films, biodiversity being<br />

limited in archives, with filamentous species in the<br />

genera Penicillium <strong>and</strong> Aspergillus being the predominant<br />

micromycetes (Opela, 1992). Aspergillus <strong>and</strong><br />

Penicillium have been reported as the most frequently<br />

found micromycetes in indoor air <strong>and</strong> buildings <strong>from</strong><br />

cold <strong>and</strong> temperate climate regions (Frisvad <strong>and</strong> Gravesen,<br />

1994; Hyva¨ rinen et al., 2002).These <strong>fungi</strong> are<br />

considered to be primary colonizers, since they are<br />

capable <strong>of</strong> growing at a w o0:8, although many species<br />

have the optimum for growth at a w values close to 1<br />

(Nielsen, 2003).Other genera <strong>of</strong> <strong>fungi</strong> (Alternaria,<br />

Cladosporium, Phoma, etc.) are secondary colonizers,<br />

because they require a w values at least between 0.8 <strong>and</strong><br />

0.9 (Nielsen, 2003).The presence <strong>of</strong> spores <strong>and</strong>/or<br />

vegetative cells <strong>of</strong> microorganisms on the surface <strong>of</strong><br />

materials indicate the possibility <strong>of</strong> future biodegradation<br />

or biodeterioration.However, colonization or<br />

microbial growth on a material almost always results<br />

in biodeterioration <strong>of</strong> the material.There are different<br />

ways in which microorganisms can compromise the<br />

structure <strong>and</strong> function <strong>of</strong> polymeric materials (Flemming,<br />

1998).For instance, they can produce pigmentation<br />

or degrade <strong>of</strong> one or more compounds.In other<br />

cases, they can hydrate, <strong>and</strong> as well as causing fouling,<br />

they may penetrate into the polymeric material.These<br />

mechanisms <strong>of</strong> biodeterioration occur when microorganisms<br />

are metabolically active <strong>and</strong> growing, but<br />

although the environment contains an extremely rich<br />

variety <strong>of</strong> microorganisms, usually only a few <strong>of</strong> the<br />

microorganisms isolated <strong>from</strong> a substrate are responsible<br />

for damaging it.<br />

In cinematographic films, the organic components<br />

mentioned previously can be considered as potential<br />

carbon sources for growth <strong>of</strong> microorganisms, if<br />

environmental conditions are adequate.Gelatin, the<br />

binder <strong>of</strong> the photographic emulsion, is the most<br />

biodegradable <strong>of</strong> the substrates.It is composed <strong>of</strong> high<br />

molecular weight polypeptides derived <strong>from</strong> collagen,<br />

<strong>and</strong> the most widely used photographic gelatin is type-B,<br />

obtained by basic pre-treatment <strong>of</strong> bones (Abrusci et al.,<br />

2004b).Many prokaryotic <strong>and</strong> eukaryotic microorganisms<br />

exhibit proteolytic capacity, so they are able to<br />

degrade gelatin. Stickley (1986) studied by viscometry<br />

the biodegradation <strong>of</strong> 5% aqueous gelatin solutions at<br />

37 1C using single strains <strong>of</strong> Bacillus <strong>and</strong> Pseudomonas.<br />

In both cases, reduced viscosity was detected after 24 h.<br />

In a more detailed study, Abrusci et al.(2004c)<br />

viscosimetrically analysed the biodegradation <strong>of</strong> type-B<br />

gelatin (Bloom 225) by <strong>bacteria</strong> isolated <strong>from</strong> cinematographic<br />

films, <strong>and</strong> noted that temperature is a very<br />

important factor affecting rate <strong>of</strong> biodegradation<br />

(Abrusci et al., 2004c).<br />

As for film base materials, a large number <strong>of</strong> studies<br />

have been carried out on biodegradation <strong>of</strong> cellulose<br />

acetates (CA) by both <strong>bacteria</strong> <strong>and</strong> <strong>fungi</strong>.The degree <strong>of</strong><br />

hydroxyl substitution (acetylation) has been found to be<br />

a factor with a strong influence on biodegradation, those<br />

CA with a higher degree <strong>of</strong> acetylation being more<br />

resistant to microbial attack (Buchanan et al., 1993;<br />

Nelson et al., 1993; Sakai et al., 1996).According to<br />

Sakai et al.(1996), CA biodegradation is mediated by<br />

the cooperative action <strong>of</strong> esterase(s), lipase(s) <strong>and</strong><br />

cellulase(s).These studies were carried out adding pure<br />

cultures <strong>of</strong> identified species (Samios et al., 1997; Nelson<br />

et al., 1993) or using mixed populations such as those<br />

included in compost (Gu et al., 1993b).The cellulose<br />

triacetate used in the photographic industry has a degree<br />

<strong>of</strong> substitution <strong>of</strong> approx.2.7.Hence, its resistance to<br />

biodegradation should be much higher than the other<br />

components <strong>of</strong> the film.In fact, it has been reported that<br />

microorganisms attack the organic part <strong>of</strong> the film<br />

emulsion especially at R.H. 460% ða w 40:6Þ (Gordon,<br />

1983).In tropical climates fungal growth is a special<br />

problem, but it is also possible to detect these troublesome<br />

growths during the summer in temperate zones<br />

with high relative humidity.<br />

Owing to the risk <strong>of</strong> biodeterioration <strong>of</strong> cinematographic<br />

film in the Spanish archives, we isolated <strong>and</strong><br />

identified <strong>bacteria</strong> <strong>and</strong> <strong>fungi</strong> <strong>from</strong> selected samples <strong>of</strong><br />

cinematographic films collected in different archives.<br />

The <strong>identification</strong> studies in organisms <strong>from</strong> black <strong>and</strong><br />

white cinematographic films are presented here, along<br />

with an analysis <strong>of</strong> the ability <strong>of</strong> these isolates to<br />

hydrolyse the gelatinous component <strong>of</strong> films.


60<br />

ARTICLE IN PRESS<br />

C. Abrusci et al. / International Biodeterioration & Biodegradation 56 (2005) 58–68<br />

2. Materials <strong>and</strong> methods<br />

2.1. Cinematographic film samples<br />

Film samples <strong>from</strong> collections at Barcelona, Madrid<br />

<strong>and</strong> Gran Canaria archives were supplied by Filmoteca<br />

Espan˜ ola.The sampling <strong>and</strong> transport <strong>of</strong> the samples<br />

were carried out under aseptic conditions.The films<br />

supplied appeared to be in good condition.<br />

2.2. <strong>Isolation</strong> <strong>of</strong> microorganisms <strong>from</strong> cinematographic<br />

films<br />

The isolation procedure for all samples was performed<br />

in a laminar-flow chamber <strong>and</strong> manual operations<br />

were carried out using sterile disposable gloves.<br />

From each cinematographic sample, two or three pieces<br />

were placed on trypticase-soya-agar (TSA), for heterotrophic<br />

<strong>bacteria</strong>, <strong>and</strong> Sabouraud-glucose-agar (SAB)<br />

supplemented with choramphenicol for <strong>fungi</strong>.Petri<br />

dishes were incubated at 30 1C for 1–2 weeks.Cultures<br />

were observed daily under a stereoscopic microscope to<br />

check the presence <strong>of</strong> <strong>bacteria</strong>l colonies <strong>and</strong>/or fungal<br />

mycelium (Fig.1).<br />

2.3. Characterization <strong>of</strong> <strong>bacteria</strong><br />

Each <strong>bacteria</strong>l strain isolated <strong>from</strong> the film samples<br />

was cultured on TSA either at 30 or 37 1C for 48 h.<br />

Replicates were made <strong>and</strong> preserved at 4 1C or 80 1C<br />

using TSB liquid medium supplemented with glycerol.<br />

Gram- <strong>and</strong> simple staining were performed using<br />

exponential TSA cultures, <strong>and</strong> oxidase <strong>and</strong> catalase tests<br />

made.Acid production <strong>from</strong> glucose <strong>and</strong> sucrose on OF<br />

basal medium, growth on Simmons citrate agar, <strong>and</strong><br />

starch <strong>and</strong> gelatin hydrolysis, were tested.In all Grampositive<br />

(<strong>and</strong> some Gram-negative strains), the ability to<br />

form spores was tested by examining 24-, 48- <strong>and</strong> 72-h,<br />

<strong>and</strong> 1-week cultures on TSA, as well as the Schaeffer-<br />

Fulton specific stain (Forbes et al., 2002).Morphological<br />

characters were examined under differential interference<br />

contrast (Nomarski) <strong>and</strong> phase contrast using a<br />

Zeiss Laboval 4 optical microscope.<br />

Fig.1.One-week Petri dish cultures at 30 1C showing on left<br />

micr<strong>of</strong>ungi P. chrysogenum (upper) <strong>and</strong> A. alternata (lower), <strong>and</strong> on<br />

right B. subtilis developing <strong>from</strong> fragments <strong>of</strong> film.<br />

After the preliminary morphological <strong>and</strong> physiological<br />

characterization as used by Oppong et al.(2000),<br />

<strong>bacteria</strong>l strains were identified employing commercial<br />

<strong>identification</strong> kits.Depending on the <strong>bacteria</strong>l nature,<br />

different commercial assays were employed such us API<br />

20 NE, API 20E, API 50 CHB <strong>and</strong> API STAPH.The<br />

preparation <strong>and</strong> inoculation procedures followed the<br />

recommendations <strong>of</strong> the manufacturer (BioMerieux<br />

Espan˜ a S.A.), with the strains being incubated at 30 1C<br />

for 24 h.The numeric pr<strong>of</strong>iles obtained were compared<br />

with a <strong>bacteria</strong>l database using the commercial s<strong>of</strong>tware<br />

APILAB <strong>from</strong> BioMerieux.Simultaneously, additional<br />

diagnostic tests were made with some <strong>bacteria</strong>l strains,<br />

such as growth on McConkey or mannitol salt agar <strong>and</strong><br />

coagulase <strong>and</strong> lysostaphin tests.<br />

2.4. <strong>Isolation</strong> <strong>and</strong> characterization <strong>of</strong> <strong>fungi</strong><br />

For isolation <strong>of</strong> micromycetes, film samples were<br />

incubated on potato-dextrose-agar (PDA) at 28 1C or<br />

30 1C for 1–2 weeks.Replicates were preserved at 4 1Cor<br />

80 1C in PD broth medium supplemented with 10%<br />

glycerol.<br />

The following media were used for characterization:<br />

(a) malt extract agar (MEA) composed <strong>of</strong> malt<br />

extract (Difco) 20 g, peptone 1 g, glucose 20 g, agar<br />

20 g, distilled water 1 L; (b) Czapek yeast extract agar<br />

(CYA) composed <strong>of</strong> K 2 HPO 4 1 g, Czapek concentrate<br />

10 ml, yeast extract (Difco) 5 g, Sucrose 30 or 200 g, agar<br />

15 g, distilled water 1 L; (c) 25% glycerol nitrate agar<br />

(G25N) composed <strong>of</strong> K 2 HPO 4 0.75 g, Czapek concentrate<br />

7.5 ml, yeast extract 3.7 g, glycerol, analytical grade<br />

250 g, agar 12 g, distilled water 750 ml; (d) potato-carrotagar<br />

(PCA) composed <strong>of</strong> shredded potato 20 g, shredded<br />

carrot 20 g, agar 20 g, distilled water 1 L; <strong>and</strong> (e) PDA<br />

(Difco).Czapek concentrate contained: NaNO 3 30 g,<br />

KCl 5 g, MgSO 4 .7H 2 O 5 g, FeSO 4 .7H 2 O 0.1 g ZnSO 4 .7<br />

H 2 O 0.1 g, CuSO 4 .5H 2 O 0.05 g, distilled water 100 ml.<br />

Seven-day cultures on MEA, CYA (with either 3% or<br />

20% sucrose), <strong>and</strong> G25N were used for <strong>identification</strong> <strong>of</strong><br />

Aspergillus <strong>and</strong> Penicillium species, based on the<br />

procedures described by Pitt (2000) <strong>and</strong> Klich (2001).<br />

The other strains were cultured on PDA <strong>and</strong> PCA for 21<br />

days at 22 1C <strong>and</strong> 80% R.H. <strong>and</strong> then subjected to cycles<br />

<strong>of</strong> NUV wavelength light exposure-darkness (12 h each)<br />

at room temperature for at least 14 days to stimulate<br />

sporulation.Morphological analysis <strong>of</strong> the isolates was<br />

carried out with a Leitz Diaplan microscope, equipped<br />

with differential interference contrast optics.The fungal<br />

isolates were identified to species (Aspergillus <strong>and</strong><br />

Penicillium) or generic level.<br />

The yeast isolate was identified on the basis <strong>of</strong><br />

metabolic/physiological features using the API 20C-<br />

AUX kit (BioMerieux Espan˜ a, S.A.), <strong>and</strong> simple crystal<br />

violet staining was used for observing cell size <strong>and</strong><br />

shape.


ARTICLE IN PRESS<br />

C. Abrusci et al. / International Biodeterioration & Biodegradation 56 (2005) 58–68 61<br />

2.5. PCR reactions, microsatellite primed PCR <strong>and</strong><br />

rDNA amplifications <strong>and</strong> sequence in <strong>fungi</strong><br />

DNA extraction was performed by the methodology<br />

described by Pela´ ez et al.(1996).Mycelium was removed<br />

<strong>from</strong> the agar plate with a razor blade, fragmented <strong>and</strong><br />

suspended in 1 ml lysis buffer (50 mM EDTA, pH 8.5,<br />

0.2% SDS) <strong>and</strong> heat-shock treated at 75 1C for 30 min.<br />

After centrifugation in a Bi<strong>of</strong>uge 13 (Heraeus) at<br />

15,000 rpm <strong>and</strong> supernatant was adjusted to a final<br />

concentration <strong>of</strong> 0.3 M potassium acetate <strong>and</strong> chilled for<br />

1 h in ice.After a second centrifugation step, the<br />

supernatant was mixed with 2 volumes absolute ethanol<br />

to precipitate the DNA, which was dissolved in TE<br />

buffer.The DNA concentration obtained using this<br />

procedure ranged <strong>from</strong> 0.01 to 0.1 mgml<br />

1 .<br />

The amplification <strong>of</strong> both internal transcribed spacers<br />

(ITS1 <strong>and</strong> ITS2) <strong>and</strong> the 5.8S gene <strong>of</strong> these isolates<br />

was performed using primers 18S-3 (5 0 TTACGTCCC<br />

TGCCCTTTGTACA3 0 ) <strong>and</strong> NL1R, inverse to NL1<br />

(O’Donnell, 1993) (5 0 CTTTTCCTCCGCTTATTGATA<br />

TCG3 0 ), following st<strong>and</strong>ard procedures (40 cycles <strong>of</strong> 30 s<br />

at 93 1C, 30 s at 531C <strong>and</strong> 2 min at 72 1C) with Taq DNA<br />

polymerase (Q-bioGene) following the procedures recommended<br />

by the manufacturer.Amplification products<br />

(0.1 mgml<br />

1 ) were sequenced using the Bigdye<br />

Terminators version 1.1 (Applied Biosystems, Norwalk<br />

CT, USA) following the procedures recommended by<br />

the manufacturer.For all the amplification products,<br />

each str<strong>and</strong> was sequenced with the same primers used<br />

for the initial amplification.Separation <strong>of</strong> the reaction<br />

products by electrophoresis was performed in an ABI<br />

PRISM 3700 DNA Analyzer (Applied Biosystems).<br />

Partial sequences were assembled manually, <strong>and</strong> a<br />

consensus sequence was generated.Comparison <strong>of</strong> the<br />

DNA sequences was performed with in-house DNA<br />

databases <strong>and</strong> GenBank using the FASTA application.<br />

Microsatellite primed PCR was performed as described<br />

by Bills et al.(1999) using primer (GTG) 5<br />

<strong>and</strong> following st<strong>and</strong>ard procedures (40 cycles <strong>of</strong> 30 s<br />

at 93 1C, 30 s at 53 1C <strong>and</strong> 2 min at 72 1C) with Taq<br />

DNA polymerase (Q-bioGene) following the procedures<br />

recommended by the manufacturer.The DNA fragments<br />

were separated on a ready-to-use 1.2% agarose<br />

E-gel (Invitrogen), with a 100-base pair ladder for<br />

comparison.<br />

2.6. Gelatin hydrolysis test<br />

With the <strong>bacteria</strong>, two gelatin assays were performed,<br />

a Petri dish <strong>and</strong> a tube tests.The fungal strains were<br />

tested using the latter assay.In the Petri dish test, the<br />

isolate was streaked out on TSA medium supplemented<br />

with gelatin (5 g L 1 ).After incubation for 24–48 h at<br />

37 1C, 5 ml Frazier’s reagent was poured over each<br />

culture plate, <strong>and</strong> the presence <strong>of</strong> a transparent halo<br />

around the microorganism taken as an indication <strong>of</strong> the<br />

positive hydrolysis.The tube test was only applied as<br />

confirmation <strong>of</strong> positive Petri dish test results.In this<br />

second procedure, each strain was used to inoculate by<br />

needle puncture gelatin medium in a test-tube.The<br />

medium <strong>of</strong> a solution <strong>of</strong> 120 g gelatin, 5 g gelatinpeptone<br />

<strong>and</strong> 3 g pure beef extract in 1 L distilled water<br />

that remains fluid at temperatures over 35 1C.The<br />

inoculated tubes were incubated under test for 14 days<br />

at the appropriate temperature for the microorganism.<br />

The tubes were then acclimated at 4 1C <strong>and</strong> gelatin<br />

hydrolysis evidenced by medium drop-down (liquefaction)<br />

when the test-tube was inverted.<br />

2.7. Scanning electron microscopy<br />

For the characterization <strong>of</strong> strains by environmental<br />

scanning electron microscopy (ESEM), a PHILIPS<br />

model XL30 with EDAX X-ray analyzer was used.<br />

Samples were examined employing an environmental<br />

control in the ‘‘wet’’ mode <strong>of</strong> microscope operation<br />

(Go´ mez-Varga, 2004), under which conditions conventional<br />

EM preparation techniques are unnecessary.A<br />

water-cooled Peltier stage was employed to keep the<br />

sample at approximately 2 1C, within a chamber<br />

environment <strong>of</strong> water vapour at a pressure <strong>of</strong> 5 torr<br />

(pressure interval <strong>of</strong> this mode 4–10 torr).For examination<br />

<strong>of</strong> some samples under dry conditions, the samples<br />

were coated with approx.3 nm <strong>of</strong> gold/palladium using<br />

a Polaron SC 7640 sputter coater.<br />

3. Results <strong>and</strong> discussion<br />

3.1. Characterization <strong>and</strong> <strong>identification</strong> <strong>of</strong> the <strong>bacteria</strong>l<br />

isolates<br />

A total <strong>of</strong> 14 <strong>bacteria</strong>l strains were isolated <strong>from</strong> films<br />

stored in the three archives, most being Gram-positive<br />

(Table 1).The rod-like <strong>bacteria</strong> isolated exhibited<br />

motility <strong>and</strong> were oxidase- <strong>and</strong> catalase-positive; they<br />

all produced exopolymers.In their <strong>identification</strong>, the<br />

percentage <strong>of</strong> similarity showed values <strong>of</strong> 97.3–99.9%<br />

for all, except for Staphylococcus haemolyticus (90.1%),<br />

Bacillus amyloliquefaciens (88.1), B. subtilis <strong>and</strong> Pasteurella<br />

haemolytica (86.5%). The Gram-positive rods were<br />

identified as four different species <strong>of</strong> Bacillus.Strain M2,<br />

isolated <strong>from</strong> the Madrid archive, corresponds to B.<br />

pichinotyi (AF 519460), which was first isolated <strong>from</strong><br />

tropical rice soils (Sneath, 1986).This strain has at least<br />

two features that differ <strong>from</strong> the other Bacillus spp: the<br />

Gram stain was always positive <strong>and</strong> endospore formation<br />

was not observed.Two strains <strong>of</strong> B. megaterium<br />

were characterized; one <strong>from</strong> Gran Canaria <strong>and</strong> the<br />

other <strong>from</strong> Barcelona.Both isolates produced abundant<br />

exopolymers <strong>and</strong> poly b-hydroxybutyrate granules.


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Table 1<br />

Archives, samples, type <strong>of</strong> base, <strong>identification</strong> <strong>and</strong> strain codes <strong>of</strong> the isolated microorganisms form cinematographic films<br />

Archive Sample Base Identification Strain code<br />

Barcelona B1 CTA Alternaria alternata HB1<br />

B2 CTA Staphylococcus epidermidis B2<br />

Aspergillus ustus<br />

HB2<br />

B3 CTA Bacillus amyloliquefaciens B3BA<br />

Bacillus subtilis<br />

B3BS<br />

Cladosporium cladosporioides<br />

HB3A<br />

B4 CTA Sphingomonas paucimobilis B4A<br />

Staphylococcus hominis<br />

B4C<br />

Penicillium chrysogenum<br />

HB41B<br />

Alternaria alternata<br />

HB41N<br />

B5 CN Staphylococcus lentus B5<br />

B6 CTA Penicillium chrysogenum HB6<br />

Cryptococcus albidus<br />

LB6<br />

B7 CN Bacillus megaterium B7<br />

Penicillium chrysogenum<br />

HB7<br />

Gran Canaria GC1 CTA Pasteurella haemolytica GC1A<br />

Staphylococcus lugdunensis<br />

GC1B<br />

Penicillium chrysogenum<br />

HGC1<br />

GC2 CTA Trichoderma longibrachiatum HGC2<br />

Bacillus megaterium<br />

GC2<br />

Aspergillus ustus<br />

HGC2B<br />

GC3 CTA Aspergillus versicolor HGC3<br />

Penicillium chrysogenum<br />

HGC3B<br />

Phoma glomerata<br />

HGC3N<br />

LV a CTA Penicillium chrysogenum HLV1<br />

Madrid M2 CTA Bacillus pichinotyi M2<br />

M3 CTA Staphylococcus haemolyticus M3<br />

Aspergillus nidulans var. nidulans<br />

HM3<br />

M4 CTA Kocuria kristinae M4<br />

Mucor racemosus<br />

HM4<br />

M5 CTA Bacillus pumilus M5<br />

MI CTA Penicillium chrysogenum HMI<br />

CTA: Cellulose triacetate base; CN: cellulose nitrate base.<br />

a LV sample was a fragment <strong>of</strong> a roll-can.<br />

Also, there were six different strains <strong>of</strong> Gram-positive<br />

cocci with cells in chains (B2 <strong>and</strong> B4C), tetrads<br />

(M4) or individual cells (B5, GC1B <strong>and</strong> M3).None<br />

showed motility <strong>and</strong> all were catalase-positive.Only two<br />

Gram-negative rods were isolated (Table 1).They were<br />

oxidase <strong>and</strong> catalase positive, <strong>and</strong> were identified<br />

as P. haemolytica <strong>and</strong> Sphingomonas paucimobilis.<br />

These cocci were identified as Staphylococcus, with the<br />

exception <strong>of</strong> the pigmented strain M4 that corresponds<br />

to yellow pigment producer Kocuria kristinae.<br />

The main habitats <strong>and</strong> morphological/physiological<br />

characteristics <strong>of</strong> the <strong>bacteria</strong>l isolates are <strong>of</strong> relevance in<br />

explaining the potential causes <strong>of</strong> contamination <strong>of</strong> the<br />

films.Members <strong>of</strong> the genus Staphylococcus are widespread<br />

in nature.Owing to their ubiquity <strong>and</strong> adaptability,<br />

they are major inhabitants <strong>of</strong> the skin, skin<br />

gl<strong>and</strong>s <strong>and</strong> mucous membranes <strong>of</strong> humans, other<br />

mammals <strong>and</strong> birds (Kloos et al., 1992).They are<br />

especially resistant to desiccation.At least one <strong>of</strong> the<br />

cocci, S. epidermidis, found in the cinematographic films<br />

produced slime (Me´ ndez-Vilas et al., 2004; Go¨ tz <strong>and</strong><br />

Peters, 2000). S. epidermidis <strong>and</strong> S. hominis are two <strong>of</strong><br />

the most prevalent <strong>and</strong> persistent <strong>bacteria</strong> on human<br />

skin (Schleifer <strong>and</strong> Kloos, 1975; Kloos <strong>and</strong> Schleifer,<br />

1975), S. haemolyticus is usually found in smaller<br />

populations <strong>and</strong> the main habitat <strong>of</strong> S. lugdunensis is<br />

the human nasal cavity where S. haemolyticus can be<br />

also found (Kloos et al., 1992).Most environments<br />

contain transient, small populations <strong>of</strong> staphylococci,<br />

many <strong>of</strong> them probably disseminated by humans or<br />

animals.Mammalian skin is also considered the primary<br />

habitat <strong>of</strong> K. kristinae <strong>and</strong> related micrococci (Cordero<br />

<strong>and</strong> Zumalacarregui, 2000).<br />

The more interesting <strong>of</strong> the two Gram-negative<br />

rods isolated is S. paucimobilis, it is widespread in<br />

nature owing to its physiological <strong>and</strong> metabolic versatility<br />

(Azeredo <strong>and</strong> Oliveira, 2000), most strains produce<br />

an extracellular polysaccharide involved in bi<strong>of</strong>ilm


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formation (Jin et al., 2003), which has been associated<br />

with biodeterioration processes (Azeredo <strong>and</strong> Oliveira,<br />

2000). Bacillus spp.<strong>of</strong> course are ubiquitous, owing to<br />

their wide range <strong>of</strong> physiological characteristics <strong>and</strong><br />

ability to degrade a wide range <strong>of</strong> substrates (Claus <strong>and</strong><br />

Berkeley, 1986), <strong>and</strong> the majority <strong>of</strong> them produce<br />

endospores that are very resistant to environmental<br />

extremes, antibiotics, disinfectants <strong>and</strong> other chemicals<br />

<strong>and</strong>, are easily disseminated.<br />

In the photographic film manufacturing process,<br />

contamination by gelatin-degrading <strong>bacteria</strong> <strong>of</strong> the<br />

genera Bacillus <strong>and</strong> Pseudomonas has been reported<br />

(Stickley, 1986).More recently, it has been demonstrated<br />

that many <strong>bacteria</strong> can colonize gelatin during<br />

its production process.In addition to Bacillus, which are<br />

predominant, non-sporulating <strong>bacteria</strong>l strains identified<br />

as diverse species in the genera Salmonella,<br />

Kluyvera, Burkholderia, Pseudomonas, Yersinia, Brevundimonas,<br />

Enterococcus, Staphylococcus <strong>and</strong> Streptococcus<br />

have been found (De Clerck <strong>and</strong> De Vos, 2002), <strong>and</strong><br />

have the ability to liquefy gelatin. De Clerck et al.(2004)<br />

reported that in semi-final gelatin extracts almost all<br />

<strong>bacteria</strong>l contaminants were Bacillus or other related<br />

endospore formers (Brevibacillus, Geobacillus <strong>and</strong> Anoxybacillus),<br />

although Enterobacter sakazakii <strong>and</strong> Staphylococcus;<br />

S. epidermidis, S.lugdunensis <strong>and</strong> S.hominis<br />

were also identified.These authors concluded that al<br />

least some spores or vegetative cells were able to resist<br />

the final UHT treatment used to prevent the potential<br />

microbial contamination during gelatin manufacture.<br />

Finally, the other important aspect is the presence <strong>of</strong><br />

<strong>bacteria</strong> in indoor environments, including archives.It is<br />

known that vegetative cells or spores <strong>of</strong> endosporeforming<br />

<strong>bacteria</strong> are common contaminants in indoor<br />

environments, where other genera <strong>of</strong> <strong>bacteria</strong>, such as<br />

Kocuria, Micrococcus, Staphylococcus, Aeromonas <strong>and</strong><br />

Pseudomonas have been isolated most frequently, at<br />

least in Central <strong>and</strong> Eastern European countries (Gorny<br />

<strong>and</strong> Dutkiewicz, 2002).<br />

It can therefore be concluded that some cinematographic<br />

films could have been contaminated during<br />

manufacture with vegetative cells <strong>and</strong> especially spores<br />

<strong>of</strong> <strong>bacteria</strong> that perhaps survive the manufacturing<br />

process.Also, since some species <strong>of</strong> Staphylococci are<br />

shed by humans, contamination may be a consequence<br />

<strong>of</strong> h<strong>and</strong>ling during film copying or during maintenance<br />

in the archives.Finally, airborne spores or vegetative<br />

cells in indoor environments, including the archives are<br />

possible contaminants.<br />

3.2. Characterization <strong>and</strong> <strong>identification</strong> <strong>of</strong> filamentous<br />

<strong>fungi</strong> <strong>and</strong> yeasts<br />

A total <strong>of</strong> 17 strains <strong>of</strong> filamentous <strong>fungi</strong> <strong>and</strong> one<br />

yeast were isolated <strong>from</strong> the films (Table 1).The most<br />

frequent genera isolated (Fig.2) were Alternaria<br />

(O’Donnell, 1993) Aspergillus (Klich, 2001) <strong>and</strong> Penicillium.<br />

Other genera observed were Cladosporium,<br />

Mucor, Trichoderma <strong>and</strong> Phoma (Fig.2).<br />

Comparison <strong>of</strong> the ITS rDNA sequences <strong>of</strong> our<br />

strains with the sequences stored in GenBank or in the<br />

proprietary fungal DNA databases showed that the<br />

strain HGC3N was 98% similar to Phoma glomerata<br />

(AY183371); HGC2 was 100% similar to Trichoderma<br />

longibranchiatum CBS446.95 (AY328039); HB1 <strong>and</strong><br />

HB41N were 100% similar to Alternaria alternata<br />

isolate wb571 (AF455406); HB3A 100% similar to<br />

Cladosporium cladosporioides strain ATCC 200941<br />

(AF393691); <strong>and</strong> HM4 100% similar to Mucor racemosus<br />

CBS 260.68 (AY213659).<br />

When the two isolates corresponding to A. alternata<br />

<strong>and</strong> the seven P. chrysogenum isolates were examined<br />

using the microsatellite-primed PCR fingerprinting<br />

technique (Bills et al., 1999), the A. alternata strains<br />

had the same fingerprint (Fig.3) suggesting that they<br />

were identical, so the cinematographic films B1 <strong>and</strong> B4<br />

were contaminated with the same fungal strain.The<br />

P. chrysogenum strains were very similar, although the<br />

pr<strong>of</strong>ile was only identical in the case <strong>of</strong> samples B6 <strong>and</strong><br />

B7 <strong>from</strong> the Barcelona archive indicating a common<br />

source <strong>of</strong> P. chrysogenum contamination for the CTA<br />

<strong>and</strong> CN films.<br />

The most frequent fungal contaminants <strong>of</strong> the films<br />

were airborne <strong>and</strong> soil micromycetes which have a<br />

cosmopolitan distribution <strong>and</strong> can colonize many kinds<br />

<strong>of</strong> surfaces (Florian <strong>and</strong> Manning, 2000; Lugauskas<br />

et al., 2003). A. alternata is well adapted to cold<br />

conditions, with a minimum growth temperature ranging<br />

<strong>from</strong> 51 to 0 1C (Domsch et al., 1980). Penicillium<br />

<strong>and</strong> Aspergillus spp.are ubiquitous taxa that can<br />

produce numerous mitospores, or conidia, which are<br />

easily dispersed by the air.Microorganisms associated<br />

with the airborne route <strong>of</strong> exposure <strong>and</strong> indoor<br />

environment may produce adverse human health effects<br />

<strong>and</strong> therefore, they should be controlled (Gorny <strong>and</strong><br />

Dutkiewicz, 2002). Penicillium, Aspergillus spp.<strong>and</strong><br />

certain species <strong>of</strong> Alternaria are usually found as<br />

contaminants or biodeterioration agents in many<br />

different habitats <strong>and</strong> materials, including those considered<br />

as representative <strong>of</strong> historical <strong>and</strong> cultural<br />

heritage.As already mentioned, the only previous study<br />

about airborne contamination <strong>and</strong> cinematographic<br />

films stored in archives was undertaken in the Slovak<br />

Republic (Opela, 1992), where in the summer months,<br />

the airborne concentration increased remarkably.Also,<br />

the microbial diversity in the air <strong>of</strong> the archives was<br />

higher than on the stored cinematographic films.In<br />

both, the taxa more frequently isolated were species <strong>of</strong><br />

Aspergillus, Penicillium <strong>and</strong> Cladosporium. At least six<br />

species <strong>of</strong> filamentous <strong>fungi</strong> were isolated <strong>from</strong> the films,<br />

including A. versicolor, C. cladosporioides, P. frequentens,<br />

P. lanosum, T. viride <strong>and</strong> Mucor, all <strong>of</strong> which have


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Fig.2.ESEM micrographs <strong>of</strong> different genera <strong>of</strong> <strong>fungi</strong> isolated <strong>from</strong> cinematographic films showing their characteristic hyphae <strong>and</strong> conidia.<br />

Micrographs by J.D. Go´ mez-Varga.


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Fig.3.Microsatellite primed PCR fingerprinting for A. alternata<br />

strains HB1 (lane 2) <strong>and</strong> HB41N (3); P. chrysogenum strains HLV1 (5),<br />

HMI (6), HGC3B (7), HGC1 (8), HB7 (9), HB6 (10) <strong>and</strong> HB41B (11);<br />

(4), (12) control, 100 bp ladder.<br />

oxygen availability.In a previous study (Abrusci et al.,<br />

2004c), it was stated that these gelatinase-positive<br />

<strong>bacteria</strong>l isolates can degrade photographic grade<br />

gelatin (Bloom 225) in aqueous solution (37 1C,<br />

6.67%, w/w) causing progressive viscosity decrease,<br />

with each species showing a characteristic viscosity<br />

decrease pr<strong>of</strong>ile, which changed with temperature.At<br />

4 1C, only B. amyloliquefaciens, B. subtilis, B. pumilus<br />

<strong>and</strong> B. megaterium were able to degrade gelatin aqueous<br />

solution.Nevertheless, in studies <strong>of</strong> several industrial<br />

gelatin production processes (De Clerck <strong>and</strong> De Vos,<br />

2002) <strong>and</strong> semi-final gelatin extracts (De Clerck et al.,<br />

2004), the authors reported that under experimental<br />

conditions the majority <strong>of</strong> isolates exhibited gelatinase<br />

activity.<br />

All filamentous <strong>fungi</strong> isolated in this work were able<br />

to degrade gelatin in the tube test (Table 2), but the<br />

yeast did not, although other strains <strong>of</strong> this species have<br />

been reported as proteolytic (Wade et al., 2003).Unlike<br />

yeasts, filamentous <strong>fungi</strong> are very important microbial<br />

Table 2<br />

Gelatinase activity <strong>of</strong> microbial strains (<strong>bacteria</strong> <strong>and</strong> <strong>fungi</strong>) isolated<br />

<strong>and</strong> identified <strong>from</strong> cinematographic films<br />

Strain Identification Gelatin hydrolysis<br />

been reported as soil <strong>and</strong> airborne <strong>fungi</strong>.The biodiversity<br />

in that research was therefore different <strong>from</strong> that in<br />

our investigation.It might be due to the higher climatic<br />

differences existing between the Spanish archives,<br />

especially if we consider that two <strong>of</strong> them are placed<br />

in coastal areas where environmental humidity is much<br />

higher than in Madrid.<br />

The only yeast isolated was identified as Cryptococcus<br />

albidus, which has been isolated <strong>from</strong> air, soils, <strong>and</strong> a<br />

range <strong>of</strong> habitats, as well as <strong>from</strong> man <strong>and</strong> other<br />

mammals (Barnett et al., 2000).Although in general<br />

terms yeasts cannot survive or develop in habitats with<br />

low water activity.However, it has been reported that C.<br />

albidus var. diffluens shows adaptation to extreme low<br />

humidity (water activity) (Aksenov et al., 1973).<br />

3.3. Gelatin microbial biodegradation tests<br />

In cinematographic films, gelatin degradation is a<br />

highly relevant problem, because it causes the loss <strong>of</strong> the<br />

image.Since some microbial contaminants found in our<br />

film samples were able to grow actively <strong>and</strong> produce<br />

severe deterioration <strong>of</strong> the films, the ability <strong>of</strong> all the<br />

microorganisms isolated <strong>from</strong> cinematographic films to<br />

degrade gelatin was checked. Table 2.Seven <strong>of</strong> the 14<br />

<strong>bacteria</strong>l isolates degraded gelatin in both Petri dish <strong>and</strong><br />

tube hydrolysis tests, six being Bacillus spp.In addition,<br />

S. lentus hydrolysed gelatin in the Petri dish assay, but<br />

not in gelatin test tube assay, perhaps owing to the lower<br />

B3BA Bacillus amyloliquefaciens +<br />

B7 Bacillus megaterium +<br />

GC2 Bacillus megaterium +<br />

M2 Bacillus pichinotyi +<br />

M5 Bacillus pumilus +<br />

B3BS Bacillus subtilis +<br />

M4 Kocuria kristinae<br />

GC1A Pasteurella haemolytica<br />

B4A Sphingomonas paucimobilis<br />

B2 Staphylococcus epidermidis<br />

M3 Staphylococcus haemolyticus<br />

B4C Staphylococcus hominis +<br />

B5 Staphylococcus lentus<br />

a<br />

GC1B Staphylococcus lugdunensis<br />

HB1 Alternaria alternata +<br />

HGC3 Aspergillus versicolor +<br />

HM3 Aspergillus nidulans var. nidulans +<br />

HB2 Aspergillus ustus +<br />

HGC2B Aspergillus ustus +<br />

HB3A Cladosporium cladosporioides +<br />

HM4 Mucor racemosus +<br />

HB41B Penicillium chrysogenum +<br />

HB41N Alternaria alternata +<br />

HB6 Penicillium chrysogenum +<br />

HB7 Penicillium chrysogenum +<br />

HMI Penicillium chrysogenum +<br />

HGC1 Penicillium chrysogenum +<br />

HGC3B Penicillium chrysogenum +<br />

HLV1 Penicillium chrysogenum +<br />

HGC3N Phoma glomerata +<br />

HGC2 Trichoderma longibrachiatum +<br />

LB6 Cryptococcus albidus<br />

+ ¼ positive;— ¼ negative.<br />

a Negative in tube-test but positive in Petri-dish assay.


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Fig.4.Individual film frames (on moist culture medium) showing extreme biodeterioration <strong>of</strong> the image caused by B. subtilis (left) <strong>and</strong><br />

P. chrysogenum (right).<br />

agents <strong>of</strong> biodeterioration; they not only degrade many<br />

kinds <strong>of</strong> molecules <strong>and</strong> materials, but also contribute to<br />

the formation <strong>of</strong> bi<strong>of</strong>ilms.As well as various <strong>bacteria</strong><br />

(mainly Bacillus, Pseudomonas, Sphingomonas), <strong>fungi</strong><br />

such as Alternaria, Trichoderma, Aspergillus <strong>and</strong> Penicillium<br />

have been found to degrade, at least partially,<br />

certain natural proteinaceus materials, e.g. silk (Seves et<br />

al., 1998), keratin (Yamamura et al., 2002) <strong>and</strong> leather<br />

(Orlita, 2004).<br />

Of course, neither presence nor absence <strong>of</strong> gelatinase<br />

activity in the microbial contaminants isolated <strong>from</strong><br />

Spanish cinematographic film is indicative <strong>of</strong> inability to<br />

degrade other components <strong>of</strong> film.Diverse species <strong>of</strong><br />

<strong>bacteria</strong> can degrade cellulose triacetate (Buchanan<br />

et al., 1993; Nelson et al., 1993; Sakai et al., 1996;<br />

Ishigaki et al., 2000), either in conditions <strong>of</strong> aerobiosis<br />

or anaerobiosis <strong>and</strong> there are also fungal biodegraders<br />

(Itävaara et al., 1999; Gu et al., 1993a, b).In all these<br />

studies cellulose triacetate with a higher degree <strong>of</strong><br />

substitution was more resistant to biodegradation<br />

(Buchanan et al., 1993).<br />

3.4. Visual observation <strong>of</strong> cinematographic film<br />

biodeterioration <strong>and</strong> microscopic analysis<br />

Bacterial <strong>and</strong> fungal growth can usually be observed<br />

on the emulsion side <strong>of</strong> film as irregular dull spots.The<br />

spots increase in size <strong>and</strong> number when the material is<br />

left unattended.Eventually, microorganisms can degrade<br />

the emulsion to the point that it is useless.A<br />

degree <strong>of</strong> extreme growth <strong>of</strong> <strong>bacteria</strong> <strong>and</strong> <strong>fungi</strong> on the<br />

side <strong>of</strong> the emulsion is shown in Fig.4.<br />

Microbial growth can be observed on individual<br />

frames between loose coils at the beginning <strong>of</strong> rolls<br />

<strong>of</strong> film <strong>and</strong> also on the margins in the appressed<br />

coils.Damage to the image is not immediate.<br />

If the microbial growth is discovered in time it<br />

is possible to remove it <strong>and</strong> to prevent recurrence.<br />

Continued growth causes permanent damage <strong>and</strong> the<br />

destruction <strong>of</strong> gelatin (Fig.5).The cryogenic fracture <strong>of</strong><br />

the film at 77 K under liquid nitrogen gives a transversal<br />

pr<strong>of</strong>ile <strong>of</strong> the gelatin layer where there are hyphae <strong>of</strong> a<br />

Penicillium.The surface <strong>of</strong> the film material is also<br />

colonized.<br />

4. Conclusions<br />

This investigation has provided evidence that<br />

black <strong>and</strong> white cinematographic films stored in<br />

the Spanish archives are contaminated by diverse<br />

species <strong>of</strong> <strong>bacteria</strong> <strong>and</strong> <strong>fungi</strong>, <strong>and</strong> as judged by the<br />

properties <strong>of</strong> many <strong>of</strong> the microbial isolates, particularly<br />

<strong>fungi</strong>, microbial colonization might result in severe<br />

biodeterioration, including aesthetic variation or<br />

chemical <strong>and</strong> mechanical degradation.Most microorganisms<br />

that were isolated can resist environmental<br />

conditions adverse to microbial life, e.g. desiccation or<br />

nutrient starvation, <strong>and</strong> they can adhere to the<br />

substrates by hyphae or exopolymers.This may give<br />

rise to bi<strong>of</strong>ilm development, increasing the corrosive<br />

action <strong>of</strong> microbial metabolic products.In addition,<br />

some <strong>of</strong> the microbial contaminants can degrade<br />

the gelatin <strong>and</strong> probably other components <strong>of</strong> the<br />

films.Therefore, it is crucial that cinematographic<br />

archives such as museums, historic libraries, etc.have<br />

a strategy for microbiological quality control <strong>of</strong> the<br />

indoor environment in order to prevent, or minimize,<br />

the potential risk <strong>of</strong> microbial colonization <strong>of</strong> the<br />

materials.


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C. Abrusci et al. / International Biodeterioration & Biodegradation 56 (2005) 58–68 67<br />

Fig.5. SEM micrographs <strong>of</strong> artificially inoculated <strong>and</strong> incubated film samples showing Penicillium on a gelatin layer (right), <strong>and</strong> in section produced<br />

by cryogenic fracture at 77 K under liquid nitrogen penetration <strong>of</strong> the material by hyphae.Micrographs by J.D.Go´ mez-Varga.<br />

Acknowledgements<br />

The authors thank Filmoteca Espan˜ ola (ICAA) <strong>and</strong><br />

the film processing company Fot<strong>of</strong>ilm-Madrid, both<br />

part <strong>of</strong> the Consortium for Scientific Collaboration:<br />

CSIC-UCM-FE-FOTOFILM-Madrid, for their financial<br />

support.<br />

References<br />

Abrusci, C., Allen, N.S., Del Amo, A., Edge, M., Martín-González,<br />

A., 2004a. Biodegradation <strong>of</strong> motion picture film stocks. Journal <strong>of</strong><br />

Film Preservation 67, 37–54.<br />

Abrusci, C., Martín-González, A., Del Amo, A., Catalina, F., Bosch,<br />

P., Corrales, T., 2004b. Chemiluminescence study <strong>of</strong> commercial<br />

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