Journal of Natural Science, Biology and Medicine

: 2018  |  Volume : 9  |  Issue : 2  |  Page : 150--158

Characterization of microflora composition and antimicrobial activity of algal extracts from italian thermal muds

Antonella Giorgio1, Federica Carraturo1, Francesco Aliberti1, Salvatore De Bonis2, Giovanni Libralato1, Mario Morra3, Marco Guida1,  
1 Department of Biology, University of Naples Federico II, Naples, Italy
2 Pausilya Therme di Donn'Anna, Naples, Italy
3 ARPA Lazio Sezione Provinciale di Frosinone, Servizio Risorse Idriche e Naturali - Suolo, Rifiuti e Bonifiche, Frosinone, Italy

Correspondence Address:
Federica Carraturo
Department of Biology, University of Naples Federico II, Via Cinthia Ed. 7, Naples


Aim: Fine granular clay, the so-called “peloids,” allowed to ripen for several months in contact with mineral thermal water and the organic substances derived from metabolic activities, represents the basis of thermal mud therapy. A complex microalgal community (Cyanophyceae, Chlorophyceae and Bacillariophyceae) is responsible for the therapeutic effects of thermal muds. Biological components of peloids produce bioactives, possessing anti-inflammatory, antirheumatic and antioxidant properties; for this reason, such matrix is widely used in thermal spas. The research reports results of a preliminary study aimed to characterize the microflora biodiversity of mature and nonmature thermal mud. Algal components were further extracted in order to test the antimicrobial activity of produced bioactive compounds. Materials and Methods: Microscopic, microbiological and molecular techniques were employed (DNA extraction, polymerase chain reaction and sequencing). For antimicrobial activity of algal extracts, Kirby–Bauer disck method was employed. Results: Results show a significant microfloral diversity in samples and a great number of taxa belonging to widely diffused genera such as Leptolyngbya sp., Nostoc sp., Scenedesmus sp., Navicula sp., and Amphora sp. Microbial communities indicate an absolute prevalence of a nonpathogenic flora, mostly composed of Bacillaceae. Conclusion: The association between the microbial and algal composition and the different maturation stages of thermal clay could represent an essential tool to identify markers of proper ripening. This ensures the best product quality and its beneficial properties. The extension of the study, characterizing the components of mud at different ripening times, consents the standardization of ripening process. Antimicrobial activity assay represents a preliminary step for subsequent analysis for the isolation of single component, employing analytical chemistry techniques, characterizing and identifying bioactive compounds of interest.

How to cite this article:
Giorgio A, Carraturo F, Aliberti F, De Bonis S, Libralato G, Morra M, Guida M. Characterization of microflora composition and antimicrobial activity of algal extracts from italian thermal muds.J Nat Sc Biol Med 2018;9:150-158

How to cite this URL:
Giorgio A, Carraturo F, Aliberti F, De Bonis S, Libralato G, Morra M, Guida M. Characterization of microflora composition and antimicrobial activity of algal extracts from italian thermal muds. J Nat Sc Biol Med [serial online] 2018 [cited 2021 Jun 19 ];9:150-158
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Thermal muds have been widely employed since ancient times because of their beneficial effects.[1],[2] Thermal muds are particularly recommended for cosmetic and medical use, treatment of cellulite, treating chronic rheumatic diseases, regeneration of the bones after fractures and as a therapy of chronic infections of bronchi, ear, nose and throat. Technically, muds (or peloids) are sludges derived from the mixture of a solid clay fraction with a thermo-mineral liquid component (cold or warm mineral and thermal water). Thermal water has different geothermic origins, whose action on underground water generates thermo-mineral water having different salinity and temperature values.

The specific properties of thermal muds depend on the mixing process: some examples include the water content, clay consistency and adhesiveness, thermal and exchange capacities, and cooling capabilities. The maturation process occurs in particular containers, where the inorganic, sterilized clay component and thermal water are combined. The mixture is generally kept in constant agitation, at a temperature of 60°C, ensuring constant luminous intensities. This procedure represents the critical stage in the development of the algal and microbial microflora, which will influence the subsequent clay maturation process.[3] The high variability in the chemical and physical parameters of the clays and the different thermal water is responsible for the thermal muds' high diversity of microorganisms, such as bacteria, protozoans, microalgae and cyanobacteria..[4],[5],[6] The organic component, produced by the biological metabolism, can trigger mud maturation and confer specific healing properties.[7],[8] In terms of biomass, cyanobacteria constitute the most abundant organisms able to colonize thermal muds. In addition, as pioneer species, they can form large-sized biofilms on the colonized surface. Scientific studies indeed demonstrated the connection between cyanobacteria and the production of several bioactive compounds, such as phycocyanins, flavonoids, unsaturated fatty acids and exopolysaccharides, which can be exploited in different ways, mostly for medical treatments.[9],[10] Previous researches demonstrated the antioxidant activity of flavonoids and the anti-inflammatory and antitumoral properties of phycocyanins.[11] The aim of this study was to characterize, using morphological, microbiological and molecular techniques, the microalgal and microbial flora typical of thermal muds, which is responsible for ripen muds' healing properties. The experimented analytical approach is based on the evaluation of thermal muds' quality during the maturation process in order to establish the effectivity of established ripening times, disposing of two thermal muds, sampled at different maturation times. The analysis was first performed through the isolation and characterization of microalgae and natural microbial flora using morphological and microscopic methodologies. The same samples were then analyzed employing genomic techniques: thermal mud genomic DNA was extracted and amplified with specific primer by polymerase chain reaction (PCR) to highlight the differences between the several mud maturation times.

In order to analyze the antimicrobial activity of algal compounds against specific bacterial strains, an organic extraction protocol was employed.

The research has been conducted in collaboration with Pausilya Therme di Donn'Anna, thermal SPA (Naples, Regione Campania, Italy), in the framework of mining operation permits. A standardized protocol for the evaluation of thermal muds' ripening process has not been developed yet, as well as specific regulations were not defined. A system able to objectively indicate the characteristics of thermal muds, based on the microalgal biodiversity and abundance, would ensure the quantitative evaluation of mud maturation levels and therefore the quality of the mud, in terms of therapeutic efficacy and beneficial properties.

 Materials and Methods

Sampling and laboratory cultivation

Mud samples were collected aseptically from tanks located in a thermal SPA of Naples. The two samples are indicated as “1-month mud,” referred to thermal mud allowed to ripen for 1 month and “6-month mud,” describing a sample allowed to ripen for 6 months. For every 20 days, from January to July 2016, we collected muds, disposing a totality of ten samples of each mud type.

Samples were stored at 4°C until they were processed in the laboratory (within 12 h). All mud samples were homogenized in sterile conditions and submitted for microbiological, microscopic and molecular analyses.

Analysis of microalgal community

An aliquot of 5 g from samples was weighed into sterile flasks and inoculated with 50 ml of specifying enrichment media, to allow microalgae growth. For the isolation of cyanobacteria, green algae and diatoms, Blue-Green 11,[12] Bold Basal,[13] and WC [14] media were used. The inoculated samples were incubated in a growth chamber at 30°C ± 2°C with a light intensity of 7.6 W/m2 (photosynthetically active radiation) and a dark/light cycle of 12/12. Three weeks after the beginning of incubation, microalgae biofilms were collected and transferred to new media, to avoid microalgal death. In order to isolate single microalgal species, an aliquot (100 μL) of algae mixture was plated, using sterile technique, onto the surface of a Petri plate containing agarized algal growth medium.[15] Inoculated plates were placed in the same condition of liquid culture until the growth of algal colonies. Colonies of different morphologies and color were collected and aseptically inoculated in the liquid medium. This procedure was repeated until achievement (the setup) of monoalgal cultures, which were used in the following laboratory analysis.

Microscopic analysis

Microscopic analysis of cyanobacteria and green algae, in living state, was made with an optical microscope, equipped with a digital image acquisition system (Leica DM4 B). Morphological features (such as chloroplast shape, cell dimension and colonies' structure) were observed at ×400, ×600 and ×1000 magnifications for the identification of genera and species. The identification of algae required standardized taxonomic literature.[16]

Samples for diatom analyses were cleaned with 30% hydrogen peroxide solution to remove organic material [17] before their mounting on microscope slides in a highly refractive medium (Naphrax Resine, Northern Biological Supplies Ltd., UK; refractive index=1.74). Diatom taxa were identified following the Krammer and Lange–Bertalot monographs,[18],[19] as well from the Krammer [20] and Lange–Bertalot [21],[22] monographs.

Total bacterial count isolation

Total bacterial count analysis was performed according to ISO 4833-1:2013, which includes pouring 1 mL from the thermal mud sample in plate count agar (PCA) (Oxoid, Thermo Fisher Scientific, USA). PCA plates were then incubated at 30°C ± 1°C for 72 h. The totality of colonies was counted. Different morphology colonies were subcultured in fresh PCA agar, reconstituted with 50 μL Milli-Q Type 1 ultrapure water and submitted for molecular analysis, in order to identify each bacterial strain.

Molecular analysis

Individually isolated microalgae cells and bacterial colonies were analyzed by molecular techniques too. DNA extraction procedure of Doyle and Doyle (1987) was performed.[23] Purity and quality of the extracted DNA were analyzed on a 0.8% agarose gel with 0.5% TAE buffer, stained with GelRed (GelRed Nucleic Acid Gel Stain, Biotium). DNA quantification was performed with spectrophotometer NanoDrop 2000 (Thermo Fisher Scientific). PCR amplification was carried out using four sets of primers [Table 1] specific for 16S rDNA for bacteria (Primer set 1), 16 rDNA for Cyanophyceae (Primer set 2), 18S rDNA for Chlorophyceae (Primer set 3) and 18S rDNA for Bacillariophyceae (Primer set 4).[24],[25],[26] All the PCR reactions were set up using a Prime Thermal Cycler (Techne) at a total volume of 50 μL containing 5 ng of DNA, 5 μL of 10X reaction buffer, 1.5 mM MgCl2, 0.2 mM of each dNTP, 0.2 μM of each primer and 2 U of Taq DNA polymerase (VWR Chemicals, Milan, Italy). The PCR amplifications were performed according to the bibliography indication.[24],[25],[26],[27] An aliquot (5 μL) of PCR products was electrophoresed in 1.5% agarose gel at a voltage of 70 V for 1 h. Gels were stained with GelRed (GelRed Nucleic Acid Gel Stain, Biotium) and visualized under ultraviolet illuminator, using a 100 bp DNA ladder (DNA Molecular Weight ladders, Amresco) as size marker. Purified PCR products (polyethylene glycol precipitation protocol) were used as templates in sequencing reaction with the BigDye Terminator V3.1 (Applied Biosystems, USA) following manufacturer's procedure. Sequencing was performed using an ABI Prism 3100 (Applied Biosystems) and sequences were analyzed with Chromas Lite software, version 2.1.1. (Chromas Lite version 2.1, Technelysium; http://technelysium. com. au/?page_id=13, Technelysium Pty Ltd Unit 406 8 Cordelia St South Brisbane QLD 4101 Australia) and submitted for Blast analysis to taxonomic affiliation.{Table 1}

Algal material extraction

Algal cultures were collected after 15 days' growth and filtered through Whatman filter paper No. 2 (Whatman International Ltd., Maidstone, UK) for isolation of the cells from the culture medium. The algal communities extracted from the muds under analysis were cleaned up in tap water and rinsed several times in distilled water. The algal samples were allowed to dry in air and stored in 15 mL tubes at room temperature. The algal materials were soaked in different solvents within 50 mL tubes (3 g dry algae/25 mL solvent), kept on a shaker at 150 rpm at room temperature (30°C) for 24 h. In order to analyze the activity of all organic components, four solvents were used: chloroform, ethanol, hexane and methanol. The samples were then filtered by Whatman No. 1 filter paper: filtrates were dried under reduced pressure at 40°C, using a Rotavapor® R-300 (BUCHI). Dried pellets were then dissolved in 5 mL dimethylsulfoxide. Extracts were filtered using 0.2 μm Millipore filter and stored at −20°C until antimicrobial testing.[28],[29]

Antimicrobial activity assay

The antimicrobial activity of mud algae extracts was evaluated against Gram-positive and Gram-negative bacteria. The organisms used in this study were ATCC® strains. The following five bacteria were used for antimicrobial assay: Escherichia coli ATCC® 8739™, Klebsiella pneumoniae ATCC® 13833™, Pseudomonas aeruginosa ATCC® 9027™, Staphylococcus aureus ATCC® 25923™ and Streptococcus pyogenes ATCC® 19615™.

Pathogenic bacteria were grown in Tryptone Soya Broth – OXOID, in 15 mL centrifuge tubes at 37°C, obtaining a 1 × 106 cells/mL concentration. Disc method as indicated by Bauer et al. was employed. Microorganisms, grown at a 106 cells/mL concentration, were plated, using a sterile swab, in Petri dishes containing Tryptone Soya Agar – OXOID. In the meanwhile, sterile discs of 6 mm diameter (antimicrobial susceptibility testing – OXOID) were soaked with 25 μl of the algal extracts (4 μg/μl), as for extracted samples, or with the used solvents, for negative controls: the prepared discs were added to the dishes spread with each of the five bacteria under analysis. Petri dishes were incubated for 24 h at 37°C and the toxic effects of algal bioactive compounds against microorganisms were determined by measuring the diameter of the halo developed around the discs. The experiments were performed in triplicate. Highly representative halos were those producing a halo with a 10 mm or higher diameter. For positive control, chloramphenicol was employed.


Overall, seven taxa of green algae, two taxa of cyanobacteria and seven taxa of diatoms were observed in both samples [Table 2]. Regarding microalgal community, sample of muds allowed to ripen for 6 months (6-month mud) presented a higher biodiversity compared to the mud allowed to ripen for 1 month (1-month mud). The dominant groups were represented by Chlorophyceae (seven taxa) and Bacillariophyceae (seven taxa). Microscopic analysis based on the observations of morphological characteristics (size and shape of cells, chloroplast and the presence of wall ornamentation) have revealed the presence of some genera and species of microalgae and diatoms, such as Leptolyngbya sp., Nostoc sp., Chlorella sp., Coccomyxa sp., Cocconeis placentula, Amphora sp. And Rhoicosphenia abbreviata [Figure 1] and [Figure 2].{Table 2}{Figure 1}{Figure 2}

On light microscopy, Leptolyngbya is typified by cells organized into long, solitary, or coiled into clusters and filaments. Filaments are arcuated, waved, or intensely coiled, isopolar, thin and fine, with usually colorless facultative sheaths opened at the apical end. Cells are isodiametrical or longer than wide (up to several times), cylindrical, with homogeneous content and pale blue-green, grayish, olive-green, yellowish, or reddish. Nostoc cells, observed at microscope, appear cylindrical, spherical, or ovoid (barrel shaped) and are not shorter than broad. Cells are organized in trichomes and spherical or ovoid gelatinous thalli are often visible. Chlorella cells are spherical, subspherical, or ellipsoid and single or colony forming. A defining feature of the genus is the single and parietal chloroplast with a pyrenoid surrounded by starch grains. Coccomyxa cells are easily recognizable by green nonflagellated colonies and by laminated layers of secreted mucilage-surrounded cells.

The oxidation treatment, using hydrogen peroxide, proved to be valuable to morphological identification of diatoms. On light microscope, valves of Cocconeis placentula result elliptic to linear-elliptic and relatively flat, with a filiform rafe, a narrow axial area and a small circular or oval central area. Distinctive elements are striae radiate and the hyaline ring positioned close to valve margin. Rhoicosphenia abbreviata valves appear clavate or club shaped with rounded apices. Frustules, in girdle view, are distinctly arched and heteropolar. Amphora valves result lunate, presenting the dorsal margin much deeper than the ventral. The raphe toward ventral margin is sinuous to strongly arcuate. The dorsal margin sometimes has hyaline areas. Surirella valves appear, under microscope, heteropolar, with headpole rounded and footpole cuneately rounded. The valves are slightly concentrically undulate. The costae extend from the margins to the apical axis and fibulae are marginal.

Molecular assays allowed the characterization of thermal muds' microflora which confirmed the morphological outcomes. The most abundant benthic microalgae taxa, identified in both samples, are Chlorella sp., Coccomyxa sp., Scenedesmus sp., Leptolyngbya sp., Anabaena sp., Cocconeis placentula, Rhoicosphenia abbreviata and Navicula cincta. Nostoc sp., Scenedesmus sp., Chlamydomonas sp., Pseudococcomyxa simplex, Monodus sp., Gomphonema acuminatum, Amphora ovalis and Nitzschia palea were isolatedexclusively from ripen mud.

Bacteria were characterized and selected for molecular analysis with respect to the morphology of the colonies. Isolated bacterial strains are listed in [Table 2]. As for microalgal communities, ripen mud presented a higher biodiversity in terms of genera and species isolated. Bacterial DNA characterization allowed the identification of 13 bacterial taxa. Among these, five were isolated from 1-month mud and eight from 6-month mud. An 85% isolation rate belongs to the Bacillaceae family, while one taxa of Pseudomonas sp. and one of Paenibacillus sp. were, respectively, identified from 1-month and 6-month mud. Comparing the isolates, Bacillus sp., Bacillus subtilis and Bacillus thuringiensis wereisolated from both samples.

The bacterial isolates of the 1-month mud and of the 6-months mud, obtained using different solvents, have showed a different activity against the bacterial microorganisms under analysis [Figure 3]. Positive controls with chloramphenicol showed 20 mm halos using 4μg/μl concentrations and pouring the discs with 25 μl solutions (same as algal extracts).{Figure 3}

For a better comprehension of the toxic effect on bacterial inocula, a scoring system was generated: whether no effect was observed, corresponding to a <6 mm halo, a “—” was used; when the zone of inhibition was between 6 and 8 mm, a “+” score was assigned, indicating a low inhibition effect; a good effect of the extract, with an 8–10 mm inhibition zone, was indicated with “++;” an inhibition zone >10 mm, indicating a really good effect, was classified as triple-positive symbol, “+++” [Table 3].{Table 3}

Analyzing the activity of the 1-month-mud extract, the methanol extraction evidenced antimicrobial activities only against Klebsiella pneumoniae [Figure 3]a.

The extracts resulting from algal components of the 6-month-mud highlighted a various and different antimicrobial capability with the microbial strains tested. Extracts from chloroform protocol showed activity against all bacterial strains, excepting Klebsiella pneumoniae. In particular, the largest inhibition halo – <10 mm – was registered for P. aeruginosa [Figure 3]f. Methanol extraction allowed the evaluation of a good inhibition activity of the ripen mud algal extract against Staphylococcus aureus and Klebsiella pneumoniae, with inhibition halos comprised between 8 and 10 mm [Figure 3]b. The extractions performed using ethanol and hexane did not show microbial growth inhibition for both algal extracts (1-month-mud and 6-month-mud) against the microorganisms' inocula under analysis.


The protocols adopted, based on microscopic and molecular analyses, were proven to be valuable for the identification and characterization of thermal muds' microflora and to associate the maturation process to the microalgal composition. Liquid and solid cultural methods, followed by morphological observations, employing optical microscope, allowed the identification of some of the isolated microalgal species belonging to the photosynthetic biomass, in particular, Cyanophyceae, Chlorophyceae and Bacillariophyceae. The molecular analysis confirmed the presence of the taxa which have been characterized at the microscope and consented the identification of microorganisms of difficult taxonomic classifications.

The analysis carried out on the muds allowed to ripen for 6 months evidenced a higher biological complexity. Considering that the evaluated samples have an environmental origin, during the maturation process, it is possible to observe the differentiation of the investigated consortia, expressed in terms of quantitative and/or qualitative variation of the biodiversity.

The results of the antimicrobial activities evidenced differences considering the extraction matrix (maturation levels) and the solvent type. Differences reside in the different extraction capabilities of the solvents; the different susceptibility of the analyzed strains toward the extracted metabolites (also depending on the varying virulence of the pathogenic bacteria).[30] Indeed, methanol is indicated for the extraction of polar molecules, such as proteins, while chloroform, with a lower polarity, consents the extraction of the grease component. The lack of efficacy of ethanol and hexane extraction could be linked to the rapid volatility of the two solvents or to the low antimicrobial activity of the extracted components, against the pathogens tested. It can be hypothesized to combine solvents in mixes in order to optimize the extraction process, widening the recovery of type of bioactive compounds.

The results indicate a higher concentration of metabolically active compounds, in continuous development because of the enrichment of the biological components produced by the thermal mud (bacteria, cyanobacteria, green algae and diatoms). The isolation of Cyanophyceae, Chlorophyceae and Bacillariophyceae, overall nonpathogenic microorganisms, was confirmed by similar studies,[10],[31] reporting that the metabolic activities of such microorganisms are responsible for the production of fatty acids, lipids and other macromolecules, having therapeutic properties. The microalgal diversity of the investigated thermal muds seems to be responsible for their beneficial activity. Some genera of Chlorophyceae, Cyanophyceae and Bacillariophyceae, such as Nostoc sp., Anabaena sp., Leptolyngbya sp., Coccomyxa sp. and Chlorella sp., isolated from the analyzed samples, are known to have important properties.

Among cyanobacteria, Leptolyngbya, Nostoc and Anabaena could exhibit bioactivity and produce interesting compounds and molecules capable of inducing cytotoxic effect in human cancer lines;[32],[33] such microorganisms indeed have potential applications in pharmaceutics.[34] A study conducted by Gustafson et al. (1989) reported the isolation of anti-HIV molecules (active sulfoglico lipids) from strains of Anabaena sp. Some species of Nostoc sp., are proved to produce antiviral proteins and lipophilic extracts with antibacterial activity.[35] According to Takara et al., 1990 and Kravolec et al., 2007, Chlorella algal extract could have antitumoral and anti-immunostimulatory activities.[36] Polysaccharidic extract of some Coccomyxa strains has demonstrated efficacy against the influenza A virus infection.[37] Among diatoms, Navicula and Amphora were widely investigated for their antioxidant activities.[38]

The isolated microbial strain results confirm previous researches reporting Bacillaceae and Paenibacillaceae as the most frequently identified bacterial species from geothermal environments.[39] Bacillaceae, Gram-positive, aerobic and rod-shaped microorganisms [40] are frequently isolated from water and soils and generally do not represent a health risk for the consumers. Bacillaceae, indeed, have been employed for decades as probiotics and, because of their ability to germinate in the gastrointestinal tract, producing bacteriocins and antibiotics acting toward pathogens, they are widely employed for biotechnology applications. Some examples of the strains showing antimicrobial activity are Bacillus cereus, Bacillus clausii, Bacillus subtilis and Bacillus licheniformis (The last two species were both isolated from the thermal muds under evaluation).[41]Bacillus have been demonstrated to produce carotenoids, the most abundant pigment group in nature,[42],[43] owning anticancer, anti-inflammatory and anti-oxidative properties. Bacillus spp., metabolism additionally enables the efficient production of purine nucleosides and vitamins. Bacillus subtilis, Bacillus amyloliquefaciens, Bacillus licheniformis and Bacillus megaterium are largely exploited as producers of vitamins such as cobalamin, riboflavin, folic acid and biotin.[44],[45],[46],[47]

Monitoring for pathogens considered fecal indicators which was moreover crucial to determine thermal mud safety, considering that the detection of such opportunistic pathogens in groundwater can represent an indication of contamination of surface waters. The isolation of fecal indicators in thermal waters employed for the treatment of pathologies involving the elderly, patients affected with various chronic conditions and, in general, immune-compromised individuals, constitutes a substantial health risk.[48] Strains having fecal origin, such as Escherichia coli or Clostridium perfringens, were not detected. One strain of Pseudomonas sp., a nonfecal microorganism, was isolated from the 1-month mud sample. The health risk connected to Pseudomonas genus is related to P. aeruginosa species, for which strict tolerance levels in case of isolation in bathwaters are allowed.[49] Hence, the isolation of a non-P. aeruginosa species does not represent a risk for the customers.


Based on the obtained results, further characterization of the bioactive compounds produced by the isolated microalgal species during the mud-ripening stages will confirm the effectiveness of the mud therapy. The available data reported the major microflora isolated from the 6-month-mud, not only in terms of abundance but also with respect to biodiversity and previous researches demonstrated the therapeutical efficacy of the microalgal flora isolated from the thermal clays under analysis: the combination of the results confirms the reliability of mud microorganism characterization to define ripening markers. Furthermore, the disposal of a method able to evaluate the maturation stages, through the identification of marker microorganisms, and to define the proper ripening times, could provide a precious contribution for the optimization of the maturation itself, aiming to the standardization of thermal muds' maturation process. Hence, thermal muds at the end of maturation process represent an important source of bioactive compounds, which can be employed as antimicrobials. Further studies, employing analytical chemistry techniques, will allow the identification of the active molecules responsible for the antibacterial activities.


This research was supported by a grant from the University of Naples “Federico II,” Department of Biology, Hygiene Laboratories, Italy. Pausilya Therme di Donn'Anna provided the samples and ensured the proper ripening times, useful to proceed with evaluations.

Financial support and sponsorship


Conflicts of interest

There are no conflicts of interest.


1Summa V, Tateo F. Geochemistry of two peats suitable for medical uses and their behavior during leaching. Appl Clay Sci 1999;15:477-89.
2Viseras C, Lopez Galindo A. Pharmaceutical applications of some Spanish clays (sepiolite, palygorskite, bentonite): Some preformulation studies. Appl Clay Sci 1999;14:69-82.
3Centini M, Tredici MR, Biondi N, Buonocore A, Maffei Facino R, Anselmi C, et al. Thermal mud maturation: Organic matter and biological activity. Int J Cosmet Sci 2015;37:339-47.
4Tolomio C, Ceschi-Berrini C, Moschin E, Galzigna L. Colonization by diatoms and antirheumatic activity of thermal mud. Cell Biochem Funct 1999;17:29-33.
5Tolomio C, Ceschi-Berrini C, De Apollonia F, Galzigna L, Masiero L, Moro I, et al. Diatoms in the thermal mud of Abano Terme, Italy (Maturation peloid). Arch Hydrobiol Suppl Algol Stud 2002;105:11-27.
6Tolomio C, De Apollonia F, Moro I, Ceschi-Berrini C. Thermophilic microalgae growth on different substrates and at different temperature in experimental tanks in Abano Terme (Italy). Arch Hydrobiol Suppl Algol Stud 2004;111:145-57.
7Tserenpil S, Dolmaa G, Voronkov MG. Organic matters in healing muds from Mongolia. Appl Clay Sci 2010;49:55-63.
8Suárez M, González P, Domínguez R, Bravo A, Melián C, Pérez M, et al. Identification of organic compounds in San Diego de Los Baños Peloid (Pinar del Río, Cuba). J Altern Complement Med 2011;17:155-65.
9Eriksen NT. Production of phycocyanin – A pigment with applications in biology, biotechnology, foods and medicine. Appl Microbiol Biotechnol 2008;80:1-4.
10Sivonen K, Börner T. Bioactive compounds produced by cyanobacteria. In: The Cyanobacteria: Molecular Biology, Genomics and Evolution. Norfolk: Caister Academic Press; 2008. p. 159-97.
11Cao G, Sofic E, Prior RL. Antioxidant and prooxidant behavior of flavonoids: Structure-activity relationships. Free Radic Biol Med 1997;22:749-60.
12Castenholz RW. Culturing methods for cyanobacteria. Method Enzymol 1988;167:68-93.
13Bischoff HW, Bold HC. Some Soil Algae from Enchanted Rock and Related Algal Species. Phycological Studies IV. University of Texas; 1963. p. 1-95.
14Guillard RR, Lorenzen CJ. Yellow-green algae with chlorophyllide C. J Phycol 1972;8:10-4.
15Lee K, Eisterhold ML, Rindi F, Palanisami S, Nam PK. Isolation and screening of microalgae from natural habitats in the Midwestern United States of America for biomass and biodiesel sources. J Nat Sci Biol Med 2014;5:333-9.
16Van den Hoeck C, Mann DG, Jahns HM. Algae: An Introduction to Phycology. Cambridge: University Press, Cambridge; 1995. p. 627.
17APAT. Campionamento ed analisi delle diatomee bentoniche dei corsi d'acqua. Metodi Biologici Per le Acque – Parte 1. 2007.
18Krammer K, Lange-Bertalot H. SüBwasswasserflora von Mitteleuropa, Bacillariophyceae 3, Centrales, Fragilariaceae, Eunotiaceae. Stuttgart: Gustav Fischer Verlag; 1991. p. 576.
19Krammer K, Lange-Bertalot H. SüBwasswasserflora von Mitteleuropa, Bacillariophyceae 4, Achnanthaceae, Literaturverzeichnis. Stuttgart: Gustav Fischer Verlag; 1991. p. 437.
20Krammer K. Diatoms of Europe. Diatoms of the European inland waters and comparable habitats. Cymbella. Vol. 3. Kapellenbergstr. 75, DE - 61389 Oberreifenberg / Germany: A.R.G. Gantner Verlag, K.G, Ruggell; 2002. p. 530.
21Lange-Bertalot H. 85 New Taxa, 2/1-4. Berlin: J. Cramer; 1993. p. 453.
22Lange-Bertalot H. Diatoms of Europe. Diatoms of the European inland waters and comparable habitats. Navicula Sensu Stricto. 10 Genera Separated from Navicula Sensu Lato. Frustulia. Vol. 2. Kapellenbergstr. 75, DE - 61389 Oberreifenberg / Germany: A.R.G. Gantner Verlag, K.G., Ruggell; 2001. p. 526.
23Doyle JJ, Doyle JL. A rapid DNA isolation procedure from small quantities of fresh leaf tissue. Phytochem Anal 1987;19:11-5.
24Nübel U, Garcia-Pichel F, Muyzer G. PCR primers to amplify 16S rRNA genes from cyanobacteria. Appl Environ Microbiol 1997;63:3327-32.
25Díez B, Pedrós-Alió C, Marsh TL, Massana R. Application of denaturing gradient gel electrophoresis (DGGE) to study the diversity of marine picoeukaryotic assemblages and comparison of DGGE with other molecular techniques. Appl Environ Microbiol 2001;67:2942-51.
26Chakravorty S, Helb D, Burday M, Connell N, Alland D. A detailed analysis of 16S ribosomal RNA gene segments for the diagnosis of pathogenic bacteria. J Microbiol Methods 2007;69:330-9.
27Moro CV, Crouzet O, Rasconi S, Thouvenot A, Coffe G, Batisson I, et al. New design strategy for development of specific primer sets for PCR-based detection of chlorophyceae and bacillariophyceae in environmental samples. Appl Environ Microbiol 2009;75:5729-33.
28Lima-Filho JV, Carvalho AF, Freitas SM, Melo VM. Antibacterial activity of extracts of six macroalgae from the northeastern Brazilian coast. Braz J Microbiol 2002;33:311-3.
29Omar HH, Shiekh HM, Gumgumjee NM, El-Kazan MM, El-Gendy AM. Antibacterial activity of extracts of marine algae from the Red Sea of Jeddah, Saudi Arabia. Afr J Biotechnol 2012;11:13576-85.
30Inci T, Bilge Hilal C, Dilek U, Atakan S. Antimicrobial activities of the extracts of marine algae from the coast of Urla (Izmir, Turkey). Turk J Biol 2006;30:171-5.
31Gerwick L, Gerwick WH, Coates RC, Engene N, Grindberg RV, Jones AC, et al. Giant marine cyanobacteria produce exciting potential pharmaceuticals. Microbe 2008;3:277-84.
32Surakka A, Sihvonen LM, Lehtimäki JM, Wahlsten M, Vuorela P, Sivonen K, et al. Benthic cyanobacteria from the Baltic sea contain cytotoxic Anabaena, Nodularia, and Nostoc strains and an apoptosis-inducing phormidium strain. Environ Toxicol 2005;20:285-92.
33Costa M, Garcia M, Costa-Rodrigues J, Costa MS, Ribeiro MJ, Fernandes MH, et al. Exploring bioactive properties of marine cyanobacteria isolated from the Portuguese coast: High potential as a source of anticancer compounds. Mar Drugs 2013;12:98-114.
34Pagliara P, Caroppo C. Cytotoxic and antimitotic activities in aqueous extracts of eight cyanobacterial strains isolated from the marine sponge Petrosia ficiformis. Toxicon 2011;57:889-96.
35Jaki B, Orjala J, Heilmann J, Linden A, Vogler B, Sticher O, et al. Novel extracellular diterpenoids with biological activity from the Cyanobacterium nostoc commune. J Nat Prod 2000;63:339-43.
36Kralovec JA, Metera KL, Kumar JR, Watson LV, Girouard GS, Guan Y, et al. Immunostimulatory principles from Chlorella pyrenoidosa – Part 1: Isolation and biological assessment in vitro. Phytomedicine 2007;14:57-64.
37Komatsu T, Kido N, Sugiyama T, Yokochi T. Antiviral activity of acidic polysaccharides from Coccomyxa gloeobotrydiformi, a green alga, against an in vitro human influenza A virus infection. Immunopharmacol Immunotoxicol 2013;35:1-7.
38Karawita R, Senevirathne M, Athukorala Y, Affan A, Lee YJ, Kim SK, et al. Protective effect of enzymatic extracts from microalgae against DNA damage induced by H2O2. Mar Biotechnol (NY) 2007;9:479-90.
39Logan NA, Lebbe L, Hoste B, Goris J, Forsyth G, Heyndrickx M, et al. Aerobic endospore-forming bacteria from geothermal environments in Northern Victoria Land, Antarctica, and Candlemas Island, South Sandwich Archipelago, with the proposal of Bacillus fumarioli sp. Nov. Int J Syst Evol Microbiol 2000;50(Pt 5):1741-53.
40Goto K, Omura T, Hara Y, Sadaie Y. Application of the partial 16S rDNA sequence as an index for rapid identification of species in the genus bacillus. J Gen Appl Microbiol 2000;46:1-8.
41Sansinenea E. Bacillus Thuringiensis Biotechnology. Netherlands: Springer Science and Business Media; 2012. p. 392.
42Khaneja R, Perez-Fons L, Fakhry S, Baccigalupi L, Steiger S, To E, et al. Carotenoids found in bacillus. J Appl Microbiol 2010;108:1889-902.
43Perez-Fons L, Steiger S, Khaneja R, Bramley PM, Cutting SM, Sandmann G, et al. Identification and the developmental formation of carotenoid pigments in the yellow/orange bacillus spore-formers. Biochim Biophys Acta 2011;1811:177-85.
44Yu WB, Gao SH, Yin CY, Zhou Y, Ye BC. Comparative transcriptome analysis of bacillus subtilis responding to dissolved oxygen in adenosine fermentation. PLoS One 2011;6:e20092.
45Sheremet AS, Gronskiy SV, Akhmadyshin RA, Novikova AE, Livshits VA, Shakulov RS, et al. Enhancement of extracellular purine nucleoside accumulation by bacillus strains through genetic modifications of genes involved in nucleoside export. J Ind Microbiol Biotechnol 2011;38:65-70.
46Zhang J, Zhou J, Liu J, Chen K, Liu L, Chen J, et al. Development of chemically defined media supporting high cell density growth of Ketogulonicigenium vulgare and Bacillus megaterium. Bioresour Technol 2011;102:4807-14.
47Eppinger M, Bunk B, Johns MA, Edirisinghe JN, Kutumbaka KK, Koenig SS, et al. Genome sequences of the biotechnologically important Bacillus megaterium strains QM B1551 and DSM319. J Bacteriol 2011;193:4199-213.
48Amarouche-Yala S, Benouadah A, Bentabet AO, Moulla AS, Ouarezki SA, Azbouche A. Physicochemical, bacteriological, and radiochemical characterization of some Algerian thermal spring waters. Water Qual Expo Health 2015;7:233-49.
49Thorolfsdottir BO, Marteinsson VT. Microbiological analysis in three diverse natural geothermal bathing pools in Iceland. Int J Environ Res Public Health 2013;10:1085-99.