Marine Bacterial Genus Euzebya in Terrestrial Environments: History
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Euzebya and other haloalkaliphilic bacteria can thrive under harsh conditions, such as high concentrations of sodium and/or calcium, high electric conductivity and alkaline pH, highly variable temperatures, and water fluctuations. These conditions are quasi-extreme in the studied terrestrial environments. 

  • biofilms
  • caves
  • soils
  • Euzebya

1. Introduction

In terms of microbial diversity, the oceans represent the largest biosphere habitat, containing about 70% of the prokaryotic biomass [1]. In recent decades, interest in the bioactive compounds from marine bacteria has grown enormously [2][3][4][5][6][7][8], and many works have focused on rare marine Actinomycetota [9][10][11][12][13]. One of the most intriguing and rare genera of marine Actinomycetota is Euzebya. No terrestrial Euzebya has been isolated so far.
The genus Euzebya was described by Kurahashi et al. [14] to accommodate a Gram-positive actinobacterial strain isolated from the epidermis of Holothuria edulis, a sea cucumber collected in the Sea of Japan. The strain was characterized by a reddish-orange or tangerine color and was able to grow in sodium chloride concentrations of 0.5–12%, but no growth was observed in the absence of sodium chloride or at a concentration of 15%. Optimal growth temperatures were in the range of 20–28 °C and pH 7–9. No growth was obtained at pH 6 or 10. The type strain is Euzebya tangerina from the new order Euzebyales and the new family Euzebyaceae [14]. A second member of the genus, Euzebya rosea, was isolated from the waters of the East China Sea and showed a light pink color, optimal growth at 25–30 °C, and pH 6–7. Optimal sodium chloride concentrations were 1–4% [15].
Euzebya pacifica was the third species of the genus, isolated from seawater collected at 150 m depth in the Eastern Pacific Ocean [16]. Colonies were pink, with optimal growth at 30–35 °C, in sodium chloride concentrations of 1–2%, and pH 6.5. This last species could grow in the absence of sodium chloride. The complete genome sequence of E. pacifica revealed its ecological roles in marine carbon, nitrogen, phosphorus, and sulfur cycles [17]. In general, the three marine species of Euzebya are characterized by their tolerance to relatively high sodium chloride concentrations, growth at neutral pH (7), and temperatures from 20 to 35 °C.
The advent of molecular tools, particularly next-generation sequencing (NGS), has dramatically changed the knowledge of the diversity of microbial life on Earth. In recent decades, many studies on different terrestrial environments, including caves [18][19][20][21][22][23][24][25][26][27][28][29][30][31][32][33][34][35][36], have described the diversity and abundance of Euzebyales/Euzebyaceae/Euzebya; however, as far as we know, no Euzebya isolates have been obtained from terrestrial niches.

2. Metagenomic Detection of Euzebya in the Environment: Caves

Caves are mineral environments, often oligotrophic in nature. Rocks, speleothems, and mineral deposits, such as moonmilk, are colonized by microbial communities, which develop as colored biofilms [18][19][20]. To our knowledge, the first report on the occurrence of Euzebya in caves was in a study by Cuezva et al. [18]. In Altamira Cave, Spain, sequences with 82–92% similarity to the nearest relative Euzebya tangerina were retrieved from grey biofilms, suggesting that they probably represented an unknown species. Euzebya represented 72.8% of the clones retrieved from the grey biofilms [18]. Riquelme et al. [19] recovered representatives of Euzebyales from colored microbial mats found in volcanic caves in the Azores, Hawai’i, and New Mexico, and stated that the different clades obtained suggested a significant diversity within the sequences found. Other papers reported Euzebya sequences from caves in different geographical regions [21][22][23][24][25][26][27][28][29][30][31][32][33][34][35][36].
The composition of microbial communities was found to be dependent on geochemical and microclimatic parameters. In this context, Frazier [29] reported the high relative abundance of Euzebya (up to 30.7%) in one cave and its negligible occurrence (up to 0.2%) in another cave from mineralogically similar formations located 65 km apart. The difference in abundance was attributed to flooding and clay deposition in the Euzebya-rich cave.
A recent study was conducted on the biofilms present in Covadura Cave, located in the gypsum karst of Sorbas, Almeria, Spain. The karst comprises over 100 km of passages within the six most important caves (Covadura Cave, GEP Complex, C3 Cave, Gypsum Cave, Treasure Cave, and Water Cave), which are subject to condensation–dissolution mechanisms. Water condensation on the cooler walls of Covadura Cave takes place mainly during the dry period (July to October) and the biofilms show water droplets on their surface. Biofilm proliferation has been associated with the strong condensation existing in some caves [36], as condensation favors the colonization of cave walls by microorganisms [18][19].

The data revealed that Euzebyaceae were abundant in Covadura Cave white biofilms collected in 2010, but their relative abundance was drastically reduced in the 2022 sampling. This could be associated with the severe droughts, the last of which occurred between 2017 and 2018, and which continue until now. In the yellow biofilms, the decrease in abundance of Euzebyaceae was lower.

Euzebya was also abundant in volcanic caves. The genus was found in caves in the Azores, Canary Islands, Galapagos, Hawai’i, Idaho, Tennessee, and Mexico [19][20][24][26][28][29][30][34]. Gonzalez-Pimentel et al. [24] stated that yellow biofilms from a cave on the Canary Island of La Palma were dominated by metabolically active Euzebya (43.9% RNA clones vs. 26.0% DNA clones).

3. Euzebyales in Extreme Environments

Saline and hypersaline terrestrial environments include salt mines, sediments of desiccated salt lakes, saline and alkaline soils, salt marshes, etc. These environments often have salt concentrations higher than that of seawater and support halophilic microorganisms that have adapted to deal with extreme environmental parameters (high salt concentrations, temperatures, and pH), although their community composition and structure vary depending on salinity fluctuations in the environment [37].
The occurrence of Euzebya in these environments has been reported in numerous studies [38][39][40][41][42][43][44][45][46][47][48][49][50][51][52][53], denoting the ability of the members of this genus to prosper in habitats with high salt concentrations.
Interestingly, the wide occurrence of Euzebya and its haloalkaliphilic relatives has been registered in the drained sediments of former Mexican lakes (Texcoco and Rincon de Parangueo) [38][43], and the Songnen Plain of Northeast China, one of the three regions with extensive saline–sodic soils in the world [48][49][50][51].
The Texcoco Lake sediments are characterized by a very high pH (10) and an electric conductivity (EC) of up to 179.8 dS m−1 [38][40][42]. There, Euzebya was one of the dominant bacterial genera with relative abundances >10% [40]. It has been reported that organic carbon additions to the sediments increased Euzebya abundance [40].
In the Songnen Plain of Northeast China, with very high pH (>10) and high EC, Euzebya showed high relative abundance [48][50], as well as a high sodicity/salinity niche preference, however, the genus was depleted or absent when sodicity/salinity decreased [49].

Deserts, cover around 33% of the planet’s surface. The use of molecular tools (NGS) revealed dominant members of the extremophilic microbial communities that have not been yet isolated. They included Euzebya, both in cold environments (Antarctica) and hot deserts (Atacama, Sahara, Colorado Plateau, etc.) [54][55][56][57][58][59][60][61][62][63][64][65].

Euzebya was one of the most frequently detected genera in Australian and Northern Antarctica soils. There, Actinomycetota diversity increased with increasing pH and sodium concentration, and this applies particularly to Euzebya [58].
The McMurdo Dry Valleys is the largest ice-free soil region in Antarctica. There, Euzebyales were abundant only in the soil samples with moisture below 6.82% but largely declined or were absent in the soil with moisture content above 15.57% [56]. In Victoria Valley, within McMurdo Dry Valleys, two families, Euzebyaceae and Rubrobacteraceae, were abundant (over 30%) in endolithic niches and less frequent in soils. It has been reported that water availability largely conditioned the distribution of these actinobacterial families [57].

4. Euzebyales in Soils and Other Diverse Environments

Euzebya was found in the rhizosphere of Agave lechuguilla in the saline and oligotrophic soils of Cuatro Ciénegas Basin, Mexico [66][67], as well as in other plant rhizospheres from different regions [67][68][69][70][71][72][73][74].
Euzebya is represented in soils all over the world [75][76][77][78][79][80][81][82][83][84][85][86]. Several authors have reported the occurrence of Euzebya in clean and healthy soils and its absence in polluted soils [76][87][88]. However, Euzebya has also been found in bauxite residue disposal areas and copper mine wastes [89][90][91][92].
The presence of Euzebya has been recorded in saltern and salt lakes, terrestrial and sea waters, marine organisms [93][94][95][96][97][98][99][100], bentonite [101], animals [102][103][104], and humans [105][106][107]. In addition, the genus was found on a sandstone surface, covered by efflorescences, at the Wawel Royal Castle in Poland [108].

5. Relationship of Euzebyales with Other Members of Microbial Communities in Diverse Environments

A review of all the reports available in the literature provided some insights into the relationship of Euzebya with other taxa in different environments. In fact, several taxonomic groups may inhabit the same niche as Euzebya. Thus, Euzebya is present in most caves together with Crossiella, Rubrobacter, wb1-P19 (Nitrosococcales), and Gaiella, among other genera [19][21][23][27][28][29][33][34][35][36]. Caves are characterized by high relative humidity, in most cases near saturation, high mineral concentration, mainly of calcite in karstic and basaltic rocks in volcanic caves, as well as alkaline pH. In some pristine caves, oligotrophy is an environmental constraint.
In saline and hypersaline environments, the order Euzebyales is accompanied by other orders common to these extreme environments, such as Nitriliruptorales, Rubrobacterales, Solirubrobacterales, Gaiellales, Acidimicrobiales, Oceanospirillales, Rhizobiales, KSA1 (Bacteroidetes), etc. [39][40][43][47][48][49][50][51]. Most members of these orders require high pH and salt concentrations, and oligotrophy is common in these environments.
In deserts, Euzebya has been found together with Nitriliruptor, Rubrobacter, Solirubrobacter, Gaiella, Halomonas, etc. [55][57][58][61][62][63][64]. Water availability is scarce in deserts and environmental conditions become more challenging (e.g., strong oligotrophy and high mineral deposits). Most of these genera are known for their ability to resist extreme desiccation, high UV and ionizing radiation, temperature fluctuations, and high salinity and metal concentrations [55].
In soils, the co-occurrence of Euzebyales with Nitriliruptorales, Rubrobacterales, Solirubrobacterales, Gaiellales, Oceanospirillales, Rhizobiales, etc., is frequently reported [81][82][83][109][110], as previously stated for caves, saline, hypersaline, and desert environments.
To summarize, some microbial lineages present in harsh terrestrial environments show successful adaptation strategies and the ability to cope with available scarce nutrient sources in unfavorable climatic and geochemical conditions.

6. Culture Media for the Isolation of Euzebya in Terrestrial Environments

The terrestrial environments where Euzebya have been found are characterized by haloalkaliphilic conditions, high pH (9–10), and high to moderate salt contents. The availability of water in these ecosystems is widely variable, from dry conditions to 100% relative humidity, which suggests the great adaptability of this genus. In addition, the range of mean temperatures of these environments is highly variable, from −30 °C (winter in McMurdo Dry Valleys) to >40 °C in deserts, with large daily temperature fluctuations in each location.
The culture media used by different authors contained a wide array of carbon and nitrogen sources (peptone, tryptone, starch, tyrosine, glycerol, asparagine, sodium caseinate, malt extract, humic acid, glucose, oatmeal, etc.), mainly used for the isolation of Actinomycetota. At the same time, the media rarely contained high concentrations of salts (sodium or calcium), and the pH was not adjusted to the alkalinity ranges where terrestrial Euzebya and other related bacteria are abundant. None of these attempts were able to isolate strains of Euzebya, Nitriliruptor, Rubrobacter, Solirubrobacter, Gaiella, Halomonas, etc., which clearly indicates that the culture media used failed to reproduce the ecological conditions where these bacteria succeed.

7. Attempts to Isolate Euzebya from Pindal Cave

Pindal Cave is a shallow limestone cave formed through epigenic processes and located very close to the surface. The cave is 590 m long and due to the geographical location has a humid oceanic climate. The cave has a stable annual temperature (11.6 °C) with only minor fluctuations throughout the year (<2 °C/year). This cave is well-ventilated with relatively low annual average values of CO2 (680 ppm) and radon (950 Bq/m3) [36].
In Pindal Cave, pink biofilms primarily develop on the surface of calcite speleothems in areas near the entrance and Euzebyaceae reached a relative abundance of 7–16%; the biofilms have a rough surface and are formed by aggregates of cells, mostly rounded, with extensive filaments (Figure 1). Other abundant genera were Crossiella and wp1-P19. The ecological significance of the five top taxa in Pindal Cave was discussed elsewhere [36][111][112]. However, attempts to isolate Euzebya using different culture media failed. The following media were used: nutrient agar (NA), B-4 medium [113], GYM Streptomyces medium (DSMZ 65), Dimethylsulfone medium [114], TSA, diluted TSA/1000, and TSA supplemented with NaCl (3%) and MgSO4·7H2O (2%) (DSMZ 1350) [115]. In all these media, the pH was near 7, and not as markedly alkaline as Euzebya requires (pH 9–10), as denoted by their habitats; in other cases, the absence of relatively high NaCl concentrations likely prevented its isolation.
Figure 1. (a) Pink biofilms growing on calcite speleothems in Pindal Cave, Spain (red arrow). (bd) Scanning electron microscopy microphotographs of pink biofilms from Pindal Cave. (b) General view of pink biofilms (red arrow). (c,d) Bacterial filaments forming the biofilm.

Culture media reproducing the environmental conditions reported in terrestrial ecosystems, e.g., SN medium and marine agar (including 1/10 dilutions of these media), pH 9–10, and sodium chloride concentrations around 3% or more, could allow the isolation of terrestrial Euzebya and other haloalkaliphilic genera. Marine agar and SN medium [116] have been used for the isolation of marine Euzebya [14][15][16]. Alternatively, for maintaining a high pH, the medium Z8-NK, as described by Flores et al. [117], R2A, and/or other media with the addition of trace elements, amino acids, vitamins, and simple carbon sources to a minimal culture medium should be explored.

8. Concluding Remarks

NGS technologies have allowed the detection of unknown microorganisms and extended our knowledge of the diversity of microbial life on Earth. However, the majority of taxa are part of the yet-uncultured microbial dark matter that significantly contributes to ecosystem functioning [118][119].

The data indicate that Euzebya is present across the entire biosphere. The question is whether their species were dispersed from marine sources to the terrestrial environment or if they are truly terrestrial, not yet described, species.

Here, it is shown that Euzebya and other bacteria can thrive under harsh conditions, such as high concentrations of sodium and/or calcium, high electric conductivity, alkaline pH, and highly variable temperature and water fluctuations. These ecological conditions in the studied terrestrial environments are quasi-extreme.

Unfortunately, the culture media used so far for the isolation of Euzebya failed to reproduce the original conditions of these harsh terrestrial ecosystems and this could be the reason why strains of Euzebya and other bacteria that inhabit the same niche were not isolated.

Some of the pitfalls and limitations of commonly used culture media and possible solutions to challenges faced in isolating terrestrial Euzebya strains are presented. The importance of combining high-throughput sequencing and cultivation techniques is of the utmost interest for this task. Data on the physicochemical and environmental parameters of the terrestrial ecosystems where Euzebya thrives should be taken into account when designing appropriate culture media.

It is expected that the interest in the biogeochemical role and geographical distribution of Euzebya will promote the optimization of culture media, and in this way, researchers will be able to isolate novel Euzebya species from different terrestrial environments.

This entry is adapted from the peer-reviewed paper 10.3390/app13179644

References

  1. Herndl, G.J.; Bayer, B.; Baltar, F.; Reinthaler, T. Prokaryotic life in the deep ocean’s water column. Annu. Rev. Mar. Sci. 2023, 15, 461–483.
  2. Debbab, A.; Aly, A.H.; Lin, W.H.; Proksch, P. Bioactive compounds from marine bacteria and fungi. Microb. Biotechnol. 2010, 3, 544–563.
  3. Eom, S.-H.; Kim, Y.-M.; Kim, S.-K. Marine bacteria: Potential sources for compounds to overcome antibiotic resistance. Appl. Microbiol. Biotechnol. 2013, 97, 4763–4773.
  4. Andryukov, B.; Mikhailov, V.; Besednova, N. The biotechnological potential of secondary metabolites from marine bacteria. J. Mar. Sci. Eng. 2019, 7, 176.
  5. Sun, W.; Wu, W.; Liu, X.; Zaleta-Pinet, D.A.; Clark, B.R. Bioactive compounds isolated from marine-derived microbes in China: 2009–2018. Mar. Drugs 2019, 17, 339.
  6. Carroll, A.R.; Copp, B.R.; Davis, R.A.; Keyzers, R.A.; Prinsep, M. Marine natural products. Nat. Prod. Rep. 2023, 40, 275.
  7. Siro, G.; Donald, L.; Pipite, A. The diversity of deep-sea actinobacteria and their natural products: An epitome of curiosity and drug discovery. Diversity 2023, 15, 30.
  8. Wibowo, J.T.; Bayu, A.; Aryati, W.D.; Fernandes, C.; Yanuar, A.; Kijjoa, A.; Putra, M.Y. Secondary metabolites from marine-derived bacteria with antibiotic and antibiofilm activities against drug-resistant pathogens. Mar. Drugs 2023, 21, 50.
  9. Subramani, R.; Aalbersberg, W. Culturable rare Actinomycetes: Diversity, isolation and marine natural product discovery. Appl. Microbiol. Biotechnol. 2013, 97, 9291–9321.
  10. Dhakal, D.; Pokhrel, A.R.; Shrestha, B.; Sohng, J.K. Marine rare Actinobacteria: Isolation, characterization, and strategies for harnessing bioactive compounds. Front. Microbiol. 2017, 8, 1106.
  11. Subramani, R.; Sipkema, D. Marine rare actinomycetes: A promising source of structurally diverse and unique novel natural products. Mar. Drugs 2019, 17, 249.
  12. Gattoni, G.; de la Haba, R.R.; Martín, J.; Reyes, F.; Sánchez-Porro, C.; Feola, A.; Zuchegna, C.; Guerrero-Flores, S.; Varcamonti, M.; Ricca, E.; et al. Genomic study and lipidomic bioassay of Leeuwenhoekiella parthenopeia: A novel rare biosphere marine bacterium that inhibits tumor cell viability. Front. Microbiol. 2023, 13, 1090197.
  13. Wei, B.; Du, A.-Q.; Ying, T.-T.; Hu, G.-A.; Zhou, Z.-Y.; Yu, W.-C.; He, J.; Yu, Y.-L.; Wang, H.; Xu, X.-W. Secondary metabolic potential of Kutzneria. J. Nat. Prod. 2023, 86, 1120–1127.
  14. Kurahashi, M.; Fukunaga, Y.; Sakiyama, Y.; Harayama, S.; Yokota, A. Euzebya tangerina gen. nov., sp. nov., a deeply branching marine actinobacterium isolated from the sea cucumber Holothuria edulis, and proposal of Euzebyaceae fam. nov., Euzebyales ord. nov. and Nitriliruptoridae subclassis nov. Int. J. Syst. Evol. Microbiol. 2010, 60, 2314–2319.
  15. Yin, Q.; Zhang, L.; Song, Z.M.; Wu, Y.; Hu, Z.-L.; Zhang, X.-H.; Zhang, Y.; Yu, M.; Xu, Y. Euzebya rosea sp. nov., a rare actinobacterium isolated from the East China Sea and analysis of two genome sequences in the genus Euzebya. Int. J. Syst. Evol. Microbiol. 2018, 68, 2900–2905.
  16. Jian, S.-L.; Xu, L.; Meng, F.-X.; Sun, C.; Xu, X.-W. Euzebya pacifica sp. nov., a novel member of the class Nitriliruptoria. Int. J. Syst. Evol. Microbiol. 2021, 71, 004864.
  17. Xu, L.; Sun, C.; Huang, M.M.; Wu, Y.-H.; Yuan, C.-Q.; Dai, W.-H.; Ye, K.; Han, B.; Xu, X.-W. Complete genome sequence of Euzebya sp. DY32-46, a marine Actinobacteria isolated from the Pacific Ocean. Mar. Genom. 2019, 44, 65–69.
  18. Cuezva, S.; Fernandez-Cortes, A.; Porca, E.; Pasic, L.; Jurado, V.; Hernandez-Marine, M.; Serrano-Ortiz, P.; Cañaveras, J.C.; Sanchez-Moral, S.; Saiz-Jimenez, C. The biogeochemical role of Actinobacteria in Altamira Cave, Spain. FEMS Microbiol. Ecol. 2012, 81, 281–290.
  19. Riquelme, C.; Hathaway, J.J.M.; Dapkevicius, M.L.N.E.; Miller, A.Z.; Kooser, A.; Northup, D.E.; Jurado, V.; Fernandez, O.; Saiz-Jimenez, C.; Cheeptham, N. Actinobacterial diversity in volcanic caves and associated geomicrobiological interactions. Front. Microbiol. 2015, 6, 1342.
  20. Spilde, M.N.; Northup, D.E.; Caimi, N.A.; Boston, P.J.; Stone, F.D.; Smith, S. Microbial Mat Communities in Hawaiian Lava Caves. In International Symposium on Vulcanospeleology 2016; 2016. Available online: http://www.cavepics.com/IVS17/SPILDE.pdf (accessed on 1 June 2023).
  21. Yun, Y.; Wang, H.; Man, B.; Xiang, X.; Zhou, J.; Qiu, X.; Duan, Y.; Engel, A.S. The relationship between pH and bacterial communities in a single karst ecosystem and its implication for soil acidification. Front. Microbiol. 2016, 7, 1955.
  22. Lepinay, C.; Mihajlovski, A.; Seyer, D.; Touron, S.; Bousta, F.; Di Martino, P. Biofilm communities survey at the areas of salt crystallization on the walls of a decorated shelter listed at UNESCO World cultural Heritage. Int. Biodeter. Biodegr. 2017, 122, 116–127.
  23. Itcus, C.; Pascu, M.D.; Lavin, P.; Persoiu, A.; Iancu, L.; Purcarea, C. Bacterial and archaeal community structures in perennial cave ice. Sci. Rep. 2018, 8, 15671.
  24. Gonzalez-Pimentel, J.L.; Miller, A.Z.; Jurado, V.; Laiz, L.; Pereira, M.F.C.; Saiz-Jimenez, C. Yellow colored mats from lava tube of La Palma (Canary Islands, Spain) are dominated by metabolically active Actinobacteria. Sci. Rep. 2018, 8, 1944.
  25. De, A.K.; Muthiyan, R.; Sunder, J.; Bhattacharya, B.; Kundu, A.; Roy, S.D. Profiling bacterial diversity of B2 cave, a limestone cave of Baratang, Andaman and Nicobar Islands, India. Proc. Indian Nat. Sci. Acad. 2019, 85, 853–862.
  26. González-Pimentel, J.L. Microorganismos de las Cuevas Volcánicas de La Palma (Islas Canarias): Diversidad y Potencial uso Biotecnológico. Ph.D. Thesis, Universidad Pablo de Olavide, Sevilla, Spain, 2019.
  27. Li, M.; Fang, C.; Kawasaki, S.; Huang, M.; Achal, V. Bio-consolidation of cracks in masonry cement mortars by Acinetobacter sp. SC4 isolated from a karst cave. Int. Biodeter. Biodegr. 2019, 141, 94–100.
  28. Luis-Vargas, M.N.; López-Martínez, R.A.; Vilchis-Nestor, A.R.; Daza, R.; Alcántara-Hernández, R.J. Bacterial insights into the formation of opaline stromatolites from the Chimalacatepec lava tube system, Mexico. Geomicrobiol. J. 2019, 36, 694–704.
  29. Frazier, V.E. Carbon Metabolism in Cave Subaerial Biofilms. Master’s Thesis, University of Tennessee, Knoxville, TN, USA, 2020.
  30. Miller, A.Z.; García-Sánchez, A.M.; Coutinho, M.L.; Pereira, M.F.C.; Gázquez, F.; Calaforra, J.M.; Forti, P.; Martínez-Frías, J.; Toulkeridis, T.; Caldeira, A.T.; et al. Colored microbial coatings in show caves from the Galapagos Islands (Ecuador): First microbiological approach. Coatings 2020, 10, 1134.
  31. Iquebal, M.A.; Passari, A.K.; Jagannadham, J.; Ahmad, F.; Leo, V.V.; Singh, G.; Jaiswal, S.; Rai, A.; Kumar, D.; Singh, B.P. Microbiome of Pukzing Cave in India shows high antimicrobial activity against plant and animal pathogens. Genomics 2021, 113, 4098–4108.
  32. González-Riancho Fernández, C. Análisis Descriptivo y Funcional de las Colonias Microbianas Visibles que Crecen en la Cueva de Altamira, Enfocado al Diseño de Medidas de Control. Ph.D. Thesis, Universidad de Cantabria, Santander, Spain, 2021.
  33. Ma, L.; Huang, X.; Wang, H.; Yun, Y.; Cheng, X.; Liu, D.; Lu, X.; Qiu, X. Microbial interactions drive distinct taxonomic and potential metabolic responses to habitats in karst cave ecosystem. Microbiol. Spectr. 2021, 9, e01152-21.
  34. Weng, M.M.; Zaikova, E.; Millan, M.; Williams, A.J.; McAdam, A.C.; Knudson, C.A.; Fuqua, S.R.; Wagner, N.Y.; Craft, K.; Nawotniak, S.K.; et al. Life underground: Investigating microbial communities and their biomarkers in Mars-analog lava tubes at Craters of the Moon National Monument and Preserve. J. Geophys. Res. Planets 2022, 127, e2022JE007268.
  35. Yi, Y.-J.; Kim, S.-I.; Ahn, U.-S.; Lee, K.C.; Lee, M.-K.; Lee, J.-S.; Kim, D.-S.; Kim, J.-S. Hex code-based geological cross-sections describing landscape dynamics in the Jeju Geomunoreum lava tube system. Korean J. Environ. Agric. 2022, 41, 65–70.
  36. Martín Pozas, T. Papel de los Microorganismos en Procesos de Captación y Emisión de Gases de Efecto Invernadero en Ambientes Subterráneos. Ph.D. Thesis, Universidad Complutense, Madrid, Spain, 2023.
  37. Paul, V.G.; Mormile, M.R. A case for the protection of saline and hypersaline environments: A microbiological perspective. FEMS Microbiol. Ecol. 2017, 93, fix091.
  38. Castro-Silva, C.; Ruíz-Valdiviezo, V.M.; Valenzuela-Encinas, C.; Alcántara-Hernández, R.J.; Navarro-Noya, Y.E.; Vázquez-Núñez, E.; Luna-Guido, M.; Marsch, R.; Dendooven, L. The bacterial community structure in an alkaline saline soil spiked with anthracene. Electron. J. Biotechnol. 2013, 16, 10.
  39. Yan, H.; Hu, J.; Long, X.; Liu, Z.; Rengel, Z. Salinity altered root distribution and increased diversity of bacterial communities in the rhizosphere soil of Jerusalem artichoke. Sci. Rep. 2016, 6, 20687.
  40. De León-Lorenzana, A.S.; Delgado-Balbuena, L.; Domínguez-Mendoza, C.A.; Navarro-Noya, Y.E.; Luna-Guido, M.; Dendooven, L. Soil salinity controls relative abundance of specific bacterial groups involved in the decomposition of maize plant residues. Front. Ecol. Evol. 2018, 6, 51.
  41. Mukhtar, S.; Mirza, B.S.; Mehnaz, S.; Mirza, M.S.; Mclean, J.; Malik, K.A. Impact of soil salinity on the microbial structure of halophyte rhizosphere microbiome. World J. Microbiol. Biotechnol. 2018, 34, 136.
  42. Martínez-Olivas, M.A.; Jiménez-Bueno, N.G.; Hernández-García, J.A.; Fusaro, C.; Luna-Guido, M.; Navarro-Noya, Y.E.; Dendooven, L. Bacterial and archaeal spatial distribution and its environmental drivers in an extremely haloalkaline soil at the landscape scale. PeerJ 2019, 7, e6127.
  43. Sánchez-Sánchez, J.; Cerca, M.; Alcántara-Hernández, R.J.; Lozano-Flores, C.; Carreón-Freyre, D.; Levresse, G.; Vega, M.; Varela-Echavarría, A.; Aranda-Gómez, J.J. Extant microbial communities in the partially desiccated Rincon de Parangueo maar crater lake in Mexico. FEMS Microbiol. Ecol. 2019, 95, fiz051.
  44. Ibarra-Sánchez, C.L.; Pince, L.; Aguirre-Noyola, J.L.; Sánchez-Cerda, K.E.; Navaro-Noya, Y.E.; Luna-Guido, M.; Conde-Barajas, E.; Dendooven, L.; Gomez-Acata, E.S. The microbial community in an alkaline saline sediment of a former maar lake bed. J. Soils Sediments 2020, 20, 542–555.
  45. Wu, N.; Li, Z.; Wu, F.; Tang, M. Microenvironment and microbial community in the rhizosphere of dioecious Populus cathayana at Chaka Salt Lake. J. Soils Sediments 2019, 19, 2740–2751.
  46. Baeshen, M.N.; Moussa, T.A.A.; Ahmed, F.; Abulfaraj, A.A.; Jalal, R.S.; Majaeed, M.A.; Baeshen, N.A.; Huelsenbeck, J.P. Diversity profiling of associated bacteria from the soils of stress tolerant plants from seacoast of Jeddah, Saudi Arabia. Appl. Ecol. Environ. Res. 2020, 18, 8217–8231.
  47. Camacho-Sanchez, M.; Barcia-Piedras, J.M.; Redondo-Gómez, S.; Camacho, M. Mediterranean seasonality and the halophyte Arthrocnemum macrostachyum determine the bacterial community in salt marsh soils in Southwest Spain. Appl. Soil Ecol. 2020, 151, 103532.
  48. Gao, W.; Xu, J.; Zhao, J.; Zhang, H.; Ni, Y.; Zhao, B.; Tebbe, C.C.; Zhang, J.; Jia, Z. Prokaryotic community assembly after 40 years of soda solonetz restoration by natural grassland and reclaimed farmland. Eur. J. Soil Biol. 2020, 100, 103213.
  49. Xu, J.; Gao, W.; Zhao, B.; Chen, M.; Ma, L.; Jia, Z.; Zhang, J. Bacterial community composition and assembly along a natural sodicity/salinity gradient in surface and subsurface soils. Appl. Soil Ecol. 2021, 157, 103731.
  50. Chang, C.; Tian, L.; Tian, Z.; McLaughlin, N.; Tian, C. Change of soil microorganism communities under saline-sodic land degradation on the Songnen Plain in northeast China. J. Plant Nutr. Soil Sci. 2022, 185, 297–307.
  51. Du, X.; Wang, S.; Huang, H.; Zhang, Y.; Ren, X.; Hu, S. Fermenting straw reduced salt damage and improved the stability of the bacterial community in a saline–sodic soil. J. Agric. Sci. Agrotechnol. 2022, 1, 1–18.
  52. Peng, M.; Wang, C.; Wang, Z.; Huang, X.; Zhou, F.; Yan, S.; Liu, X. Differences between the effects of plant species and compartments on microbiome composition in two halophyte Suaeda species. Bioengineered 2022, 13, 12475–12488.
  53. Urana, R.; Yadav, J.; Panchal, S.; Sharma, P.; Singh, N. Phytoremediation of PAH compounds by microbial communities in sodic soil. Int. J. Phytoremediation 2023, 25, 1501–1509.
  54. Van Goethem, M.W.; Makhalanyane, T.P.; Valverde, A.; Cary, S.C.; Cowan, D.A. Characterization of bacterial communities in lithobionts and soil niches from Victoria Valley, Antarctica. FEMS Microbiol. Ecol. 2016, 92, fiw051.
  55. Meslier, V.; Casero, M.C.; Dailey, M.; Wierzchos, J.; Ascaso, C.; Artieda, O.; McCullough, P.R.; DiRuggiero, J. Fundamental drivers for endolithic microbial community assemblies in the hyperarid Atacama Desert. Environ. Microbiol. 2018, 20, 1765–1781.
  56. Lee, K.C.; Caruso, T.; Archer, S.D.J.; Gillman, L.N.; Lau, M.C.Y.; Cary, S.C.; Lee, C.K.; Pointing, S.B. Stochastic and deterministic effects of a moisture gradient on soil microbial communities in the McMurdo Dry Valleys of Antarctica. Front. Microbiol. 2018, 9, 2619.
  57. Rego, A.; Raio, F.; Martins, T.P.; Ribeiro, H.; Sousa, A.G.G.; Séneca, J.; Baptista, M.S.; Lee, C.K.; Cary, S.C.; Ramos, V.; et al. Actinobacteria and cyanobacteria diversity in terrestrial Antarctic microenvironments evaluated by culture-dependent and independent methods. Front. Microbiol. 2019, 10, 1018.
  58. Araujo, R.; Gupta, V.V.S.R.; Reith, F.; Bisset, A.; Mele, P.; Franco, C.M.M. Biogeography and emerging significance of Actinobacteria in Australia and Northern Antarctica soils. Soil Biol. Biochem. 2020, 146, 107805.
  59. Miralles, I.; Soria, R.; Lucas-Borja, M.E.; Soriano, M.; Ortega, R. Effect of biocrusts on bacterial community composition at different soil depths in Mediterranean semi-arid ecosystems. Sci. Total Environ. 2020, 733, 138613.
  60. Bona, E.; Massa, N.; Toumatia, O.; Novello, G.; Cesaro, P.; Todeschini, V.; Boatti, L.; Mignone, F.; Titouah, H.; Zitouni, A.; et al. Climatic zone and soil properties determine the biodiversity of the soil bacterial communities associated to native plants from desert areas of North-Central Algeria. Microorganisms 2021, 9, 1359.
  61. Khomutovska, N.; de los Ríos, A.; Syczewski, M.D.; Jasser, I. Connectivity of edaphic and endolithic microbial niches in cold mountain desert of Eastern Pamir (Tajikistan). Biology 2021, 10, 314.
  62. Ortiz, M.; Leung, P.M.; Shelley, G.; Jirapanjawat, T.; Nauer, P.A.; Van Goethem, M.W.; Bay, S.K.; Islam, Z.F.; Jordaan, K.; Vikram, S.; et al. Multiple energy sources and metabolic strategies sustain microbial diversity in Antarctic desert soils. Proc. Natl. Acad. Sci. USA 2021, 118, e2025322118.
  63. Osman, J.R.; Wang, Y.; Jaubert, C.; Nguyen, T.-N.; Fernandes, G.R.; DuBow, M.S. The bacterial communities of surface soils from desert sites in the eastern Utah (USA) portion of the Colorado Plateau. Microbiol. Res. 2021, 244, 126664.
  64. Sun, X.; Pei, J.; Zhao, L.; Ahmad, B.; Huang, L.-F. Fighting climate change: Soil bacteria communities and topography play a role in plant colonization of desert areas. Environ. Microbiol. 2021, 23, 6876–6894.
  65. Li, Y.; He, X.; Yuan, H.; Lv, G. Differed growth stage dynamics of root-associated bacterial and fungal community structure associated with halophytic plant Lycium ruthenicum. Microorganisms 2022, 10, 1644.
  66. Echeverría Molinar, A. Efecto de Factores Abióticos y Bióticos Sobre la Estructura de la Comunidad Microbiana del Suelo en un Ambiente Oligotrófico. Master’s Thesis, Instituto Potosino de Investigación Científica y Tecnológica, San Luis Potosí, Mexico, 2017.
  67. López-Lozano, N.E.; Echeverría Molinar, A.; Ortiz Durán, E.A.; Hernández Rosales, M.; Souza, V. Bacterial diversity and interaction networks of Agave lechuguilla rhizosphere differ significantly from bulk soil in the oligotrophic basin of Cuatro Cienegas. Front. Plant Sci. 2020, 11, 1028.
  68. Sun, J.; Zhang, Q.; Zhou, J.; Wei, Q. Pyrosequencing technology reveals the impact of different manure doses on the bacterial community in apple rhizosphere soil. Appl. Soil Ecol. 2014, 78, 28–36.
  69. Lee, H.-J.; Han, S.-I.; Whang, K.-S. Phylogenetic characteristics of actinobacterial population in bamboo (Sasa borealis) soil. Korean J. Microbiol. 2016, 52, 59–64.
  70. An, Z.; Guo, F.; Chen, Y.; Bai, G.; Chen, Z. Rhizosphere bacterial and fungal communities during the growth of Angelica sinensis seedlings cultivated in an Alpine uncultivated meadow soil. PeerJ 2020, 8, e8541.
  71. Liu, A.; Li, Y.; Wang, Q.; Zhang, X.; Xiong, J.; Li, Y.; Lei, Y.; Sun, Y. Analysis of microbial diversity and community structure of rhizosphere soil of Cistanche salsa from different host plants. Front. Microbiol. 2022, 13, 971228.
  72. Duan, M.; Wang, L.; Song, X.; Zhang, X.; Wang, Z.; Lei, J.; Yan, M. Assessment of the rhizosphere fungi and bacteria recruited by sugarcane during smut invasion. Braz. J. Microbiol. 2023, 54, 385–395.
  73. Cheng, Y.; Xie, X.; Wang, X.; Zhu, L.; Qiu, Q.-S.; Xu, X. Effects of the salt-tolerant gramineous forage Echinochloa frumentacea on biological improvement and crop productivity in saline–alkali land on the Hetao Ningxia Plain in China. Sustainability 2023, 15, 5319.
  74. Wang, D.; Ren, H. Microbial community in buckwheat rhizosphere with different nitrogen application rates. PeerJ 2023, 11, e15514.
  75. Jiménez Bueno, N.G. Efecto de las Diferentes Prácticas de Agricultura Sobre las Comunidades Bacterianas en Suelos del Valle del Yaqui. Ph.D. Thesis, Centro de Investigación y de Estudios Avanzados del Instituto Politécnico Nacional, Mexico City, Mexico, 2016.
  76. Wolinska, A.; Görniak, D.; Zielenkiewicz, U.; Kuzniar, A.; Izak, D.; Banach, A.; Blaszczyk, M. Actinobacteria structure in autogenic, hydrogenic and lithogenic cultivated and non-cultivated soils: A culture-independent approach. Agronomy 2019, 9, 598.
  77. Liu, C.; Zhao, X.; Lin, Q.; Li, G. Decrease in diversity and shift in composition of the soil bacterial community were closely related to high available phosphorus in agricultural Fluvisols of North China. Acta Agric. Scand. Soil Plant Sci. 2019, 69, 618–630.
  78. Biderre-Petit, C.; Hochart, C.; Gardon, H.; Dugat-Bony, E.; Terrat, S.; Jouan-Dufournel, I.; Paris, R. Analysis of bacterial and archaeal communities associated with Fogo volcanic soils of different ages. FEMS Microbiol. Ecol. 2020, 96, fiaa104.
  79. Cui, Y.; Yong, L.; Rongli, M.; Wen, D.; Zhixian, Z.; Xingming, H. Metagenomics analysis of the effects of long-term stand age on beneficial soil bacterial community structure under Chinese ancient mulberry farming practice. Hortic. Environ. Biotechnol. 2020, 61, 1063–1071.
  80. Lopes, L.S.; Mendes, L.W.; Antunes, J.E.L.; Oliverira, L.M.S.; Melo, V.M.M.; Pereira, A.P.A.; Costa, A.F.; Oliveira, J.P.; Martínez, C.R.; Figueiredo, M.V.B.; et al. Distinct bacterial community structure and composition along different cowpea producing ecoregions in Northeastern Brazil. Sci. Rep. 2021, 11, 831.
  81. Hazzouri, K.M.; Sudalaimuthuasari, N.; Saeed, E.E.; Kundu, B.; Al-Maskari, R.S.; Nelson, D.; AlShehhi, A.A.; Aldhuhoori, M.A.; Almutawa, D.S.; Alshehhi, F.R.; et al. Salt flat microbial diversity and dynamics across salinity gradient. Sci. Rep. 2022, 12, 11293.
  82. Pino-Otín, M.R.; Ferrando, N.; Ballestero, D.; Langa, E.; Roig, F.J.; Terrado, E.M. Impact of eight widely consumed antibiotics on the growth and physiological profile of natural soil microbial communities. Chemosphere 2022, 305, 135473.
  83. Baldi, D.S.; Humphrey, C.E.; Kyndt, J.A.; Moore, T.C. Native plant gardens support more microbial diversity and higher relative abundance of potentially beneficial taxa compared to adjacent turf grass lawns. Urban Ecosyst. 2023, 26, 807–820.
  84. David, A.B.; Mwaikomo, K.S.; Midega, C.; Magingo, F.; Alsanius, B.W.; Drinkwater, L.E.; Dekker, T.; Lyantagaye, S. A comparative study on the impact of five Desmodium species on soil microbiome reveals enrichment of selected bacterial and fungal taxa. bioRxiv 2023.
  85. Manucharova, N.A.; Kovalenko, M.A.; Alekseeva, M.G.; Babenko, A.D.; Stepanov, A.L. Biotechnological potential of hydrolytic prokaryotic component in soils. Eurasian Soil Sci. 2023, 56, 558–572.
  86. Wang, Y.; Wang, Y.; Zhang, Q.; Fan, H.; Wang, X.; Wang, J.; Zhou, Y.; Chen, Z.; Sun, F.; Cui, X. Saline-alkali soil property improved by the synergistic effects of Priestia aryabhattai JL-5, Staphylococcus pseudoxylosus XW-4, Leymus chinensis and soil microbiota. Int. J. Mol. Sci. 2023, 24, 7737.
  87. Peng, M.; Zi, X.; Wang, Q. Bacterial community diversity of oil-contaminated soils assessed by high throughput sequencing of 16S rRNA genes. Int. J. Environ. Res. Public Health 2015, 12, 12002–12015.
  88. Kumar, V.; AlMomin, S.; Al-Aqeel, H.; Al-Salameen, F.; Nair, S.; Shajan, A. Metagenomic analysis of rhizosphere microflora of oil-contaminated soil planted with barley and alfalfa. PLoS ONE 2018, 13, e0202127.
  89. Ke, W.; Zhang, X.; Zhu, F.; Wu, H.; Zhang, Y.; Shi, Y.; Hartley, W.; Xue, S. Appropriate human intervention stimulates the development of microbial communities and soil formation at a long-term weathered bauxite residue disposal area. J. Hazard. Mater. 2021, 405, 124689.
  90. Rahman, K.M.J.; Diba, F.; Shuvo, M.S.R.; Siddique, M.A.; Hossain, M.A.; Sultana, M. Metagenomic investigation of bacterial community of arsenic-prone area in the northwest region of Bangladesh. Bangladesh J. Microbiol. 2022, 39, 31–38.
  91. Ossanna, L.Q.R.; Serrano, K.; Jennings, L.L.; Dillon, J.; Maier, R.M.; Neilson, J.W. Progressive belowground soil development associated with sustainable plant establishment during copper mine waste revegetation. Appl. Soil Ecol. 2023, 186, 104813.
  92. Feng, G.; Yong, J.; Liu, Q.; Chen, H.; Hu, Y.; Mao, P. Remedial effect and operating status of a decommissioned uranium mill tailings (UMT) repository: A micro-ecological perspective based on bacterial community. J. Environ. Manag. 2023, 340, 117993.
  93. Héry, M.; Rizoulis, A.; Sanguin, H.; Cooke, D.A.; Pancost, R.D.; Polya, D.A.; Lloyd, J.R. Microbial ecology of arsenic-mobilizing Cambodian sediments: Lithological controls uncovered by stable-isotope probing. Environ. Microbiol. 2014, 17, 1857–1869.
  94. Mirete, S.; Mora-Ruiz, M.R.; Lamprecht-Grandío, M.; de Figueras, C.G.; Rosselló-Móra, R.; González-Pastor, J.E. Salt resistance genes revealed by functional metagenomics from brines and moderate-salinity rhizosphere within a hypersaline environment. Front. Microbiol. 2015, 6, 1121.
  95. Ivanova, E.A.; Pershina, E.V.; Kutovaya, O.V.; Sergaliev, N.K.h.; Nagieva, A.G.; Zhiengaliev, A.T.; Provorov, N.A.; Andronov, E.E. Comparative analysis of microbial communities of contrasting soil types in different plant communities. Russ. J. Ecol. 2018, 49, 30–39.
  96. Truchado, P.; Gil, M.I.; Suslow, T.; Allende, A. Impact of chlorine dioxide disinfection of irrigation water on the epiphytic bacterial community of baby spinach and underlying soil. PLoS ONE 2018, 13, e0199291.
  97. West, N.J.; Parrot, D.; Fayet, C.; Grube, M.; Tomasi, S.; Suzuki, M.T. Marine cyanolichens from different littoral zones are associated with distinct bacterial communities. PeerJ 2018, 6, e5208.
  98. Feby, A.; Divya, B.; Nair, S. Bacterial diversity in demosponges from the coral reefs of Lakshadweep, India. Rom. J. Biol. Zool. 2021, 66, 85–100.
  99. Li, C.; Liu, J.; Chen, X.; Ren, H.; Su, B.; Ma, K.; Tu, Q. Determinism governs the succession of disturbed bacterioplankton communities in a coastal maricultural ecosystem. Sci. Total Environ. 2022, 828, 154457.
  100. Parab, A.S.; Manohar, C.S.; Ghose, M.P. Influence of seasonal variations in primary productivity on the bacterial community structure at Chlorophyll Maximum (C-Max) depths along the west coast of India. bioRxiv 2023.
  101. Povedano-Priego, C.; Jroundi, F.; Lopez-Fernandez, M.; Sánchez-Castro, I.; Martín-Sánchez, I.; Huertas, J.; Merroun, M.L. Shifts in bentonite bacterial community and mineralogy in response to uranium and glicerol-2-phosphate exposure. Sci. Total Environ. 2019, 692, 219–232.
  102. Ephraim, E.; Brockman, J.A.; Jewell, D.E. A diet supplemented with polyphenols, prebiotics and omega-3 fatty acids modulates the intestinal microbiota and improves the profile of metabolites linked with anxiety in dogs. Biology 2022, 11, 976.
  103. Marchywka, M. Clinical and Microbiological Improvement in Dog after Metal and Benzoate Containing Supplement Mix; Tech Report MJM-2022-013; Public Note: Austin, TX, USA, 2022.
  104. Niemiec, B.A.; Gawor, J.; Tang, S.; Prem, A.; Krumbeck, J.A. The bacteriome of the oral cavity in healthy dogs and dogs with periodontal disease. Am. J. Vet. Res. 2022, 83, 50–58.
  105. Richter, H.E.; Carnes, M.U.; Komesu, Y.M.; Lukacz, E.S.; Arya, L.; Bradley, M.; Rogers, R.G.; Sung, V.W.; Siddiqui, N.Y.; Carper, B.; et al. Association between the urogenital microbiome and surgical treatment response in women undergoing midurethral sling operation for mixed urinary incontinence. Am. J. Obstet. Gynecol. 2022, 226, 93.e1–93.e15.
  106. Chen, B.-Y.; Lin, W.-Z.; Li, Y.-L.; Bi, C.; Du, L.-J.; Liu, Y.; Zhou, L.-J.; Liu, T.; Xu, S.; Shi, C.-J.; et al. Roles of oral microbiota and oral-gut microbial transmission in hypertension. J. Adv. Res. 2023, 43, 147–161.
  107. Fan, S.; He, X.; Zhu, Z.; Chen, L.; Zou, Y.; Chen, Z.; Yu, J.; Chen, W.; Guan, H.; Ma, J. Integrating host transcriptomic signatures for distinguishing autoimmune encephalitis in cerebrospinal fluid by metagenomic sequencing. Cell Biosci. 2023, 13, 111.
  108. Dyda, M.; Pyzik, A.; Wilkojc, E.; Kwiatkowska-Kopka, B.; Sklodowska, A. Bacterial and fungal diversity inside the medieval building constructed with sandstone plates and lime mortar as an example of the microbial colonization of a nutrient-limited extreme environment (Wawel Royal Castle, Krakow, Poland). Microorganisms 2019, 7, 416.
  109. Wang, L.; Peng, C.; Gong, B.; Yang, Z.; Song, J.; Li, L.; Xu, L.; Yue, T.; Wang, X.; Yang, M.; et al. Actinobacteria community and their antibacterial and cytotoxic activity on the Weizhou and Xieyang volcanic islands in the Beibu Gulf of China. Front. Microbiol. 2022, 13, 911408.
  110. Weels, S.S.L.; Welz, P.J.; Prins, A.; Le Roes-Hill, M. Impact of physicochemical parameters on the diversity and distribution of microbial communities associated with three South African peatlands. Microorganisms 2022, 10, 2103.
  111. Martin-Pozas, T.; Gonzalez-Pimentel, J.L.; Jurado, V.; Laiz, L.; Cañaveras, J.C.; Fernandez-Cortes, A.; Cuezva, S.; Sanchez-Moral, S.; Saiz-Jimenez, C. Crossiella, a rare Actinomycetota genus, abundant in the environment. Appl. Biosci. 2023, 2, 194–210.
  112. Martin-Pozas, T.; Fernandez-Cortes, A.; Cuezva, S.; Cañaveras, J.C.; Benavente, D.; Duarte, E.; Saiz-Jimenez, C.; Sanchez-Moral, S. New insights into the structure, microbial diversity and ecology of yellow biofilms in a Paleolithic rock art cave (Pindal Cave, Asturias, Spain). Sci. Total Environ. 2023, 897, 165218.
  113. Boquet, E.; Boronat, A.; Ramos-Cormenzana, A. Production of calcite (calcium carbonate) crystals by soil bacteria is a general phenomenon. Nature 1973, 246, 527–528.
  114. Borodina, E.; Kelly, D.P.; Rainey, F.A.; Ward-Rainey, N.L.; Wood, A.P. Dimethylsulfone as a growth substrate for novel methylotrophic species of Hyphomicrobium and Arthrobacter. Arch. Microbiol. 2000, 173, 425–437.
  115. Laiz, L.; Miller, A.Z.; Jurado, V.; Akatova, E.; Sanchez-Moral, S.; Gonzalez, J.M.; Dionísio, A.; Macedo, M.F.; Saiz-Jimenez, C. Isolation of Rubrobacter strains from biodeteriorated monuments. Naturwissenschaften 2009, 96, 71–79.
  116. Kurahashi, M.; Fukunaga, Y.; Sakiyama, Y.; Harayama, S.; Yokota, A. Iamia majanohamensis gen. nov., sp. nov., an actinobacterium isolated from sea cucumber Holothuria edulis, and proposal of Iamiaceae fam. nov. Int. J. Syst. Evol. Microbiol. 2009, 59, 869–873.
  117. Flores, N.; Hoyos, S.; Venegas, M.; Galetovic, A.; Zúñiga, L.M.; Fábrega, F.; Paredes, B.; Salazar-Ardiles, C.; Vilo, C.; Ascaso, C.; et al. Haloterrigena sp. strain SGH1, a bacterioruberin-rich, perchlorate-tolerant halophilic archaeon isolated from halite microbial communities, Atacama Desert, Chile. Front. Microbiol. 2020, 11, 324.
  118. Jiao, J.-Y.; Liu, L.; Hua, Z.-S.; Fang, B.-Z.; Zhou, E.-M.; Salam, N.; Hedlund, B.P.; Li, W.-J. Microbial dark matter coming to light: Challenges and opportunities. Nat. Sci. Rev. 2021, 8, nwaa280.
  119. Pascoal, F.; Costa, R.; Magalhaes, C. The microbial rare biosphere: Current concepts, methods and ecological principles. FEMS Microbiol. Ecol. 2021, 97, fiaa227.
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