the prominent role of the iron cycle in the ecosystem. The identification of iron sulfates and oxides on Mars, analogous to those generated in the Tinto basin by microbial metabolism, has made Rio Tinto one of the best geochemical and mineralogical terrestrial Mars analogues.
Keywords: Acidophiles, chemolithotrophy, pyrite, iron cycle, subsurface geomicrobiology, Mars, Meridiani Planum, methane
2.1 Introduction
Although Darwin’s observation of samples from an Argentinian salt pond led him to predict the existence of life associated with diverse extreme environments [2.26], almost two hundred years had to pass before extremophiles gained serious scientific consideration. At the beginning of the XXth century the interest in preventing the spoiling of salt-preserved codfish by halophilic microorganisms, with its damaging economic and social consequences, led to a need to understand how these microorganisms overcome the osmotic pressure created by the saturated salt preservation conditions. Unfortunately, the interest in halophiles decreased after an effective solution for fish preservation using salt from continental mines that contained fewer viable halophilic organisms, was put into practice. In the forties, the interest in extremophiles re-emerged after the discovery that the massive oxidation of metal components in metal mining activities was mainly due to the metabolic activity of chemolithoautotrophic microorganisms that obtained energy from reduced mineral sources, and was not the result of chemical oxidation promoted by the atmospheric oxygen, as had been sustained for a long period of time [2.23]. Extremophile studies grew as a result of increased biotechnological interest in thermophiles based on the application of the Arrhenius equation [2.107]. Finally, the discovery of a new domain of life, Archaea, by Carl R. Woese (originally named Archaebacteria), in which many known extremophiles were included (halophiles, thermophiles, acidophiles, strict anaerobes), led to the explosion of microbial ecology’s search for new extremophilic champions, in an attempt to establish the limits of life [2.108] [2.109].
The systematic exploration of extreme environments has led to the discovery of habitats that had been considered uninhabitable only a few years ago. As a consequence, interest in extreme environments has grown exponentially not only to answer fundamental questions about the mechanisms used by extremophiles to grow in different extreme environments but to explore their biotechnological potential (e.g., biomining, catalysis, energy generation, bioremediation, etc.).
The exploration of extreme environments has also played an important role in the development of Astrobiology. As specified in the NASA Astrobiology roadmap (https://astrobiology.nasa.gov/research/astrobiology-at-nasa/astrobiology-strategy) and the European AstRoMap (http://astromap.esf.org/astromap-roadmap.html) one of the main goals of this transdisciplinary area of research is to characterize extreme environments, the microorganisms developing in them and the mechanisms used to cope with the extreme conditions of the environment, to estimate the possible existence of life outside of planet Earth. The experiments performed by the Viking mission (https://www.nasa.gov/mission_pages/viking), the first astrobiological mission aimed at searching for signs of life on Mars, determined that there was little chance that life could have developed on its surface given the extreme conditions detected there [2.76]. In the last fifty years important advances in microbiology have confronted this rather negative vision. Thanks to the exploration of extreme habitats here on Earth we now know that life is extremely robust and can adapt to a wide range of extreme conditions, thus raising the probability of finding life on other planetary bodies.
In this chapter we will review our current knowledge of Rio Tinto as an acidic geomicrobiological model system and address its astrobiological implications. The main interest of acidophiles is that unlike the rest of the extremophiles, which are simple adaptations to different geophysical constrains (radiation, pressure, temperature, ionic strength, water activity, chaotropicity, etc.), the chemolithotrophic metabolisms of these microorganisms generate the extreme acidic conditions of pH and the associated high concentration of heavy metals in which they dwell.
2.2 Acidic Chemolithotrophy
Natural acidic environments are generally associated with volcanic and mining activities. In the first case sulfur chemolithotrophic microorganisms are the main players while metal and coal mining activities expose sulfidic minerals to aerobic chemolithotrophic microorganisms, facilitating their development and causing the so-called acid mine drainage (AMD) or acid rock drainage (ARD), both of which lead to serious environmental problems due to their high content of soluble heavy toxic metals [2.61] [2.62].
The mechanism by which chemolithotrophic microorganisms conserve energy using reduced sulfidic minerals has been under debate for many years [2.30]. The demonstration that ferric iron generated by iron oxidizing microorganisms is responsible for the chemical oxidation of metal sulfides has conclusively clarified this controversial issue [2.98]. We now know that the differences observed over the years in enrichment cultures using diverse metal sulfides depends on the chemical oxidation mechanism used, which is determined by the crystallographic structure of the mineral substrates. Three metal sulfides—pyrite, tungstenite and molybdenite—can be oxidized by ferric iron through the so-called thiosulfate mechanism, generating sulfuric acid [2.99]. The rest of the metal sulfides can experience ferric iron oxidation through the polysulfide mechanism, producing, in this case, elemental sulfur as final product [2.99], and requiring the additional activity of sulfur oxidizing microorganisms to generate sulfuric acid. The main players in these reactions are the iron-oxidizing microorganisms responsible for maintaining a high concentration of the chemical oxidizing agent, ferric iron.
The acidophilic strict chemolithoautotroph Acidithiobacillus ferrooxidans (formerly known as Thiobacillus ferrooxidans) was isolated for the first time in a coal mine in the middle of the last century [2.23]. Although At. ferrooxidans can obtain energy by oxidizing both reduced sulfur and iron, bioenergetic considerations ignored the role of reduced iron as an important source of energy for chemolithotrophic organisms for many years [2.90] [2.7] [2.30]. But the isolation and characterization of the strict chemolithotroph Leptospirillum ferrooxidans, which can only grow using ferrous iron as its source of energy, and the evaluation of its important role in biohydrometallurgical operations, has finally changed this point of view [2.91] [2.61] [2.48] [2.30]. In addition, it is now well-known that iron can also be oxidized in anaerobic conditions through anoxygenic photosynthesis using reduced iron as reducing power [2.106] or anaerobic respirations using nitrate as an electron acceptor [2.16], although the mechanism in this case is still very controversial [2.64] [2.20] [2.65] [2.110].
The current demonstration that subsurface chemolithotrophic microorganisms participate very actively in the dark biosphere, already predicted by Darwin almost two hundred years ago, has opened interesting perspectives not only in microbial ecology but also in astrobiology [2.52] [2.15] [2.86] [2.21] [2.111] [2.9] [2.10] [2.12] [2.87] [2.43]. There is an increasing list of alternative sources of chemolithotrophic energy (H2,
Extreme acidic environments