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Deliquescence-induced formation and habitability of chloride and perchlorate brines
M. Sc. Chem.
Jacob Heinz
ORCID: 0000-0002-8237-4713
von der Fakultät II - Mathematik und Naturwissenschaften
der Technischen Universität Berlin
zur Erlangung des akademischen Grades
Doktor der Naturwissenschaften
Dr. rer. nat.
genehmigte Dissertation
Promotionsausschuss:
Vorsitzende: Prof. Dr. rer. nat. Birgit Kanngießer
Gutachter: Prof. Dr. rer. nat. Dirk Schulze-Makuch
Gutachter: Prof. Dr. rer. nat. Kai Finster
Tag der wissenschaftlichen Aussprache:
12.08.2019
Berlin 2019
Preface
II
Preface
This thesis was written at the Center for Astronomy and Astrophysics at the Technical
University of Berlin and was embedded in the “Habitability of Martian Environments”
(HOME) project (ERC grant no. 339231). Most laboratory work was carried out at the
laboratory of the Astrobiology Group housed at the Institute for Chemistry, and at the
Center for Electron Microscopy (ZELMI) at the TU Berlin.
This study is written in English and is presented as a cumulative doctoral thesis
containing an introduction, three first-author publications, and a conclusion part as well as
additional material provided in the Supplementary Information. The first publication
embedded in this thesis was published in the journal “Geophysical Research Letters” with
an impact factor of 4.339 (2017), while the other two publications were published in the
journal “Astrobiology” with an impact factor of 3.610 (2017).
Acknowledgements
III
Acknowledgements
I would like to express my special thanks to my first supervisor, Prof. Dr. Dirk Schulze-
Makuch, for giving me the opportunity to conduct this interesting research work in the field
of astrobiology and for his invaluable guidance, continuous support and encouragement.
Furthermore, I would like to specially thank Prof. PhD Sam Kounaves for additional
guidance, Prof. PhD Kai Finster for evaluating my doctoral thesis, and Prof. PhD Lyle Whyte
for providing input on the bacterial strain Planococcus halocryophilus used in this study.
This thesis could not have been achieved without the help and support of numerous
excellent co-authors and members of the Astrobiology Research Group at the TU Berlin,
namely Dr. Janosch Schirmack, Dr. Alessandro Airo, Deborah Maus, Annemiek Waajen,
Armando Alibrandi, Laura Jentzsch, Felix Arens, Yunha Hwang, Christof Sager, and Max
Riekeles. I am especially grateful to Debbie for her great help with the metabolomics
experiments, to Janosch, Annemiek and Armando for their support in the lab, and to P.
halocryophilus for surviving many torturing experiments. Finally, I want to thank my beloved
family and friends for their support.
Abstract
IV
Abstract
The availability of liquid water on Mars is one of the key factors for its habitability.
While there is strong morphological and geochemical evidence for the existence of large
water bodies on the surface of Early Mars, at the present time, the planet is dry, cold and
hostile. However, liquid water might still be found in niches like cold brines. These are
especially relevant for Mars since several hygroscopic salts have been detected in the
Martian regolith which cause a significant freezing point depression of water and, hence,
enhance the habitability range of Mars to subzero temperatures. Formation of these brines
could occur through deliquescence, i.e. water absorption by these salts followed by
dissolution of the salts in the absorbed water. This process might has already been observed
on Mars, namely by the formation of Recurring Slope Lineae (RSL) which are dark, flow-like
features extending downslope from bedrock outcrops.
In this study, both the formation process of RSL caused by deliquescence of various
perchlorate (ClO
4-
) and chloride (Cl
-
) salts, and the survivability of the halo- and cryotolerant
bacterial strain Planococcus halocryophilus within brines has been investigated. It was
found that measuring electrical conductivity (EC) is an excellent method for following the
process of deliquescence-induced RSL formation. The results of these experiments revealed
that the darkening of soil typical for RSL can occur very fast, e.g. after 2.5 hours for soil
containing calcium perchlorate (Ca(ClO
4
)
2
) under the provided experimental conditions
(25°C, 70–85% RH), and requires only small amounts of intergranular water. In contrast, the
formation of larger amounts of bulk water requires substantially longer, e.g. 17 days for soil
containing magnesium perchlorate (Mg(ClO
4
)
2
) under the same experimental conditions.
This suggests that RSL on Mars do actually not represent flows of briny water but a
rewetting of salt-cemented soils generated by the evaporation of water tracks that flowed
down the hills at a time when Mars had a warmer and wetter climate.
The brines that formed via deliquescence were too concentrated to enable growth of
P. halocryophilus within them. However, an enhanced survivability with decreasing
temperature was observed. This effect was most pronounced in calcium chloride (CaCl
2
)
containing samples. Additionally, we found that the presence of sodium chloride (NaCl) is
Abstract
V
beneficial for the survival of P. halocryophilus during freeze/thaw cycles. To enable bacterial
growth in these salty samples a dilution of the brines is necessary. Hence, the maximum salt
concentration suitable for growth at 25°C and 4°C was determined for six Cl
-
and ClO
4-
salts.
The results showed an increased CaCl
2
tolerance of P. halocryophilus at 4°C compared to
25°C, while the tolerances to other salts were similar or lower at 4°C compared to 25°C. The
highest ClO
4-
tolerance reported to date was found with 12 wt% NaClO
4
at 25°C. Growth of
P. halocryophilus under these salty conditions yielded serval stress responses like cell
clustering, formation of nanofilaments, cell encrustation, and formation of different cell
colony morphologies.
Putting all together, this study provides important and coherent insights in the
formation and habitability of brines as they might occur on Mars. The results of a large set
of experiments give an impression on how life on Mars could have adapted to its cold and
salty environmental conditions and what influence different salt species and variations in
temperature and salt concentration might have.
Zusammenfassung
VI
Zusammenfassung
Flüssiges Wasser ist eine der wichtigsten Voraussetzung für die Existenz von Leben auf
dem Mars. Während Oberflächenstrukturen und geologische Funde darauf hindeuten, dass
auf dem Mars einst größere Gewässer existierten, präsentiert sich der Planet heute als
trocken, kalt und lebensunfreundlich. Es ist jedoch wahrscheinlich, dass flüssiges Wasser
nicht gänzlich von der Mars-Oberfläche verschwunden ist. So gibt es Hinweise auf flüssige
Salzlösungen, sogenannte „Brines“, die zumindest temporär auf der Planetenoberfläche
stabil sind. Die Wahrscheinlichkeit ihrer Existenz ist durch den Nachweis hygroskopischer
Salze auf dem Mars noch einmal gestiegen, denn diese können in einem „Deliqueszenz“
genannten Prozess Wasser aus der dünnen Mars-Atmosphäre anziehen und sich in diesem
Wasser auflösen. Es gibt Hinweise darauf, dass dieser Prozess bereits in Form von jährlich
wiederkehrenden, dunklen Ablaufrinnen (Recurring Slope Lineae, RSL) beobachtet wurde.
Für die vorliegende Dissertation wurden Experimente durchgeführt und ausgewertet,
die sowohl das Verständnis für die Deliqueszenz-induzierte Entstehung von RSL vergrößern,
als auch die sich bildenden Brines in Bezug auf ihre mikrobiologische Habitabilität
untersuchen sollen. Es hat sich gezeigt, dass die bei der Bildung der RSL beteiligte
Wasserabsorption hervorragend mit der elektrischen Leitfähigkeit des Bodens korreliert.
Die Ergebnisse der Experimente haben verdeutlicht, dass die für RSL typische Verdunklung
des Bodens sehr schnell einsetzen kann. So treten zum Beispiel im Falle von Ca(ClO
4
)
2
-
haltigen Böden bereits 2,5 Stunden nach dem Start des Experiments (25°C, 70–85%
Luftfeuchte) Verdunklungen auf. Dafür werden nur geringe Mengen intergranularen
Wassers benötigt. Im Gegensatz dazu bedarf es deutlich mehr Zeit bis sich größere
Flüssigkeitsmengen in Form von Tropfen herausbilden, im Fall von Mg(ClO
4
)
2
-haltigen
Böden 17 Tage. Das lässt vermuten, dass RSL auf dem Mars keine Ströme flüssigen Wassers
darstellen, sondern vielmehr nur das temporäre Feuchtwerden salz-zementierter Böden,
die sich beim Verdunsten von Wasser bildeten, das einst floss, als der Mars ein wärmeres
und nasseres Klima aufwies.
Die Habitabilität von Brines wurde beispielhaft am Überleben und Wachstum des salz-
und kältetoleranten Bakterienstammes Planococcus halocryophilus untersucht. Es stellte
Zusammenfassung
VII
sich heraus, dass Brines, die sich durch Deliqueszenz bilden, zu stark konzentriert sind, um
Wachstum von P. halocryophilus zu ermöglichen. Es konnte jedoch gezeigt werden, dass
dessen Überlebensrate deutlich ansteigt, wenn die Temperatur der Brines gesenkt wird.
Dieser positive Effekt war am stärksten in CaCl
2
-haltigen Lösungen ausgeprägt. Außerdem
stellte sich heraus, dass sich die Anwesenheit von NaCl positiv auf die Überlebensfähigkeit
von P. halocryophilus während des wiederholten Einfrierens und Auftauens der Brines
auswirkt. Um jedoch Zellwachstum in diesen Lösungen beobachten zu können, muss die
Salzkonzentration reduziert werden. Daher wurde für sechs unterschiedliche Cl
-
- und
ClO
4-
-Salze bei 4°C und 25°C die maximale Salzkonzentration bestimmt, bei der noch
bakterielles Wachstum nachgewiesen werden kann. Die Ergebnisse zeigten unter anderem,
dass die CaCl
2
-Toleranz durch Herabsenken der Temperatur von 25°C auf C merklich
gesteigert werden kann, während die Toleranzen gegenüber der anderen Salze bei 4°C
ähnlich oder gar geringer waren als bei 25°C. Zudem weist P. halocryophilus mit 12 Gew.%
NaClO
4
bei 25°C die höchste bisher beschriebene ClO
4-
-Toleranz auf. Zellwachstum unter
diesen salzigen Bedingungen führte zu interessanten Stressreaktionen, wie zum Beispiel zur
Ausbildung von Zellclustern mit Nanofilamenten, Krustenbildung um einzelne Zellen oder
die Herausbildung neuer Zellkolonie-Morphologien.
All diese Funde und experimentellen Ergebnisse liefern einen entscheidenden Einblick
in die Entstehung und die potentielle Habitabilität von Brines auf dem Mars. Sie vermitteln
einen Eindruck wie sich Leben an die kalten und salzigen Bedingungen angepasst haben
könnte und welchen Einfluss die unterschiedlichen Salztypen und Schwankungen in
Temperatur und Salzkonzentration haben können.
Contents
VIII
Contents
Preface ......................................................................................................................... II
Acknowledgements ...................................................................................................... III
Abstract ....................................................................................................................... IV
Zusammenfassung ....................................................................................................... VI
Contents .................................................................................................................... VIII
List of Figures ............................................................................................................... XI
List of Tables .............................................................................................................. XIII
Abbreviations and chemical formulas ......................................................................... XIV
1. Introduction ........................................................................................................... 1
1.1 Environmental conditions on Mars and the Atacama Desert, Chile, as Mars-
analogue field site ................................................................................................... 1
1.2 Salts on Mars and deliquescence-induced brine formation .................................... 3
1.3 Recurring Slope Lineae (RSL) on Mars ..................................................................... 6
1.4 Microbial habitability of RSL-analogue brines ......................................................... 8
1.4.1 Water activity and other habitability-limiting factors ....................................... 8
1.4.2 Habitability of Cl
-
-containing brines .................................................................... 9
1.4.3 Habitability of ClO
4-
-containing brines .............................................................. 10
1.4.4 Microbial adaptations to salt stress .................................................................. 11
1.5 Aim of this study and overview of the publications .............................................. 13
2. Publication I: Deliquescence-induced wetting and RSL-like darkening of a Mars
analogue soil containing various perchlorate and chloride salts ................................ 16
2.1 Introduction ........................................................................................................... 17
2.2 Materials and Methods .......................................................................................... 19
2.2.1 Reagents and sample treatment ....................................................................... 19
2.2.2 Measurements and data treatment ................................................................. 20
2.3 Results .................................................................................................................... 20
2.4 Discussion ............................................................................................................... 24
2.5 Conclusion .............................................................................................................. 25
2.6 Acknowledgments .................................................................................................. 26
IX
3. Publication II: Enhanced Microbial Survivability in Subzero Brines ........................ 27
Abstract ......................................................................................................................... 28
3.1 Introduction ........................................................................................................... 29
3.2 Materials and Methods .......................................................................................... 31
3.2.1 Strain and culture conditions ............................................................................ 31
3.2.2 Experiments in eutectic salt solutions .............................................................. 32
3.2.3 Cell number quantification ................................................................................ 33
3.2.4 Freeze/thaw cycle experiments ........................................................................ 34
3.3 Results .................................................................................................................... 34
3.3.1 Microbial survival rates in chloride brines........................................................ 34
3.3.2 Microbial survival rates in perchlorate brines .................................................. 36
3.3.3 Arrhenius plot ..................................................................................................... 38
3.3.4 Microbial survival rates during freeze/thaw cycles ......................................... 38
3.4 Discussion ............................................................................................................... 40
3.5 Conclusion .............................................................................................................. 44
3.6 Acknowledgments .................................................................................................. 45
Author Disclosure Statement ........................................................................................ 45
4. Publication III: Bacterial growth in chloride and perchlorate brines: Halotolerances
and salt stress responses of Planococcus halocryophilus ........................................... 46
Abstract ......................................................................................................................... 47
4.1 Introduction ........................................................................................................... 48
4.2 Materials and Methods .......................................................................................... 50
4.2.1 Organism and culture conditions ...................................................................... 50
4.2.2 Determination of the maximum salt concentration suitable for growth
(MSCg)......................................................................................................................51
4.2.3 Light, fluorescence and scanning electron microscopy ................................... 52
4.3 Results .................................................................................................................... 53
4.3.1 Growth at 25°C and 4°C ..................................................................................... 53
4.3.2 Cellular and colonial phenotypic salt-stress adaptations ................................ 58
4.4 Discussion ............................................................................................................... 61
4.4.1 Salt-stress response and phenotypic adaptation ............................................. 61
4.4.2 Halotolerances of P. halocryophilus at 25°C and 4°C ....................................... 62
X
4.5 Conclusion .............................................................................................................. 66
Acknowledgments ......................................................................................................... 67
Author Disclosure Statement ........................................................................................ 67
5. Conclusions and Outlook ....................................................................................... 68
6. References ............................................................................................................ 71
7. Supplementary Information .................................................................................. 90
7.1 Effect of the salt/soil ratio on the deliquescence process ..................................... 90
7.1.1 Materials and methods ...................................................................................... 90
7.1.2 Results and discussion ....................................................................................... 90
7.2 RSL-simulating field experiments in the Atacama Desert, Chile ............................ 91
7.2.1 Materials and methods ...................................................................................... 91
7.2.2 Results and discussion ....................................................................................... 91
7.3 Metabolomics studies on P. halocryophilus .......................................................... 93
7.3.1 Materials and Methods ...................................................................................... 93
7.3.2 Results and Discussion ....................................................................................... 94
7.4 Supplementary Information on Publication III ...................................................... 96
7.4.1 Growth curves of P. halocryophilus .................................................................. 96
7.4.2 Ionic strengths and water activities at the MSCg........................................... 109
7.4.3 Cell colony morphologies of P. halocryophilus grown under salt stress
conditions ......................................................................................................... 110
7.4.4 Fluorescence microscopy images .................................................................... 111
8.
List of Publications ............................................................................................... 112
List of Figures
XI
List of Figures
FIG. 1-1: Photos of Atacama Desert, Chile, and the Husband Hill on Mars ........................... 2
FIG. 1-2: RSL occurring at Palikir Crater on Mars ................................................................... 7
FIG. 1-3: Colonies of P. halocryophilus grown on agar plates .............................................. 12
FIG. 2-1: Soil sample photos ................................................................................................. 21
FIG. 2-2: Changes in normalized voltage (N) and RH as a function of time ......................... 23
FIG. 3-1: Bacterial growth curve of P. halocryophilus .......................................................... 32
FIG. 3-2: Survival rates of P. halocryophilus in eutectic Cl
-
samples .................................... 35
FIG. 3-3: Survival rates of P. halocryophilus in ClO
4-
samples .............................................. 37
FIG. 3-4: Arrhenius type plot for all Cl
-
samples and NaClO
4
................................................ 39
FIG. 3-5: Survivability of P. halocryophilus during freeze/thaw cycles ................................ 40
FIG. 4-1: Growth curves of P. halocryophilus at different CaCl
2
concentrations ................. 53
FIG. 4-2: Maximum salt concentrations suitable for growth (MSCg) of P. halocryophilus .. 55
FIG. 4-3: Relative changes in the MSCg induced by lowering the temperature .................. 57
FIG. 4-4: Macroscopically visible salt stress responses ........................................................ 59
FIG. 4-5: Light, fluorescence, scanning electron microscopy images of P. halocryophilus .. 60
FIG. 7-1: Increasing EC caused by deliquescence-induced water absorption of the soil ..... 90
FIG. 7-2: Simulated RSL in the Atacama Desert .................................................................... 92
FIG. 7-3: Temperature, RH and EC data collected during the RSL-simulating experiment .. 92
FIG. 7-4: Growth curves in NaCl containing media at 25°C .................................................. 97
FIG. 7-5: Growth curves in NaCl containing media at 4°C. ................................................... 98
FIG. 7-6: Growth curves in MgCl
2
containing media at 25°C ................................................ 99
FIG. 7-7: Growth curves in MgCl
2
containing media at 4°C ................................................ 100
FIG. 7-8: Growth curves in CaCl
2
containing media at 25°C ............................................... 101
FIG. 7-9: Growth curves in CaCl
2
containing media at 4°C ................................................. 102
FIG. 7-10: Growth curves in NaClO
4
containing media at 25°C .......................................... 103
FIG. 7-11: Growth curves in NaClO
4
containing media at 4°C ............................................ 104
List of Figures
XII
FIG. 7-12: Growth curves in Mg(ClO
4
)
2
containing media at 25°C ..................................... 105
FIG. 7-13: Growth curves in Mg(ClO
4
)
2
containing media at 4°C ....................................... 106
FIG. 7-14: Growth curves in Ca(ClO
4
)
2
containing media at 25°C. ...................................... 107
FIG. 7-15: Growth curves in Ca(ClO
4
)
2
containing media at 4°C. ........................................ 108
FIG. 7-16: Ionic strengths and water activities at the MSCg .............................................. 109
FIG. 7-17: Irregular jagged colonies (type III) of P. halocryophilus ..................................... 110
FIG. 7-18: Mucoid and shiny colonies (type IV) of P. halocryophilus ................................. 110
FIG. 7-19: Fluorescence microscopy images of cell clusters of P. halocryophilus .............. 111
List of Tables
XIII
List of Tables
TAB. 1-1: T
e
, c
e
and DRH values of Cl
-
and ClO
4-
salts and their occurrence on Mars ............ 5
TAB. 1-2: A selection of the highest microbial perchlorate tolerances ............................... 11
TAB. 2-1: DRH values for salts used in the experiments ...................................................... 18
TAB. 2-2: T
V
and T
EC
values monitored during the experiment ............................................ 22
TAB. 3-1: c
e
,T
e
, ionic strengths and a
w
for salt solutions used in this study......................... 33
TAB. 4-1: MSCg values and corresponding physicochemical paramters. ............................ 54
TAB. 7-1: Metabolites detected in lysed samples of P. halocryophilus ............................... 95
Abbreviations and chemical formulas
XIV
Abbreviations and chemical formulas
a
w
Ca
2+
CaCl
2
Ca(ClO
4
)
2
c
e
CFU
Cl
Cl
-
ClO
4-
DRH
EC
IM
M
Mg
2+
MgCl
2
Mg(ClO
4
)
2
MSCg
N
Water activity
Calcium (ion)
Calcium chloride
Calcium perchlorate
Eutectic concentration
Colony forming units
Chlorine
Chloride (ion)
Perchlorate (ion)
Deliquescence relative
humidity
Electrical conductivity
Inoculation method
Molar (mol/L)
Magnesium (ion)
Magnesium chloride
Magnesium perchlorate
maximum salt concentration
suitable for growth
Normalized Voltage
Na
+
NaCl
NaClO
4
PB
PBS
RH
RSL
SEM
ST
T
T
e
T
EC
, T
V
TSB
V
VX
wt%
wt/vol%
Sodium (ion)
Sodium chloride
Sodium perchlorate
Phosphate buffer
Phosphate buffer saline
Relative humidity
Recurring Slope Lineae
Scanning electron microscopy
Sample type
Temperature
Eutectic Temperature
Time until Deliquescence could
be observed visually (T
V
) or via
electrical conductivity (T
EC
)
Tryptic soy broth
Voltage
Excitation Voltage
Weight percentage
Weight per volume (%)
Introduction
1
1. Introduction
1.1 Environmental conditions on Mars and the Atacama Desert, Chile, as Mars-analogue field
site
Characteristic surface morphologies like fluvial valleys, large fluid-eroded channels,
dendritic networks and glacial features (Masson et al., 2001), as well as the occurrence of
minerals like hematite (Christensen et al., 2000), and sulfate deposits (Squyres et al., 2004),
which only form in the presence of liquid water, give evidence that 4.5 3.6 billion years
ago Mars had a warmer and wetter climate (Ramirez, 2017). It had a denser atmosphere
than today and presumably large water bodies on its surface conditions we would call
appropriate for life on Earth. It is likely that this habitable period in the Martian history
lasted long enough to theoretically develop life in form of simple microorganisms since we
found evidence for those on Earth in 3.5 3.7 billions old rocks (Schopf, 1993; Ohtomo et
al., 2014). However, due to the loss of its magnetic field the solar wind stripped away large
parts of the Martian atmosphere which caused an irreversible climate change leading to the
cold, dry and hostile planet that we know from today (Vaisberg, 2015; Jakosky et al., 2017).
Hence, potential Martian microorganisms would have had to adapt to a gradually decrease
in water availability and to lower water activities.
Such a transition from a wet and habitable to a dry and hostile environment over
geological timescales can be investigated in several environments on Earth. One of the most
studied Mars-analogue field sites in this context is the Atacama Desert in Chile (Fig. 1-1A)
which had a humid climate 14 - 35 million years ago but became one of the driest places on
Earth due to the Andean orogeny causing a rain shadow effect at the desert’s eastern
border while the Humboldt Current running parallel to the desert prevents precipitation in
the western coastal areas (Dunai et al., 2005).
Introduction
2
FIG. 1-1: Photo of the Yungay Valley in the Atacama Desert, Chile, taken during the field trip in 2018
(A) and a section from a panorama image from the top of Husband Hill on Mars taken from NASA
Mars Rover Spirit (Credit: NASA/JPL-Caltech/Cornell Univ.; NASA ID: PIA17760) (B).
Investigating the microbial adaptions to the increasing dryness and the survival
strategies in such a Mars-analogue environment is a major goal of the Astrobiology
Research Group at the Center for Astronomy and Astrophysics at the TU Berlin where this
thesis was elaborated. Results achieved from several field trips gave evidence that even in
the hyperarid Atacama soils microbial life can be active, at least temporally (Schulze-
Makuch et al., 2018).
Introduction
3
However, the environmental conditions on today´s Mars (Fig. 1-1B) are even more
challenging. There, microbes would have to struggle with low temperatures (-138°C +30°C
(Jones et al., 2011)), low pressures (6 8 mbar (Catling, D.C., Leovy C. 2006)), and high doses
of galactic cosmic rays (180 225 μGy/day (Hassler et al., 2014)) and UVB and UVC radiation
(361 kJ/m
2
(Cockell, 2000)). Under these temperature and pressure conditions bulk liquid
water is not stable in most locations at the Martian surface. Pure water can only sustain as
water vapor in the atmosphere, in form of ice on the Martian surface, as a liquid in the
deeper subsurface or as supercooled interfacial water in the Martian regolith (Martínez and
Renno, 2013).
Solid water ice has been detected at the poles and in the shallow subsurface, e.g. by
the sounding radar SHARAD on the Mars Reconnaissance Orbiter (Grima et al., 2009) and
the Gamma-Ray Spectrometer on Mars Odyssey (Boynton et al., 2002), respectively. The
total water vapor amount in the Martian atmosphere can reach values of 60 70
precipitable microns (pr μm) in the northern summer (Trokhimovskiy et al., 2015), while the
relative humidity (RH) on Mars ranges from nearly 0% during daytime up to 100% in the
morning where frost can occur (Martínez et al., 2017). However, the stability range of liquid
water can be expanded to subzero temperatures and lower atmospheric pressures by
adding solutes.
1.2 Salts on Mars and deliquescence-induced brine formation
These solutes can be provided by various types of hygroscopic salts that occur on the
Martian surface. Evidence for their occurrence exists for sulfates (Kounaves et al., 2010b),
carbonates (Niles et al., 2013), nitrates (Stern et al., 2015), bromides (Clark et al., 2005),
chlorates (Kounaves et al., 2014a), chlorides (Hecht et al., 2009), and perchlorates (Hecht
et al., 2009; Kounaves et al., 2010a). The focus of this study is on the latter two types of salt
which are widely distributed on Mars (Keller et al., 2007; Kounaves et al., 2014b) and cause
intense freezing point depressions (Möhlmann and Thomsen, 2011).
Introduction
4
In general, the intensity of the freezing point depression in a given salt-water system is
dependent on the type of salt and its concentration and can be visualized by a water-salt
phase diagram (reviewed e.g. in Hennings, 2014). The maximum freezing point depression
is reached at the eutectic point composed of a specific eutectic salt concentration (c
e
) and
eutectic temperature (T
e
). When the temperature is above the T
e
of a salt-water mixture
liquid salt solutions (brines) can be formed directly by water ice getting in contact with salts
(Fischer et al., 2014). Another brine formation mechanism is given by deliquescence, which
is defined by the process where a hygroscopic salt absorbs water from the atmosphere and
dissolves in the absorbed water (Davila et al., 2010). To initiate this process the RH has to
be above the deliquescence relative humidity (DRH) of a specific salt and the temperature
above T
e
. DRH values for all salts relevant for this study are summarized in Table 1-1
together with their T
e
and c
e
values as well as their occurrence on Mars.
On the one hand, both requirements for deliquescence, i.e. temperatures above T
e
and
a RH above the DRH of the salt of interest, occur only rarely at the same time on the Martian
surface (Gough et al., 2011; Nuding et al., 2014). On the other hand, once a liquid brine has
formed the recrystallization of the salt hydrate is kinetically hindered and, therefore, the
brine can persist as metastable solution at temperatures below T
e
(Toner et al., 2014b) and
at RHs below the DRH (Gough et al., 2011). Investigations on the stability of Ca(ClO
4
)
2
solutions showed that an eutectic brine of this salt could exist metastable on the surface of
Mars for 17 hours of a Martian day (called “sol”, 24.66 hours) under Martian temperature,
pressure and RH conditions (Nuding et al., 2014).
Although the amount of studies investigating deliquescence phenomena has been
increasing recently, important questions, especially regarding the kinetics of the
deliquescence process, remain unclear: Is the water uptake within the short window of RH
> DRH and temperature > T
e
long enough to form a brine, and which influence on the
deliquescence process have parameters like temperature, pressure, hydration state of the
salt, surrounding soil particles, and grain sizes?
Introduction
5
TAB. 1-1: Te, ce and DRH values of various Cl- and ClO4- salts as well as their occurrence on Mars.
Salt Eutectic Point DRH (%)*
[at T (°C)] Occurrence on Mars
T
e
(°C) c
e
(mol/l)
NaCl -22
a
5.2
a
75 [20]
e
,f
Chlorine (Cl) is globally
distributed
i
, but can be in form of
Cl
-
or ClO
4-
ClO
4-
: Cl
-
ratio of approx. 4 at
the Phoenix landing site
j
MgCl
2
-33.5
a
2.79
a
33 [20]
f
CaCl
2
-50
a
3.9
a
32 [20]
e
80 [-50]
g
NaClO
4
-34
b
9.06
b
51 [0]
h
65 [-45]
h
0.4 – 0.6 wt. % ClO
4-
in the
Martian soil
j
with probably
Ca(ClO
4
)
2k
or Mg(ClO
4
)
2l
as parent
salt
Presumably widespread on
Martian surface
m
Mg(ClO
4
)
2
-57
c
3.52
a
42 [0]
h
55 [-50]
h
Ca(ClO
4
)
2
-77.5
d
4.2
d
13 [0]
h
55 [-50]
h
*referring to the highest salt hydration state existing at the respective temperature. DRH values for
decreased hydration states can be lower (Gough et al., 2016).
References: a(Möhlmann and Thomsen, 2011), b(Hennings et al., 2013), c(Stillman and Grimm, 2011),
d(Pestova et al., 2005), e(Cohen et al., 1987), f(Greenspan, 1977), g(Gough et al., 2016), h(Nuding et
al., 2014), i(Keller et al., 2007), j(Hecht et al., 2009), k(Kounaves et al., 2014b), l(Toner et al., 2015),
m(Clark and Kounaves, 2016)
Introduction
6
1.3 Recurring Slope Lineae (RSL) on Mars
While recently a subsurface brine lake has been discovered near the Martian south
pole (Orosei et al., 2018), there is no clear proof but several strong indications that
deliquescence and/or temporally stable liquid brines can also occur occasionally on the
surface of Mars. For example, the darkening, growth and subsequent disappearance of
particles on the Phoenix lander struts were interpret as deliquescence of saline mud and
down-dripping of the resulting brine (Rennó et al., 2009). One of the most promising
evidence for the temporal occurrence of briny surface water is the observation of RSL
identified by the Mars Reconnaissance Orbiter (McEwen et al., 2011a).
RSL are relatively dark flow-like features on Mars that extend downslope from bedrock
outcrops and occur annually during spring and summer, especially on steep, equator-facing,
southern slopes (Fig. 1-2) (Runyon and Ojha, 2014). Although the role of liquid water on the
formation of RSL has been questioned (Edwards and Piqueux, 2016) and dry granular flow
mechanisms have been proposed (Dundas et al., 2017) there is spectral evidence for
hydrated ClO
4-
salts being present within the RSL while being absent in the surrounding soil
(Ojha et al., 2015). This indicates that the formation of salt hydrates and their corresponding
brines likely play an important role in the RSL formation process.
However, the exact mechanism of RSL formation is still not well understood and
requires more laboratory and simulation experiments. Therefore, within the scope of this
thesis lab experiments have been conducted investigating the deliquescence process as
potential trigger of RSL. These experiments are described in the first publication of this
thesis (chapter 2) and some follow-up experiments are shortly summarized in chapter 7.1.
Furthermore, during the Atacama Desert field trip in 2018 RSL-simulating field experiments
were carried out (unpublished data, chapter 7.2). The results from the field experiments
showed that a saturated solution of NaCl poured down a hill forms a RSL-like darkened track
that dries out slowly during several days (Fig. 7-2). Nevertheless, when the RH increased in
the night and morning hours the briny RSL-like track absorbed additional water correlating
with an increase in EC (Fig. 7-3). However, the water amount evaporating during daytime
exceeded the water amount absorbed through deliquescence in the night and morning.
Introduction
7
Hence, no growth but only fading of the RSL-like track could be observed. The more
hygroscopic and therefore more promising ClO
4-
salts could not be used due to safety
restrictions. Thus, additional field experiments also considering perchlorates should be
conducted in the future.
FIG. 1-2: RSL (indicated by black arrows) occurring at Palikir Crater on Mars imaged by the HiRISE
camera on NASA Mars Reconnaissance Orbiter (Credit: NASA/JPL-Caltech/Univ. of Arizona; NASA ID:
PIA17933).
Introduction
8
1.4 Microbial habitability of RSL-analogue brines
1.4.1 Water activity and other habitability-limiting factors
The habitability of salt solutions is determined by two main factors: the type of salt and
its concentration. When talking about cold brines (cryobrines) also the effect of
temperature has to be considered as will be discussed more detailed in the Publications II
and III of this thesis (chapters 3 and 4, respectively). At high salt concentration the limiting
factor for habitability at a specific temperature is usually given by the water activity (a
w
)
which describes the amount of free biologically available water molecules. In pure water all
water molecules are accessible for microorganism and, therefore, a
w
= 1. In brines the salt
ions bind water molecules in their hydration shells and reduce therefore the a
w
. On Earth,
the lowest a
w
supporting life is approx. 0.61 (Stevenson et al., 2015).
However, additional lethal effects of the solutes can lead to a reduced halotolerance.
These toxic effects include, among others, salt-induced pH changes (Yaganza et al., 2009),
membrane destabilization (Xie and Yang, 2016), molecular mimicry (Cianchetta et al., 2010),
and chaotropicity of ions causing a destabilization of macromolecules like proteins
(Hallsworth et al., 2003; Hallsworth et al., 2007). Additionally, for brines with a high
divalent:monovalent ion ratio ionic strength might be the limiting factor for life rather than
water activity (Fox-Powell et al., 2016). Results from recent experiments conducted in our
research group indicated that one parameter, among others, effecting the habitability of
brines is the strength of hydration shells around ions (especially anions) (Waajen et al.,
2019, in preparation). The stronger the hydration shell around an ion the lower its cell
membrane permeability and, hence, its toxicity (see also Publications II and III).
Introduction
9
1.4.2 Habitability of Cl
-
-containing brines
Halophilic microorganisms can thrive in saturated NaCl solutions (6.1 M, a
w
= 0.75 at
25°C) (Oren, 2008) and, thus, inhabit entrapped salt rocks (Kunte et al., 2002). Endolithic
bacteria in the hyperarid core of the Atacama Desert, Chile, can utilize water condensed
from the atmosphere via deliquescence of NaCl deposits (Davila et al., 2008). Experiments
carried out within our research group showed that halophilic methanogenic archaea can
survive desiccation in Mars-analogue soil interspersed with NaCl and regain their viability
(methane production) after water provision through NaCl deliquescence [Maus et al.,
2019].
While the habitability of NaCl brines is well investigated, studies focusing on life in non-
NaCl brines are sparser although those are more relevant for simulating Mars-analogue
environments (chapter 1.2). Several organisms have been isolated form the Dead Sea which
contains besides Na
+
(1.54 M) and Cl
-
(6.48 M) large amounts of Mg
2+
(1.98 M) and Ca
2+
(0.47 M) (Oren, 2010). Due to halite precipitation the divalent:monovalent ion ratio in the
Dead Sea is even increasing with time which decreases the habitability. Blooms of
microorganism only occur after very rainy winters when salt concentrations in the Dead Sea
are diluted indicating that the salt-induced limit of life is nearly reached and microbes in the
Dead Sea are dying (Oren, 2010).
Two organisms isolated from the Dead Sea are Haloferax volcanii which can grow in
the presence of 2 M Na
+
and 1.4 M Mg
2+
(Mullakhanbhai and Larsen, 1975) and
Halobaculum gomorrense which can grow in the presence of 0.5 M NaCl and 1.5 to 2.0 M
MgCl
2
and can even tolerate high CaCl
2
concentrations of up to 1 M (in the presence of 2.1
M NaCl and 15 mM MgCl
2
) (Oren, 1983). These and other Dead Sea microorganisms require
divalent cations at relatively high concentration levels (approx. 75 mM Mg
2+
) for survival
(Cohen et al., 1983). It has been stated that the maximum MgCl
2
concentration suitable for
life is limited by its chaotropicity and is around 2.3 M in the absence of compensating
kosmotropic substances (Hallsworth et al., 2007).
Introduction
10
Halophilic fungi can tolerate up to 2.1 M MgCl
2
or 2.0 M CaCl
2
(Zajc et al., 2014).
Environments with markedly higher MgCl
2
or CaCl
2
concentrations, e.g. 5 M MgCl
2
in the
Discovery Basin (Hallsworth et al., 2007) or 3.7 M CaCl
2
in the Don Juan Pond, Antarctica
(Marion, 1997; Samarkin et al., 2010), are thought not to be inhabited by active microbial
communities.
1.4.3 Habitability of ClO
4-
-containing brines
On Earth natural occurring ClO
4-
salts can be found only in low concentrations in very
dry environments like the Atacama Desert, Chile (Ericksen, 1981; Catling et al., 2010), or the
Dry Valleys, Antarctica (Kounaves et al., 2010c). Hence, the scientific interest in the
habitability of ClO
4-
brines was limited prior the detection of ClO
4-
on Mars in 2008 (Hecht
et al., 2009). Even today, more than 10 years later, little is known about microbial ClO
4-
tolerances and toxicity effects of the ClO
4-
anion to microorganisms.
There have been several studies investigating the dissimilatory reduction of ClO
4-
by
bacteria especially in context of anthropogenic ClO
4-
ground water contamination
(reviewed in Coates and Achenbach, 2004; Bardiya and Bae, 2011), however, in these
studies ClO
4-
concentrations of only approx. 1 mM are typical which is far below the ClO
4-
concentrations expected to occur in Martian brines (Al Soudi et al., 2017). Only a few studies
focused on determining the maximum ClO
4-
concentration suitable for growth of halophilic
microorganisms. The highest halotolerances to ClO
4-
described prior this study are
summarized in Table 1-2.
Introduction
11
TAB. 1-2: A selection of the highest microbial perchlorate tolerances reported prior this thesis.
Organism Salt providing
ClO
4-
Perchlorate
tolerance
[mol/l ClO
4-
]
Reference
Halomonas venusta
NaClO
4
1.0 (Al Soudi et al.,
2017)
Mg(ClO
4
)
2
0.5 (inconsistent
results for 1.0 M)
Halorubrum lacusprofundi NaClO
4
0.8 (Laye and
DasSarma, 2018)
Mg(ClO
4
)
2
0.6
Haloferax mediterranei NaClO
4
0.6 (Oren et al., 2014)
Hydrogenothermus
marinus NaClO
4
0.45 (Beblo-Vranesevic
et al., 2017)
1.4.4 Microbial adaptations to salt stress
Halophilic and halotolerant microorganisms developed two approaches to cope with
high salt concentrations, which are the organic-osmolyte mechanism and the salt-in-
cytoplasm mechanism (Kunte et al., 2002). The first one encompasses the production or
accumulation of highly water-soluble organic solutes in the cytoplasma of the cell to
counter the external osmotic pressure. These osmolytes (or osmoprotectants) can be sugars
like trehalose, anions like glutamate, or zwitterionic compounds like betaine or proline
(Roberts, 2005). Halophilic microorganisms using the salt-in-cytoplasm strategy enrich salts,
typically potassium chloride (KCl), in their cytoplasma which requires substantial adaptation
of the intracellular enzymatic machinery to the high inner-cellular salt concentration (Oren,
2008). Therefore, organisms using this strategy cannot tolerate low salt concentrations
since their highly adapted proteins denature under these conditions.
For the habitability experiments described in this thesis (Publications II and III) the
survival and growth of Planococcus halocryophilus (Fig. 1-3) in Cl
-
and ClO
4-
brines was
studied. This bacterial strain is adapted to thrive under the cold and salty conditions
prevailing in its natural habitat, the active layer of permafrost soil in the Canadian Arctic
(Mykytczuk et al., 2012; 2013). Although its name indicates the opposite, P. halocryophilus
Introduction
12
is not halophilic but halotolerant, i.e. it tolerates high salinities but can also grow in salt-free
medium. This indicates that this organism uses the organic-osmolyte mechanism to
counteract high salt concentrations, however, the occurrence of osmolytes in P.
halocryophilus cells grown under salt stress conditions has not been investigated prior this
study. Therefore, we conducted some initial metabolomics experiments (unpublished data,
chapter 7.3). The results showed that cells of P. halocryophilus contain the osmolytes
betaine and proline in large quantities fitting well to the detection of several betaine and
proline transport proteins that are expressed under osmotic stress (Mykytczuk et al., 2013).
FIG. 1-3: Colonies of P. halocryophilus grown on agar plates.
Introduction
13
1.5 Aim of this study and overview of the publications
The major goal of this thesis was to gain a better understanding of the deliquescence-
induced formation of RSL-like brines and to investigate the habitability of those at
temperatures ranging from -30°C to +25°C. For this purpose the following three first-author
papers have been published in international journals:
Publication I: Deliquescence-induced wetting and RSL-like darkening of a Mars analogue
soil containing various perchlorate and chloride salts.
Authors: Jacob Heinz, Dirk Schulze-Makuch, and Samuel P. Kounaves
Journal: Geophysical Research Letters (2016), 43:4880–4884,
https://doi.org/10.1002/2016GL068919 (Open Access)
Aims and summary: To investigate the RSL-analogue brine formation lab experiments were
conducted studying the wetting and darkening of Mars-analogue soil caused by
deliquescence of Cl
-
and ClO
4-
salts dispersed in the soil. The deliquescence process was
followed at constant temperature (25°C) and RH (70 85 %) conditions through visible
observations and EC measurements revealing differences in the time needed to start
deliquescence and in the deliquescence rates of the different salts. Conclusions for possible
RSL formation processes were drawn.
Personal and co-authors contribution: I conducted all experiments described within this
study and wrote the manuscript by myself. Samuel P. Kounaves and Dirk Schulze-Makuch
were involved in the data interpretation and helped to improve the manuscript.
Introduction
14
Publication II: Enhanced Microbial Survivability in Subzero Brines.
Authors: Jacob Heinz, Janosch Schirmack, Alessandro Airo, Samuel P. Kounaves, and Dirk
Schulze-Makuch
Journal: Astrobiology (2018), 18:1171–1180, https://doi.org/10.1089/ast.2017.1805 (Open
Access)
Aims and summary: The goal of this study was the investigation of the habitability of Mars-
relevant brines that could result from deliquescence of Martian salts (see Publication I). For
this purpose the survival of P. halocryophilus in these salt solutions was studied. In a first
set of experiments the survivability of P. halocryophilus in eutectic brines was investigated
at temperatures ranging from -30°C to 25°C. These experimental conditions were chosen
because temperatures on Mars are mostly in the subzero range and deliquescence of salts
always results in saturated solutions (which corresponds to the eutectic concentration at
the eutectic temperature of the respective salt) before further water absorption of the
brine can dilute the solution to some extent. Since on Mars temperatures are varying and
periodically drop below the freezing point of the brines, putative Martian microbes would
also have to deal with freezing and thawing processes of these brines. Hence, we studied in
a second set of experiments the effect of salts (in this study only NaCl) on the survival of P.
halocryophilus during freeze/thaw cycles.
Personal and co-authors contribution: Approx. 90% of all experiments described within this
study were conducted by myself. Janosch Schirmack helped in some cases with dilution and
plating of the samples during the long-term growth experiments (approx. 10%). The
manuscript was written by myself. All co-authors were involved in the data interpretation
and helped to improve the manuscript.
Introduction
15
Publication III: Bacterial growth in chloride and perchlorate brines: Halotolerances and
salt stress responses of Planococcus halocryophilus.
Authors: Jacob Heinz, Annemiek C. Waajen, Alessandro Airo, Armando Alibrandi, Janosch
Schirmack, Dirk Schulze-Makuch
Journal: Astrobiology (2019), in press.
Aims and summary: At the high salt concentrations investigated in Publication II no growth
of P. halocryophilus was observed. Thus, the question arose how far the Cl
-
and ClO
4-
solutions had to be diluted for bacterial growth to occur. To address this question we
inoculated low-concentrated saline media with P. halocryophilus and adapted the cells
stepwise to higher concentrations to determine the maximum salt concentration suitable
for growth. These experiments were conducted at 25°C (optimum growth temperature) and
at 4°C for examining the effect of a temperature decline. Additionally, the salt stress
responses of P. halocryophilus were investigated visually on agar plates and through
different microscopical techniques to better understand which adaption mechanisms
putative Martian microbes could develop under the cold and briny conditions found on
Mars.
Personal and co-authors contribution: I conducted all growth experiments by myself and
approx. 80% of all microscopical experiments described within this study. Annemiek C.
Waajen, supported by Janosch Schirmack, did the first run of the fluorescence and scanning
electron microscopy experiments (15%) whereas I did run number 2 and 3. Armando
Alibrandi provided some of the light microscopy images (5%). The manuscript was written
by myself. All co-authors were involved in the data interpretation and helped to improve
the manuscript.
Publication I
16
2. Publication I: Deliquescence-induced wetting and RSL-like
darkening of a Mars analogue soil containing various perchlorate
and chloride salts
J. Heinz
1
, D. Schulze-Makuch
1,2
, and S. P. Kounaves
3
1
Center of Astronomy and Astrophysics, Technical University of Berlin, Hardenbergstr. 36,
10623 Berlin, Germany.
2
School of the Environment, Washington State University, Pullman, WA 99164, USA.
3
Department of Chemistry, Tufts University, Medford, MA 02155, USA.
Corresponding author: Dirk Schulze-Makuch (dirksm@astro.physik.tu-berlin.de)
Key Points:
Deliquescence of salts in a Mars simulant soil sample causes a RSL-like darkening.
Forming thicker liquid films or bulk water via deliquescence is a relatively slow
process.
The deliquescence process can be investigated by electrical conductivity
measurements.
Accepted manuscript of:
Heinz, J., Schulze-Makuch, D., and Kounaves, S.P. (2016) Deliquescence-induced wetting and
RSL-like darkening of a Mars analogue soil containing various perchlorate and chloride salts.
Geophys. Res. Lett., 43 (10) 4880-4884, https://doi.org/10.1002/2016GL068919.
Published by American Geophysical Union (AGU) under a CC BY-NC-ND 4.0 license (license terms
cf. http://creativecommons.org/licenses/by-nc-nd/4.0/)
Publication I
17
Abstract
Recurring Slope Lineae (RSL) are flow-like features on Mars characterized by a local
darkening of the soil thought to be generated by the formation and flow of liquid brines.
One possible mechanism responsible for forming these brines could be the deliquescence
of salts present in the Martian soil. We show that the JSC Mars-1a analogue soil undergoes
a darkening process when salts dispersed in the soil deliquesce, but forming continuous
liquid films and larger droplets takes much longer than previously assumed. Thus, RSL may
not necessarily require concurrent flowing liquid water/brine or a salt-recharge mechanism,
and their association with gullies may be the result of previously flowing water and
deposited salts during an earlier warmer and wetter period. In addition, our results show
that electrical conductivity measurements correlate well with the deliquescence rates and
provide better overall characterization than either Raman spectroscopy or estimates based
on deliquescence relative humidity (DRH).
2.1 Introduction
Recurring Slope Lineae (RSL) are narrow (< 5 m) and relatively dark flow-like features
on Mars that extend downslope from bedrock outcrops. The features were identified by the
Mars Reconnaissance Orbiter (MRO) (McEwen et al., 2011a) and occur annually during
spring and summer, especially on steep, equator-facing, southern slopes (Runyon and Ojha,
2014). Several mechanisms have been proposed to explain the occurrence of RSL, ranging
from dry granular flows (McEwen et al., 2011b) to effects caused by rapid heating of
nocturnal frost (Dundas et al., 2015). The best current hypotheses for their formation
involve either the melting of frozen brines, the seasonal discharge of a local aquifer, or via
deliquescence of salts dispersed in the soil (Chevrier and Rivera-Valentin, 2012; McEwen et
al., 2015; Ojha et al., 2015).
Experimental investigations into the formation of brines via deliquescence has been
widely reported (Zorzano et al., 2009; Gough et al., 2011, 2014; Fischer et al., 2014; Nuding
et al., 2014, 2015; Nikolakakos and Whiteway, 2015). These investigations clearly showed
Publication I
18
that the salts present on Mars, such as magnesium and calcium perchlorates or chlorides
(Kounaves et al., 2010a; 2014b), are highly deliquescent and some of their solutions could
be, at least temporally, stable on the surface of Mars. The relative humidity (RH) needed to
start the deliquescence process of a salt, the deliquescence relative humidity (DRH), is
shown in Table 2-1 for some Mars-relevant salts.
TAB. 2-1: Deliquescence relative humidity (DRH) values for salts used in the experiments.
DRH (%) Temperature (K) References
Ca(ClO
4
)
2
·4H
2
O 13 273 (Nuding et al., 2014)
CaCl
2
·6H
2
O 29 298 (Lide, 2003)
MgCl
2
·6H
2
O 33 298 (Lide, 2003)
Mg(ClO
4
)
2
·6H
2
O 42 273 (Gough et al., 2011)
Most of the research has been conducted by investigating phase changes of the salts
with the aid of Raman spectroscopy, whereby the Raman laser beam was focused on small
salt particles or thin layers (Gough et al., 2011, 2014; Fischer et al., 2014; Nuding et al.,
2014, 2015; Nikolakakos and Whiteway, 2015). However, these studies do not take into
consideration that the salts on Mars are probably intimately mixed with the soil.
To date, there have been no reported studies correlating the observed darkening of
Mars analog soils and deliquescence as a function of the types of salts and environmental
parameters such as humidity or temperature. Here we demonstrate that visual observation
in parallel with electrical conductivity (EC), a technique commonly used for detection of
liquid water in soils (McKay et al., 2003; Davis et al., 2010), can be used to monitor the
deliquescence process in mixtures of soil and salt.
Publication I
19
2.2 Materials and Methods
2.2.1 Reagents and sample treatment
The soil salt mixtures consisted of JSC Mars-1a analogue soil and either magnesium
perchlorate hexahydrate Mg(ClO
4
)
2
·6H
2
O (Sigma-Aldrich, Lot # MKBQ3075V), calcium
perchlorate tetrahydrate Ca(ClO
4
)
2
·4H
2
O (Acros Organics, Lot # A0332298), magnesium
chloride hexahydrate MgCl
2
·6H
2
O (Fluka, Analysis # 350301/1696) or calcium chloride
hexahydrate CaCl
2
·6H
2
O (Fluka, Analysis # 349745/163796). Salts were ground in a mortar
before mixing with soil. One sample contained only pure soil. The other samples consisted
of 10 g soil and 0.0123 mol of the corresponding salt hydrate (i.e. 4.075 g Mg(ClO
4
)
2
·6H
2
O;
3.825 g Ca(ClO
4
)
2
·4H
2
O; 2.5 g MgCl
2
·6H
2
O, 2.695 g CaCl
2
·6H
2
O). The salt contents were
chosen sufficiently high to ensure a visible and measurable change during deliquescence
(salt concentrations in RSL are expected to be much higher than at Martian landing sites
and variable salt concentrations might affect their deliquescence). After mixing the
components by shaking in a 30 mL polycarbonate container, the samples were dried for 2
days in a desiccator under vacuum over anhydrous calcium chloride.
To increase the RH in the system the desiccant in the lower part of the desiccator was
replaced by water. A hot plate was used to cycle the temperature in the desiccator between
290 and 298 K to evaporate water until the relative humidity (RH) increased from 40%
(which was the RH in the lab after opening the desiccator and removing the desiccant) to
over 70%. This value increased over several days slowly to a RH of 85% without any
treatment (Fig. 2-2). After 18 days the experiment was stopped. Afterwards the samples
were dried again until there was no measurable conductivity and the samples regained their
light brown color. The experiment was then repeated to ensure reproducibility of the
results.
Publication I
20
2.2.2 Measurements and data treatment
All EC measurements were made using two parallel 1 mm diameter copper wire
electrodes inserted 25 mm apart into the soil samples, and connected to a CR 10 data logger
(Campbell Scientific). The CR 10 is capable of applying an AC excitation voltage that prevents
polarization of the electrodes. The applied excitation voltage (V
X
) results in a current
between the electrodes proportional to the EC of the sample. This current is converted to
a measured voltage V. The observed output value of the data logger, equivalent to the
conductivity, is a normalized voltage N given by:
=
1000
The upper detection limit of this technique is reached when V equals V
X
. That happens
when, due to increasing ion mobility in the sample, the resistance tends to zero, so that EC
goes to infinity. In this case N tends to 1000. The N values can also be converted into
conductivity values (in Siemens per meter) when the cell constant of the system is known
(Stone et al., 1993). The data logger was set to register N values every 5 minutes. RH and
temperature were measured with a HOBO Pro v2 data logger throughout the entire
experiment.
2.3 Results
The pure JSC Mars-1a analogue is a light reddish brown soil (Fig. 2-1a). Mixing it with
the various salt hydrates resulted in a dark brown soil sprinkled with some remaining dry
particles (Fig. 2-1b). The darkening of the sample is due to the wetting of the soil caused by
some minor initial amount of liquid water adsorbed by the hygroscopic salts. After drying,
the soil/salt mixtures regained the light reddish brown color of the pure JSC Mars-1a
analogue soil but with the noticeable exception that near the surface larger clumps of soil
are visible (Fig. 2-1c). Similar clumpy or cloddy soils were observed in the soils at the Phoenix
landing site and attributed to their being wetted at some point in the past (Arvidson et al.,
2009).
Publication I
21
FIG. 2-1: Soil sample photos. a Pure and dry JSC Mars-1a analogue soil. b Soil mixed with wet
Ca(ClO4)2·4H2O. c – Dried sample of soil and Ca(ClO4)2·nH2O.
The results of our experiments are shown in Figure 2-2, where the measured
normalized voltage (N) and the RH in the system are plotted versus the duration of the
experiment in days. Selected images of the samples taken through the glass of the
desiccator at specific points of time are included to show the correlation between the
increasing conductivity and the darkening of the soil due to deliquescence. As expected, at
the beginning of the experiment for RH
~
40%, the samples were dry with N = 0. The changes
in appearance and conductivity that occurred after the RH was increased to 70% are
described below and summarized in table 2-2, where T
V
is the time after the start when first
visible changes (wet grains on the sample surface) were observed and T
EC
the time when EC
started to increase.
About 2.5 hours after increasing the RH to 70%, some of the clumped grains on the
surface of the calcium perchlorate sample started to become wet, as can be seen by the
darkening of these particles compared to the brighter soil beneath (Fig. 2-2a). As the wet
grains are not connected to each other, the conductivity remained at zero. About 19 hours
after the experiment started a complete layer of wet soil had formed (Fig. 2-2b), coinciding
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22
with an increase in conductivity, most likely due to a thin layer of salt water forming around
the soil particles. The increase of conductivity in these first minutes of detection can better
be seen in the enlarged segment of Figure 2-2.
TAB. 2-2: Time after experimental start at which the beginning of deliquescence could be observed
visually (TV) and via electrical conductivity (TEC) in hours (h) and days (d).
Salt (mixed with soil) T
V
T
EC
Ca(ClO
4
)
2
·nH
2
O 2.5 ± 0.5 h 19 h
MgCl
2
·nH
2
O 48 ± 2 h (2 d) 61 h (
~
2.5 d)
Mg(ClO
4
)
2
·nH
2
O 70 ± 4 h (
~
3 d) 72 h (3 d)
CaCl
2
·nH
2
O 108 ± 4 h (
~
4.5 d) 124 h (
~
5 d)
The other samples stayed dry and non-conductive for two days after the start of the
experiment. During this time the diameter of the dark and wet layer in the calcium
perchlorate sample constantly increased in size, which was also mirrored by an increase in
conductivity. After two days some grains on the top of the magnesium chloride sample
became dark and wet, similar to the calcium perchlorate sample. After 2.5 days, an increase
in the conductivity in the magnesium chloride sample was also detected. Similar to the
calcium perchlorate soil mixture, a dark wet layer also formed that grew with time
proportional to the conductivity. Similar results were obtained for the magnesium
perchlorate and calcium chloride samples after 3 and 4.5 days, respectively.
The soil sample with calcium perchlorate started to deliquesce first at a rate similar to
the other salts, but continued at a lower rate after about the 8th day. The rate of increase
for the calcium perchlorate sample reached its maximum after 16 days, where it remained
nearly constant until the end of the experiment (Fig. 2-2). The other samples did not reach
a maximum value, but they approached the detection limit of the technique.
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FIG. 2-2: Changes in normalized voltage (N) and RH as a function of time, and photos of soil samples.
(a–c) The time when sample photos were taken. Wet separated grains on surface of Ca(ClO4)2 · nH2O
sample with no measurable conductivity after 2.5 h (Fig. 2-2a). Thin wet layer of soil in the upper
part of the sample causes first measurable conductivity values after 19 h (Fig. 2-2b). Wet layers and
droplets of salty water in the sample of Mg(ClO4)2 · nH2O with the highest measured conductivity
after 17 days (Figure 2-2c). The enlarged segment of the graph displays the TV values in more detail.
Short data gaps in the curves are results of temporary connection problems with the CR10 data
logger.
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When the experiment was stopped after 18 days, all samples, except the pure soil
which stayed dry, were completely wet and dark brown. In the magnesium perchlorate
sample, which reached the highest conductivity, small liquid droplets and films where
visible on the wall of the vessel after 17 days (Fig. 2-2c). A repetition of the experiment
resulted in very similar curve progressions compared to the first run, with the exception
that a slightly lower deliquescence rate for magnesium chloride was observed.
2.4 Discussion
The results clearly show that the salts in the Mars JSC-1a analogue soil deliquesce when
sufficiently high RH values are reached. However, without any added salts the soil stays
completely dry for 18 days at RH values up to 70 85%, which shows that the wetting of
the other samples is not caused by adsorption or direct condensation of water onto the soil.
The deliquescence process coincides with a darkening of the soil, similar to that observed
for the RSL on Mars. We have shown that EC is an excellent method for monitoring soil
wetting by deliquescence. Some salts (in our case calcium perchlorate) can initiate this
process after only 2.5 hours at RH
~
70%, however, other salts (here magnesium perchlorate,
magnesium chloride and calcium chloride) need several days until they have absorbed
enough liquid water to provide ion mobility, even if their DRH are below the starting RH of
the experiment (70%) (Table 2-1). We found that it takes much more time (in our
experiment 17 days) until sizable liquid droplets and films form under the experimental
conditions used here. Therefore we agree with Fischer et al. (2014) who showed that bulk
deliquescence (meaning the formation of greater amounts of liquids) is a slow process, but
in contrast to their work, we find that some salts like calcium perchlorate can start to
deliquesce much more rapidly (< 3.5 hours). This is seen as the time during which
atmospheric conditions at the Phoenix landing site would meet the conditions necessary
for deliquescence to occur (Möhlmann, 2011).
An interesting observation is that there seems to be no correlation between the T
V
or
T
EC
values of a salt and its DRH value. The calcium perchlorate sample with the lowest DRH
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(13 %) started first to deliquesce, but it was followed chronologically by the samples with
magnesium chloride (DRH 33 %), magnesium perchlorate (DRH 42 %) and calcium chloride
(DRH 29 %). Thus, one cannot predict the order in which different salts start to deliquesce
only by taking the DRH values into consideration. There may be several reasons for this lack
of correlation. One reason may be that the hydration state present at deliquescence may
be different than the hydration state as received due to the desiccation of the samples at
the beginning of the experiment.
Furthermore, the velocity of the deliquescence process can neither be estimated by
DRH nor T
V
or T
EC
values, as can be seen in the flatter slope of the calcium perchlorate
conductivity curve (Fig. 2-2). As calcium perchlorate has the lowest DRH and T
EC
values one
could expect the highest rate of deliquescence and therefore the steepest curve slope, but
this is not so according to our experiments.
2.5 Conclusion
We have shown that the darkening of the soil similar to what is seen at the RSL on Mars
can be reproduced by the wetting of perchlorate and chloride containing soils caused by
deliquescence of these salts. However, due to the longer timescales required to produce
greater amounts of liquid water in the forms of bulk or droplets, it appears likely that the
RSL would not necessarily require the concurrent presence of flowing liquid water or brine.
Thus, it is possible that their association with gullies may be the result of an earlier period
when Mars may have had a warmer and wetter climate that allowed for the melting of
subsurface ice at exposed outcrops and/or the flow of liquid water and subsequent
precipitation of salts on evaporation. This process would have been most effective on the
warmer equator-facing slopes of the craters and dunes, where RSLs are found today. The
steep slopes of these formations may have also impeded new dry soil from covering the salt
deposits. This hypothesis, consistent with the latest spectral evidence for hydrated salts in
the RSL (Ojha et al., 2015), does not require a salt-recharge mechanism since the liquid
water films are formed in-place by the previously deposited salts.
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2.6 Acknowledgments
We thank Chris McKay and Alfonso Davila for donating the CR10 data logger and
helping to improve the experimental setup. Moreover, we thank Raina V. Gough for helping
to improve the manuscript. This project was funded by European Research Council
Advanced Grant Habitability of Martian Environments” (HOME, # 339231). All of the
numerical data for this paper are provided in the figures and are also available in tabular
form from the authors upon request (dirksm@astro.physik.tu-berlin.de).
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3. Publication II: Enhanced Microbial Survivability in Subzero Brines
Jacob Heinz
1
, Janosch Schirmack
1
, Alessandro Airo
1
, Dirk Schulze-Makuch
1,2
, Samuel P.
Kounaves
3,4
1
Center of Astronomy and Astrophysics, Technical University of Berlin, Hardenbergstr. 36,
10623 Berlin, Germany.
2
School of the Environment, Washington State University, Pullman, Washington, USA.
3
Department of Chemistry, Tufts University, Medford, Massachusetts, USA.
4
Department of Earth Science and Engineering, Imperial College London, UK.
Corresponding author: Jacob Heinz (+493031479484; j.heinz@tu-berlin.de)
Running Title: Survivability in Subzero Brines.
Search Terms: Brines; Subzero; Perchlorate; Survival; Halophile; Mars
Accepted manuscript of:
Heinz, J., Schirmack, J., Airo, A., Kounaves, S. P., and Schulze-Makuch, D. (2018)
Enhanced Microbial Survivability in Subzero Brines. Astrobiology, 18(9), 1171–1180. https://
doi.org/10.1089/ast.2017.1805
Published by Mary Ann Liebert under a CC BY 4.0 license (license terms cf.
http://creativecommons.org/licenses/by/4.0)
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Abstract
It is well known that dissolved salts can significantly lower the freezing point of water
and thus extend habitability to subzero conditions. However, most investigations thus far
have focused on sodium chloride as a solute. Here, we report on the survivability of the
bacterial strain Planococcus halocryophilus in sodium, magnesium and calcium chloride or
perchlorate solutions, respectively, at temperatures ranging from +25°C to -30°C.
Additionally, we determined the survival rates of P. halocryophilus when subjected to
multiple freeze/thaw cycles. We found that cells suspended in chloride-containing samples
have markedly increased survival rates compared to those in perchlorate-containing
samples. In both cases the survival rates increase with lower temperatures, however, this
effect is more pronounced in chloride-containing samples. Furthermore, we found that
higher salt concentrations increase survival rates when cells are subjected to freeze/thaw
cycles. Our findings have important implications not only for the habitability of cold
environments on Earth but also for extraterrestrial environments such as Mars, where cold
brines might exist in the subsurface and perhaps even appear temporarily at the surface
such as at Recurring Slope Lineae.
Keywords: Brines; Subzero; Perchlorate; Survival; Halophile; Mars
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3.1 Introduction
Life as we know it requires liquid water as the principle solvent for its biochemistry, but
most planetary surfaces in our Solar System never reach temperatures above the freezing
point of pure water, rendering these localities as likely uninhabitable compared to the
benign climate conditions on Earth. However, the presence of salts can lead to a substantial
freezing point depression down to the eutectic temperature of a given salt-water mixture
(e.g. -50°C for a 31 wt% CaCl
2
solution) and, thus, greatly expand the temperature range for
potential habitats (Möhlmann and Thomsen, 2011). Hence, the question arises whether
microorganisms can thrive or at least survive in such subzero brines.
On Earth, microbial organisms such as yeast can tolerate water activities (a
w
) down to
0.61 (Rummel et al., 2014). However, the lowest salt-induced water activity that halophilic
microorganisms can tolerate is that of a saturated NaCl solution (a
w
= 0.75) while other salts
(e.g. those containing Ca
2+
and Mg
2+
ions) are more inhibitory to cell metabolism (Rummel
et al., 2014). Furthermore, it has been reported that certain cyanobacterial species
embedded in hygroscopic sodium chloride (NaCl) deposits found in the hyperarid soils of
the Atacama Desert are able to utilize water condensed from the atmosphere via
deliquescence (Davila et al., 2008; Davila and Schulze-Makuch, 2016).
Additionally, many halophilic microorganisms can also be psychrophilic or
psychrotolerant (Gounot, 1986; Hoover and Pikuta, 2010). To date, the lowest reported
temperature for microbial growth is -18°C for yeast on frozen surfaces (Collins and Buick,
1989). Metabolic ammonia oxidation has been detected down to -32°C (Miteva et al., 2007)
and, finally, there are indications for photosynthetic activity of lichens at -40°C (de Vera et
al., 2014).
It has been argued that low temperature and high salt tolerances are closely linked,
since at subzero temperatures water ice forms which increases the solute concentration of
the remaining liquid water (Bakermans, 2012). Moreover, chaotropic agents like
magnesium chloride (MgCl
2
), i.e. substances destroying the bulk water structure and
therefore reducing hydrophobic interactions (Gerba, 1984), at moderate concentrations
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can decrease the minimal temperature at which cell division can occur for certain
microorganisms and increase their growth rates at low temperatures, presumably by
increasing the macromolecular flexibility (Chin et al., 2010). Furthermore, some
microorganisms shift their salinity optimum for growth to higher salt concentrations if
exposed to lower temperatures (Gilichinsky et al., 2003).
Organisms have evolved several adaptations for thriving and/or surviving in cold saline
environments. These include production of antifreeze or ice-binding proteins,
cryoprotectants or extracellular polymeric substances (EPS) (Jia et al., 1996; Gilbert et al.,
2005; Kuhlmann et al., 2011), an increase of fatty acids branching to maintain membrane
fluidity (Denich et al., 2003), a higher antioxidant defense against reactive oxygen species
(Chattopadhyay et al., 2011), the expression of isozymes adapted to low temperatures and
high salinities (Maki et al., 2006), or the exclusion of inhibitory ions by accumulating
intercellular compatible solutes (Csonka, 1989).
Most of the studies dealing with brines at subzero temperatures have focused on NaCl
as a solute, the most common salt found in saline environments on Earth. However, certain
environments on Earth are dominated by high concentrations of other salts such as calcium
chloride (CaCl
2
) in Don Juan Pond, Antarctica (Cameron et al., 1972; Dickson et al., 2013) or
sodium and magnesium sulfates in Spotted Lake, Canada (Pontefract et al., 2017).
Furthermore, Martian soils are known to contain various chloride (Cl
-
) and perchlorate
(ClO
4-
) salts (Hecht et al., 2009; Kounaves et al., 2010a), emphasizing the importance of
research in the field of non-NaCl briny habitats at subzero temperatures.
In this study we used the halo- and cryo-tolerant bacterial strain Planococcus
halocryophilus Or1 (DSM 24743
T
) isolated from the active-layer of permafrost soil in the
Canadian High Arctic (Mykytczuk et al., 2012). This organism grows at temperatures
between -15°C and +37°C and under NaCl concentrations of up to 19 wt/vol.% at which
metabolic activity has been detected at temperatures down to -25°C (Mykytczuk et al.,
2013). This bacterial strain shows many cold- and osmotic-stress responses such as the
expression of cold-adapted proteins, the expression of various osmolyte transporters, a
high lipid turnover rate, a high resource efficiency at cold temperatures with an
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accumulation of carbohydrates as energy resource (Mykytczuk et al., 2013) and complex
changes in protein abundances (Raymond-Bouchard et al., 2017). Furthermore, under cold
growth conditions P. halocryophilus develops a nodular sheet-like crust around the cells
(Mykytczuk et al., 2016; Ronholm et al., 2015).
The above described ability of P. halocryophilus to cope with low temperatures and
high salt concentrations makes it an ideal organism for studying if and how well terrestrial
life might be able to survive or even thrive in Martian environments. In particular, we have
investigated how well P. halocryophilus can survive repeated freezing/thawing cycles and
in subzero chloride and perchlorate brines, since such conditions may be temporarily
present on Mars (Martínez and Renno, 2013).
3.2 Materials and Methods
3.2.1 Strain and culture conditions
We used the bacterial strain Planococcus halocryophilus Or1 (DSM 24743
T
) obtained
from the DSMZ (Leibniz Institute DSMZ German Collection of Microorganisms and Cell
Cultures). P. halocryophilus was grown in DMSZ growth medium #92 containing additional
10 wt% NaCl. Its growth curve at 25°C was determined via colony forming units (CFUs) and
cell suspensions used for inoculating the experiments were either retrieved after 4 days
(sample type ST 1) or 7 days (sample type ST 2) of growth (Fig. 3-1).
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FIG. 3-1: Bacterial growth curve of P. halocryophilus in DMSZ growth media #92 + 10 wt% NaCl at
25°C. CFUs obtained as technical duplicates. Crosses mark the sampling times for inoculating of
sample types ST 1 and ST 2.
3.2.2 Experiments in eutectic salt solutions
In all experiments 2 mL of the cell suspension (prepared as described in Section 2.1)
was mixed with 8 mL of a salt solution resulting in 10 mL sample solution with a eutectic
salt concentration. The eutectic compositions of the investigated salts are listed in Table 3-
1, together with the ionic strength, the water activity at 25°C calculated from the Pitzer
equation (Pitzer, 1991) with Pitzer parameters taken from Toner et al. (2015), and the
eutectic temperature. All samples were prepared and analyzed as biological duplicates.
Before mixing cell suspensions and salt solutions the suspensions were cooled to 4°C and
the salt solutions to the respective incubation temperature. Additionally, for testing if ClO4-
preconditioning of the cells has a positive effect on their survival in ClO4- containing
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samples, cell suspensions with either up to 10 wt% NaClO4 or 5 wt% NaClO4 + 10 wt% NaCl
were prepared and incubated for seven days at 25°C.
TAB. 3-1: Eutectic concentrations and temperatures, ionic strength and water activities at 25°C for
salt solutions used in this study.
Eutectic
Concentration
Ionic
strength
water
activity
at 25°C
Eutectic
Temperature
[wt%] [mol/L] [mol/L] [°C] [K]
NaCl 23.3
a
5.20 5.20 0.80 -22 251
a
MgCl
2
21
a
2.79 8.38 0.75 -33.5 239.5
a
CaCl
2
30.2
a
3.90 11.70 0.65 -50 223
a
NaClO
4
52.6
b
9.06 9.06 0.68 -34 239
b
Mg(ClO
4
)
2
44
a
3.52 10.56 0.56 -57 216
c
Ca(ClO
4
)
2
50.1
d
4.20 12.60 0.52 -77,5 195.5
d
a
(Möhlmann and Thomsen, 2011),
b
(Hennings et al., 2013),
c
(Stillman and Grimm, 2011),
d
(Pestova
et al., 2005).
3.2.3 Cell number quantification
The concentration of viable cells in the samples were determined after specific time
intervals via colony formation unit (CFU) counts, and where necessary samples were diluted
in phosphate buffer saline (PBS) containing 21 wt% NaCl or MgCl2 to avoid osmotic bursting
of cells. Highest values of CFU ml-1 were achieved when dilution was done with NaCl
enriched PBS for samples containing NaCl, MgCl2, NaClO4 or Mg(ClO4)2, and MgCl2 enriched
PBS for samples containing CaCl2 or Ca(ClO4)2. Because cell death occurred at higher
temperatures during plating, especially in Ca2+ containing samples, plating for all
experiments described in this study was carried out rapidly at cold temperatures. The
NaCl/MgCl2 enriched PBS was precooled to -15/-30°C and agar plates to 4°C.
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3.2.4 Freeze/thaw cycle experiments
For investigating the effect of dissolved salts on cell survival when subjected to multiple
freeze/thaw cycles, we incubated P. halocryophilus at 25°C for one week in six individual
vials. Three of them contained 10 mL of DMSZ growth medium #92 (with no additional NaCl)
while the other three samples contained additionally 10 wt% NaCl. After incubation all
samples where repeatedly frozen at -50°C, stored at this temperature for between one and
three days and thawed at room temperature until the unfrozen sample reached 20°C, which
took approximately two hours. After taking an aliquot from each sample for CFU
determination the samples were frozen again. These freeze/thaw cycles were repeated up
to 70 times and the survival was tested intermittently. The results for samples with the
same growth media composition were averaged and the standard deviation was calculated.
3.3 Results
3.3.1 Microbial survival rates in chloride brines
The survival rates of P. halocryophilus in eutectic Cl- samples were significantly
increased when the samples were kept at lower temperatures (Fig. 3-2). For example, if P.
halocryophilus was left in NaCl containing samples at room temperature all cells died within
two weeks, while their survival was substantially increased at 4°C, and nearly no CFU
reduction occurred at -15°C. Two samples of ST 2 were investigated for the NaCl system to
confirm reproducibility. Samples of ST 2 had slightly higher starting cell numbers in all cases
studied. However, survival rates of ST 1 and ST 2 samples were similar, although the curve
for the NaCl ST 1 sample at 4°C had a steeper slope during the first 40 days but approached
the slope of the ST 2 curves afterwards.
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FIG. 3-2: Survival rates of P. halocryophilus in eutectic Cl
-
samples. Initial cell cultures were incubated
for 4 days (ST 1) or 7 days (ST 2) at 25°C in growth medium containing 10 wt% NaCl before mixing
them with the salt solution. CFUs were obtained as biological duplicates. Detection limit for CaCl
2
containing samples at 103 CFU/mL results from the dilution factor of 3 that is necessary to decrease
the Ca
2+
concentration on the agar plate sufficiently for colony growth to occur.
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The cell survival results for the MgCl2 containing samples were very similar to those of
NaCl, but at -15°C and -30°C there appears to be a slow reduction of surviving cells. The
survival rates of P. halocryophilus in CaCl2 containing samples at 25°C and C were
significantly lower than those containing NaCl or MgCl2. In contrast, survival rates at subzero
temperatures were comparable to the MgCl2 system, i.e. cells were dying slower at these
lower temperatures.
3.3.2 Microbial survival rates in perchlorate brines
The survival rates of P. halocryophilus in eutectic ClO4- samples (Fig. 3-3) were orders
of magnitude lower than in Cl- samples (Fig. 3-2). Although survivability at lower
temperatures in NaClO4 samples increased, the survival rate is generally so low that even
at -30°C few cells survived for only one day (Fig. 3-3A and 3-3B). For Mg(ClO4)2 and Ca(ClO4)2
containing samples, survival was even lower, where CFU detection was only possible for
samples stored at -30°C and none were detected for samples kept at higher temperatures.
We increased the NaClO4 concentration in the growth media to determine if ClO4-
preconditioning of P. halocryophilus could enhance their survival in eutectic ClO4- samples.
It was found that P. halocryophilus can grow in the presence of up to at least 10 wt% NaClO4
(with no additional NaCl in the growth medium) or up to 10 wt% NaCl + 5 wt% NaClO4.
However, cell growth under these conditions was markedly slower than in ClO4- free
medium. Thus, for the preconditioning experiments we used cells preconditioned with 8
wt% NaClO4 or with 10 wt% NaCl + 3 wt% NaClO4 (Fig. 3-3B). Nevertheless, in these cases
cells grew slower than in the experiments with 10 wt% NaCl in the growth media, which
resulted in a lower starting cell number. Due to the slower growth rates in ClO4- containing
media, the cells should still be in the exponential growth phase after 7 days of incubation.
We found that changing the preconditioning salt from NaCl to NaClO4 does not increase the
survivability in ClO4- containing samples. However, increasing the total salt concentration
by adding 3 wt% NaClO4 on 10 wt% NaCl results in a slight increase in survival. Cells in these
samples doubled their maximum survival time from approximately one day in samples
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containing either 8 wt% NaClO4 or 10 wt% NaCl to two days in samples containing 3 wt%
NaClO4 + 10 wt% NaCl.
FIG. 3-3: (A) Survival rates of P. halocryophilus in ClO
4-
samples. Initial cell cultures were incubated
for 7 days at 25°C in growth medium containing 10 wt% NaCl before mixing them with the salt
solution (B) Effects of different preconditioning methods at -30°C. Before mixing them with the salt
solution, the initial cell cultures were incubated for 7 days at 25°C in growth medium containing
salts as indicated the figure legend. CFUs were obtained in biological duplicates.
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3.3.3 Arrhenius plot
For a better comparison of the temperature dependences of cell survival in different
Cl- and ClO4- containing samples, the data was plotted as an Arrhenius type graph, with the
slopes of the survival rate-fitted lines for all Cl- and NaClO4 containing samples (values for
same salt-temperature combinations were averaged) plotted logarithmically against the
temperature of the sample (Fig. 3-4A). As the slope (S) of these curves is the crucial
parameter for evaluating the extent to which survival is increased with lowering
temperature, the slope values for each curve were plotted as well (Fig. 3-4B).
The slopes for the Cl- containing samples, especially for MgCl2 and CaCl2, flatten below
death rate constants of about 0.1 day-1. However, it has to be kept in mind that the death
rates are on a logarithmic scale and, therefore, the flattening might only be the result of
approaching a non-lethal state, i.e. a death rate of zero. Therefore only the steeper slops of
the curves towards higher temperatures were compared in Figure 3-4B.
3.3.4 Microbial survival rates during freeze/thaw cycles
P. halocryophilus survives repeated freeze/thaw cycles more readily if the growth
medium contains additional NaCl. Without NaCl, the CFU reduction is 20% per freeze/thaw
cycle, whereas an addition of 10 wt% NaCl lowered the death rate to 7% per freeze/thaw
cycle (Fig. 3-5). Cells in the salt-free samples survived up to 70 freeze/thaw cycles, while
extrapolation of the death rate curve for the samples containing 10 wt% NaCl reveals that
cells in these samples could survive up to approximately 200 freeze/thaw cycles.
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FIG. 3-4: (A) Arrhenius type plot for all Cl
-
samples and NaClO
4
including slopes for linear parts of
the curves and molar concentrations (c), water activities (a
w
) and ionic strengths (I) for all samples.
(B) Slopes (S) of the steeper curve parts plotted as bar charts.
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FIG. 3-5: Survivability of P. halocryophilus during freeze/thaw cycles. Cells were incubated for 7 days
at 25°C in growth medium containing either no additional salt (black circles) or 10 wt% NaCl (grey
triangles) before subjecting them to freeze/thaw cycles. CFUs obtained from biological triplicates.
3.4 Discussion
We have shown that survival of P. halocryophilus is significantly lower in eutectic ClO4-
samples than in Cl- containing samples at all investigated temperatures, although ionic
strength and water activities at 25°C are similar, e.g. for CaCl2 and NaClO4 samples (Tab. 3-
1 and Fig. 3-4A). Moreover, the water activity should not change markedly when lowering
the temperature since it has been shown to remain reasonably constant at subzero
temperatures for solutions containing Cl- (Fontan and Chirife, 1981) and ClO4- (Toner and
Catling, 2016). Furthermore, the oxidizing ability of ClO4- is negligible in solutions at these
low temperatures (Brown and Gu, 2006). Thus, other ion specific properties must be
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responsible for the differences in the inhibitory effects of the ClO4- and Cl- containing
samples.
Additionally, we demonstrated that the survival of P. halocryophilus cells in eutectic Cl-
and ClO4- samples increases systematically with decreasing temperatures. The Arrhenius
plot (Fig. 3-4) indicates that this correlation is more significant in Cl- containing samples. The
slope for the CaCl2 containing samples (0.225 °C-1) is more than 2.5-fold steeper than for
the NaClO4 containing samples (0.079 °C-1), which means that survivability in the CaCl2
samples is increased by lowering temperature to a significantly higher extant than in the
NaClO4 samples. The slopes for MgCl2 (0.152 °C-1) and NaCl (0.135 °C-1) containing samples
lie between those of NaClO4 and CaCl2. The slow decrease of the death rate constant in the
NaClO4 containing samples with decreasing temperature is caused by the normal
temperature dependence of all chemical reactions (including cell damaging reactions)
described by the Arrhenius equation. The steeper slopes for the Cl- samples indicate an
additional effect on the decrease of death rates with lowering the temperature.
We propose the main reason for this difference in the temperature dependence of the
cell survival in Cl- and ClO4- containing samples is caused by the increase of size and stability
of hydration spheres around the ions in the Cl- brines at lower temperatures. Previous
studies have shown that with decreasing temperatures the hydration number around
cations such as Ca2+ increases (Zavitsas, 2005) and that the first hydration sphere around
Na+ in NaCl solutions becomes more rigid (Gallo et al., 2011). Furthermore, X-ray and
neutron diffraction studies have shown that a decrease in temperature results in the first
hydration shell of Cl- ions becoming gradually more structured and a second hydration
sphere forming (Yamaguchi et al., 1995). Data from the method of integral equations has
revealed a strengthening of the hydrogen bonding between Cl- and water molecules in the
first hydration shell at lower temperatures (Oparin et al., 2002). These results demonstrate
that lowering the temperature in Cl- containing samples increases stability and size of the
hydration spheres around the dissolved ions, which is known to reduce the permeability of
ions through cell membranes (Degrève et al., 1996; Jahnen-Dechent and Ketteler, 2012).
Hence, we conclude that a reduced ion permeability caused by larger and more stable
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hydration spheres minimizes the toxicity of the extracellular high ion concentration.
Therefore the cell survivability in low temperature Cl- brines is increased over the extent of
the normal Arrhenius-like temperature dependence.
In contrast to cations and Cl- ions, ClO4- ions do not tend to form stable hydration shells
(Neilson et al., 1985; Lindqvist-Reis et al., 1998). The reason for the small size and low
stability of hydration shells around ClO4- is its large ionic radius and its low electrical charge
with an even distribution over the entire anion (Brown and Gu, 2006) resulting in weak
hydrogen bonds and one of the lowest hydration energies of common inorganic anions
(Moyer and Bonnesen, 1979). The low tendency of ClO4- ions to form stable hydration
spheres at any temperature presumably correlates with a constant cell membrane
permeability and is a reasonable explanation for the observed low survival rate increase in
ClO4- containing samples with lower temperatures.
Finally, the higher membrane permeability at all investigated temperatures explains
the general low survivability of cells in ClO4- verses Cl- containing samples. However, several
other structural factors may play a significant role as well, for example, the formation of
chloro complexes in CaCl2 containing samples (Phutela and Pitzer, 1983; Wang et al., 2016),
ion pair formations (Fleissner et al., 1993; Smirnov et al., 1998), molecular mimicry
(Cianchetta et al., 2010), or the reported formation of a crust around P. halocryophilus cells
at low temperatures, which consist of peptidoglycan, choline and calcium carbonate
(Mykytczuk et al., 2016), that might provide protection against Cl- but not ClO4-.
The freeze/thaw experiments have shown that the survivability of cells during freezing
and thawing processes increases when NaCl is present. Studies have argued that the
formation of large water crystals during freezing might be destructive to cell membranes
and might even grow larger during thawing due to migratory recrystallization (Mazur,
1960). Greater amounts of large water crystals should only form in the salt-free samples,
because in the salt-rich samples pure water crystals are formed during freezing only until
the solution under the ice layer reaches the eutectic composition. After that point, eutectic
freezing results in very small water ice and salt hydrate particles, which potentially could be
physically less harmful to the cells. Another lethal effect during the freezing process might
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43
be the osmotic shock resulting from the increasing solute concentration in the remaining
liquid solution (Harrison, 1956). It is reasonable to assume that the decreased water activity
as a result of the enhanced solute concentration in the growth media during the freezing
process, is less harmful to bacteria that were already preconditioned with 10 wt% NaCl
during incubation. Furthermore, studies have shown that a heat or cold shock treatment of
Deinococcus radiodurans cells increases their survivability against freeze/thaw cycles (Airo
et al., 2004), hence an exposure to higher salt concentrations may result in a similar stress
response in P. halocryophilus and a higher tolerance against freeze/thaw cycling. The
beneficial effect of NaCl during the freeze/thaw process has been described in previous
studies (e.g. Calcott and Rose, 1982). In contrast, other studies have shown the opposite
trend, that the presence of NaCl decreases the percent of surviving bacteria during
freeze/thaw cycles (Postgate and Hunter, 1961; Nelson and Parkinson, 1979). However,
these bacteria are not known to be halotolerant and therefor might suffer more under the
increased osmotic stress than P. halocryophilus does. In the future, freeze/thaw
experiments with halophilic microorganisms like P. halocryophilus should also include other
types of salts in the growth medium, to test their influence on the cell survivability in
comparison to NaCl.
On Mars, NaCl has been detected globally, and especially at high levels by remote
sensing in the Southern Highlands (Osterloo et al., 2008). Perchlorates have been detected
at the Phoenix lander and the Curiosity Rover sites and is also likely global in extent (Clark
and Kounaves, 2016). These salts have also been suggested to be part of the brines
associated with the Recurrent Slope Lineae (RSL) (Ojha et al., 2015). However, more recent
studies have argued that only small amounts of water might be present within RSL (Edwards
and Piqueux, 2016) and that the darkening of the RSL might only be a result of a rewetting
process of former flows of salty water (Heinz et al., 2016). Furthermore, it has also been
suggested that RSL may be the result of granular flows where water plays no or only a
subordinated role (Dundas et al., 2017).
However, in general, the ubiquitous presence of hygroscopic salts and of water in the
form of ice on the poles or in the subsurface or as gas in the atmosphere makes the
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existence of cold, highly concentrated brines conceivable. Such brines could develop
through deliquescence or at salt-ice contacts (Fischer et al., 2014), being temporally stable
at the surface of Mars and perhaps permanently stable in the subsurface as briny
groundwater (Burt and Knauth, 2003; Martínez and Renno, 2013). Our data reveal that
microorganism resident in such brines could survive significantly longer at subzero
temperatures than previously thought and they might even thrive in slightly diluted brines
as has been shown for P. halocryophilus in 19 wt% NaCl solution (Mykytczuk et al., 2012).
As temperatures on Mars are change throughout the day and the seasons it is conceivable
that temperatures drop temporally below the eutectic temperature of the brine. Our
freeze/thaw experiments demonstrate that the freezing and thawing of cells in eutectic
brines would be less lethal than freezing and thawing in salt-free water.
3.5 Conclusion
We have shown enhanced microbial survival in subzero eutectic Cl- brines compared
to their warmer analogues. Based on the results, the best hypothesis is that the increase in
size and stability of hydration shells around ions at lower temperatures reduces osmotic
and chaotropic stress factors for microbial organisms. Although P. halocryophilus grew even
in the presence of 10 wt% NaClO4, higher ClO4- concentrations lower survival rates
significantly even at subzero temperatures. It appears that the decreased capability of ClO4-
ions to form stable hydration spheres causes the high toxicity of eutectic ClO4- solutions and
the lower temperature dependence of cell survival compared to Cl- brines. Furthermore,
we have shown that the presence of salts like NaCl increases the survivability during
freeze/thaw processes. This has broad implications for the habitability of some extreme
environments on Earth and the potential habitability of Mars.
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3.6 Acknowledgments
We thank Lyle Whyte for helping to improve the manuscript. This project was funded
by European Research Council Advanced Grant “Habitability of Martian Environments”
(HOME, # 339231). All of the numerical data for this paper are provided in the figures and
are also available in tabular form from the authors upon request (j.heinz@tu-berlin.de).
Author Disclosure Statement
No competing financial interests exist.
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4. Publication III: Bacterial growth in chloride and perchlorate
brines: Halotolerances and salt stress responses of Planococcus
halocryophilus
Jacob Heinz
1
, Annemiek C. Waajen
1,2
, Alessandro Airo
1
, Armando Alibrandi
1
, Janosch
Schirmack
1
, Dirk Schulze-Makuch
1,3
1Center of Astronomy and Astrophysics, Astrobiology Research Group, Technical University
of Berlin, Hardenbergstr. 36, 10623 Berlin, Germany.
2UK Centre for Astrobiology, School of Physics and Astronomy, University of Edinburgh, UK.
3School of the Environment, Washington State University, Pullman, Washington, USA.
Corresponding author: Dirk Schulze-Makuch (+493031423736; schulze-makuch@tu-
berlin.de)
Running Title: Bacterial Growth in Brines.
Search Terms: Brines; Salt; Growth; Mars; Perchlorate; Halotolerance
Accepted manuscript of:
Heinz, J., Waajen, A.C., Airo, A., Alibrandi, A., Schirmack, J., and Schulze-Makuch, D.
(2019) Bacterial growth in chloride and perchlorate brines: Halotolerances and salt stress
responses of Planococcus halocryophilus.
Astrobiology, ahead of print,
https://doi.org/10.1089/
ast.2019.2069.
Published by Mary Ann Liebert under a CC BY-NC 4.0 license (license terms cf.
https://creativecommons.org/licenses/by-nc/4.0/)
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Abstract
Extraterrestrial environments encompass physicochemical conditions and habitats
that are unknown on Earth, such as perchlorate-rich brines that can be at least temporarily
stable on the Martian surface. In order to better understand the potential for life in these
cold briny environments, we determined the maximum salt concentrations suitable for
growth (MSCg) of six different chloride and perchlorate salts at 25°C and 4°C for the
extremophilic cold- and salt-adapted bacterial strain Planococcus halocryophilus. Growth
was measured through colony forming unit (CFU) counts, while cellular and colonial
phenotypic stress responses were observed through visible light, fluorescence, and electron
scanning microscopy. Our data show that (1) the tolerance to high salt concentrations can
be increased through a step-wise inoculation toward higher concentrations, (2) ion-specific
factors are more relevant for the growth limitation of P. halocryophilus in saline solutions
than single physicochemical parameters like ionic strength or water activity, (3) P.
halocryophilus shows the highest microbial sodium perchlorate tolerance described so far,
however, (4) MSCg values are higher for all chlorides compared to perchlorates, (5) the
MSCg for calcium chloride was increased by lowering the temperature from 25°C to 4°C,
while sodium and magnesium containing salts can be tolerated at 25°C to higher
concentrations than at 4°C, (6) depending on salt type and concentration, P. halocryophilus
cells show distinct phenotypic stress responses such as novel types of colony morphology
on agar plates and biofilm-like cell clustering, encrustation, and development of
intercellular nanofilaments. This study, taken in context with previous work on the survival
of extremophiles in Mars-like environments, suggests that high-concentrated perchlorate
brines on Mars might not be habitable to any present organism on Earth, but they might be
able to evolve thriving in such environments.
Keywords: Brines; Salt; Growth; Mars; Perchlorate; Halotolerance
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4.1 Introduction
Most subzero saline habitats on Earth are dominated by sodium chloride (NaCl) and
most research has been focused on this salt (for review e.g. Gunde-Cimerman et al., 2018).
However, non-NaCl saline environments exist on Earth as well, such as the calcium chloride-
rich Don Juan Pond, Antarctica (Dickson et al., 2013) or the Spotted Lake, Canada having
high sulfate concentrations (Pontefract et al., 2017).
Similarly, soils on Mars contain non-NaCl salts such as perchlorates (Hecht et al., 2009).
Accordingly, the presence of perchlorate-rich Martian groundwater has been discussed
(Clifford et al., 2010). Fitting well to this hypothesis, it was recently proposed that the
discovered subsurface lake might contain magnesium and calcium perchlorates causing a
freezing point depression of water down to its calculated temperature of -68°C (Orosei et
al., 2018). Furthermore, spectral investigations indicated that perchlorate salt hydrates and
their brines might play a role in the formation of Recurring Slope Lineae (RSL) on Mars (Ojha
et al., 2015).
At the Phoenix landing site, perchlorate concentrations in the Martian soil are ranging
from 0.4 to 0.6 wt% (Hecht et al., 2009). However, it has to be kept in mind that the
perchlorates are present as solid salts which will form highly concentrated brines whenever
the temperature is above the eutectic temperature and the relative humidity is above the
deliquescence relative humidity (RH) of the perchlorate salt (Davila et al., 2010; Nikolakakos
and Whiteway, 2015; Heinz et al., 2016). For example, at -34°C the sodium perchlorate
concentration of the forming eutectic brine would be 52.6 wt% (9 M) (Hennings et al., 2013),
which is too high for any organism we know from Earth to thrive therein. Therefore, only
diluted perchlorate brines might serve as a habitat. These diluted solutions could be stable
in the subsurface of Mars (Burt, 2003; Martínez and Renno, 2013).
Since there are diurnal and seasonal temperature and humidity changes on Mars, it
can be assumed that salt concentrations in these brines also fluctuate due to crystallization
of ice or salt hydrates at cold temperature conditions or due to water absorption from the
atmosphere at high RH conditions, e.g. in the morning hours when the RH in the Martian
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atmosphere is highest and can reach saturation (Harri et al., 2014). Thus, microorganisms
would have to survive temporarily enhanced salt concentrations (including crystallization
processes) at low temperatures and thrive at times of higher temperatures and brine
dilution. It has already been shown that low temperatures enhance the bacterial survival in
chloride (Cl-) and perchlorate (ClO4-) brines with eutectic concentrations while, additionally,
the high salt concentrations benefit the survival during freeze/thaw cycles of the brine
(Heinz et al., 2018). However, the question how low the salt concentration would have to
be for microbial growth remained open prior to this study.
The exploration of the physicochemical limits for growth and survival of organisms
thriving in cold saline environments, gives not only insight into the microbial ecosystems
adapted to the most extreme habitats on Earth but also provides the necessary data for
assessing the habitability of extraterrestrial environments, e.g. on Mars (Schulze-Makuch et
al., 2015; Schulze-Makuch et al., 2017). A model organism for halo- and psychrotolerant
bacteria is Planococcus halocryophilus, which has been isolated from the active layer of
permafrost soil in the Canadian High Arctic (Mykytczuk et al., 2012). It is able to grow at 19
wt/vol% NaCl (corresponding to 16 wt%) concentration and at -15°C, while showing
metabolic activity down to -25°C (Mykytczuk et al., 2013; Raymond-Bouchard et al., 2017).
Bacterial growth of P. halocryophilus under these harsh conditions is enabled by the
expression of various osmolyte transporters and cold-adapted proteins, a high lipid
turnover rate, and a high resource efficiency at subzero temperatures with an accumulation
of carbohydrates as energy resource (Mykytczuk et al., 2013). Furthermore, analyses of the
proteome of P. halocryophilus revealed intricate changes in protein expression (Raymond-
Bouchard et al., 2017). Under subzero growth conditions, this bacterial strain develops a
nodular sheet-like crust around the cells which might provide protection against cold and
osmotic stress (Ronholm et al., 2015; Mykytczuk et al., 2016).
The ability to tolerate these cold and salty conditions was the reason for choosing P.
halocryophilus as a suitable analog microorganism to test how well microbes on Earth can
adapt to the conditions prevailing on Mars and whether adaption to high-concentration
perchlorate brines is possible with the available biochemical toolset of life as we know it.
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P. halocryophilus is an aerobic organism and thus, at first glance, might not appear relevant
to Martian habitability, given that the molecular oxygen (O2) content in the Martian
atmosphere is with 0.13 % very low. However, recent studies found that Martian brines can
be enriched with dissolved O2 up to 2 mol m-3, enabling aerobic microbes to metabolize
(Stamenković et al., 2018). In addition, there might be other suitable extraterrestrial
habitats that provide both osmotic stress conditions and feasible O2 levels.
Here, we investigated the maximum halotolerance for growth of P. halocryophilus at
optimal growth temperature (25°C) and low temperature (4°C) for various Cl- and ClO4- salts.
Furthermore, we investigated the phenotypic adaptations to salt stress such as changes in
cell and colony morphology and the formation of cell clusters. This study examines several
major aspects important for astrobiological research especially on Mars where Cl- and ClO4-
brines might be the last possible refuges for life (Davila and Schulze-Makuch, 2016).
4.2 Materials and Methods
4.2.1 Organism and culture conditions
The bacterial strain Planococcus halocryophilus Or1 (DSM 24743T), obtained from the DSMZ
(Leibniz Institute DSMZ - German Collection of Microorganisms and Cell Cultures) was used
in all experiments described within this study. The bacteria were grown aerobically at 25°C
(optimum growth temperature) or 4°C (low temperature control) in liquid DMSZ growth
medium #92 (3% Tryptic soy broth (TSB), 0.3% Yeast extract) with various concentrations (1
wt% (w/w) incremental steps) of one of the following salts: sodium chloride (NaCl),
magnesium chloride (MgCl2), calcium chloride (CaCl2), sodium perchlorate (NaClO4),
magnesium perchlorate (Mg(ClO4)2), or calcium perchlorate (Ca(ClO4)2). The media were
prepared by mixing the media components, salt and water, followed by pH adjustment (pH
7.2 – 7.4), centrifugation if necessary (in calcium-containing samples yeast flocculation can
occur (Stratford, 1989) which has no influence on the cells growth, because P.
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halocryophilus readily thrives in medium containing only TSB (Mykytczuk et al., 2012)), and
sterile filtration.
4.2.2 Determination of the maximum salt concentration suitable for growth (MSCg)
Bacteria were monitored for growth and death using colony forming unit (CFU) counts to
determine the MSCg values of the respective salts. Two identical samples were prepared
and inoculated separately (biological duplicates) for each experiment. For CFU counts two
aliquots of 100 µl were taken from each sample and were plated on agar plates containing
DMSZ growth medium #92. CFUs for the same experimental conditions were averaged using
the arithmetic mean. Where necessary, the aliquots were diluted with phosphate buffer
saline (PBS) containing additional 10 wt% NaCl (for all sodium containing samples) or 10
wt% MgCl2 (for all magnesium or calcium containing samples). The increased amount of salt
in the PBS was necessary to avoid bursting of cells by osmotic pressure during the dilution
of the saline growth media. Some experiments were repeated to check reproducibility.
To investigate the effect of the inoculation culture on growth and survival of P.
halocryophilus in the salty samples 5 ml of the saline medium (biological duplicates) were
inoculated with one of the following inoculation methods (IM):
IM 1: The medium was inoculated with the stock culture (growth medium + 10 wt%
NaCl) at 25°C.
IM 2: The medium was inoculated with a culture grown at the respective
temperature (25°C or 4°C) in medium with lower concentration of the respective
salt (progressive culture adaption).
IM 3: Medium for experiments at 25°C was inoculated with a culture grown at 4°C
in medium with the same or higher concentration of the respective salt.
IM 4: Medium for experiments at 4°C was inoculated with a culture grown at 25°C
in medium with the same or higher concentration of the respective salt.
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Inoculation volumes ranged from 10 µl to 50 µl depending on the cell density of the
inoculation culture. However, due to cell clustering (section 3.2.2) the starting cell density
after inoculation varied between 5·102 CFU/mL and 5·104 CFU/mL.
Because progressive culture adaptions were done by a 1 wt% stepwise increase in the
salt concentrations of the medium, the MSCg values had an inherent uncertainty of 1 %.
Larger uncertainties (up to 2 %) occurred for some samples incubated at 4°C when cells in
media with salt concentrations above the MSCg neither grew nor died within the time of
the experiment.
4.2.3 Light, fluorescence and scanning electron microscopy
A set of samples was investigated under the light microscope (Primo Star, Zeiss,
equipped with Axio Cam 105 color) without prior sample treatment. For fluorescence
microscopy of living and dead cells samples were washed twice with PBS containing 10 wt%
NaCl. Three ml of each sample were stained with 3 µl of a 1:2 mixture of component A (SYTO
9 dye, 3.34 mM) and component B (Propidium iodide, 20 mM), where component A causes
green fluorescence of intact cells and component B causes red or orange fluorescence of
dead cells with damaged cell walls. The stained samples were imaged with a fluorescence
microscope (Polyvar 2, Reichert-Jung) equipped with a Xenon lamp (XBO 150 W/1).
Samples for scanning electron microscopy (SEM) were washed twice with PBS
containing 10 wt% NaCl followed by fixation in 2.5 % glutaraldehyde solution (in 0.1 M
phosphate buffer (PB), pH = 7.3). The fixed samples were washed twice with 0.1 M PB,
dehydrated through a graded acetone series (50, 70, 90, 95, 100%), critical point dried in a
Leica CPD300, coated with carbon, and imaged with a Hitachi S-2700 microscope.
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4.3 Results
4.3.1 Growth at 25°C and 4°C
4.3.1.1 GROWTH CURVES AND MSCG VALUES: For determining the MSCg values of all Cl- and
ClO4- salts we used growth versus death as a distinction criterion. For example, after 6 days
of incubation in CaCl2-rich media P. halocryophilus shows an increase in CFU values (i.e.
growth) at 25°C under all tested salt concentrations with the exception of 9 wt%; hence at
this temperature the MSCg value is 8 wt% (Fig. 4-1). However, at 4°C the MSCg value is
greater with 10 wt% (embedded plot of Fig. 4-1).
FIG. 4-1: Growth curves of P. halocryophilus in liquid growth media with different CaCl
2
concentrations at 25°C (red curves) and 4°C (blue curves). X indicates the detection limit (no
detectable CFUs in a 100µl aliquot). IM describes the inoculation method as explained in section 2.2.
MSCg values are 8 wt% and 10 wt% CaCl
2
for 25°C and 4°C, respectively. Growth in 10 wt% CaCl
2
at
4°C (embedded plot) was only observed for one of the two biological duplicates, thus, lacking an
error bar.
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All growth curves generated are provided in the supplementary materials (Fig. 7-4
7-15) and the resulting MSCg values for all salts and temperatures, including their
corresponding total ion concentrations (sum of cation and anion concentration), anion
concentrations, ionic strengths and water activities are listed in Table 4-1. The MSCg (wt%),
total molar ion concentrations and anion concentrations are plotted as bar charts in Fig.
4-2.
TAB. 4-1: MSCg values and corresponding total ion concentrations (sum of cations and anions),
anion concentrations, ionic strengths and water activities at 25°C and 4°. Values in brackets give the
deviation as described in section 2.2.
MSCg total ion
conc.
anion
conc.
ionic
strength
water
activity*
[wt.%] [mol/l] [mol/l] [mol/l] [mol/l]
25°C 4°C 25°C
4°C 25°C
4°C 25°C
4°C 25°C
4°C 25°C 4°C
NaCl
14(1)
11(1)
2.79
2.11
5.57
4.23
2.79
2.11
2.79
2.11
0.90
0.93
MgCl
2
11(1)
10(2)
1.30
1.17
3.89
3.50
2.60
2.33
3.89
3.50
0.92
0.93
CaCl
2
8(1)
10(1)
0.78
1.00
2.35
3.00
1.57
2.00
2.35
3.00
0.96
0.95
NaClO
4
12(1)
7(2)
1.11
0.61
2.23
1.23
1.11
0.61
1.11
0.61
0.96
0.98
Mg(ClO
4
)
2
5(1)
4(1)
0.24
0.19
0.71
0.56
0.47
0.37
0.71
0.56
0.99
0.99
Ca(ClO
4
)
2
3(1)
3(1)
0.13
0.13
0.39
0.39
0.26
0.26
0.39
0.39
0.99
0.99
* Water activity calculated for 25°C from the Pitzer equation (Pitzer, 1991) with Pitzer parameters
taken from (Toner et al., 2015). The temperature dependence (25°C vs. 4°C) of the water activity is
negligible for Cl
-
(Fontan and Chirife, 1981) and ClO
4-
solutions (Toner and Catling, 2016) at
temperatures at above 0°C.
Overall, P. halocryophilus shows exceptionally high halotolerances to all Cl- and ClO4-
salts at both 25°C and 4°C (Fig. 4-2A, B). The Cl- tolerance is at least 2.5-fold higher than the
tolerance to ClO4- in media with the same cation (Fig. 4-2C). However, with 12 wt% (1.1 M)
NaClO4 at 25°C we found the highest microbial tolerance to NaClO4 described so far. The
lowest tolerated water activity was 0.90 in 14 wt% (2.8 M) NaCl, while the highest tolerable
ionic strength (3.9 mol/l) was reached in 11 wt% (1.3 M) MgCl2 at 25°C (Tab. 4-1).
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FIG. 4-2: Maximum salt concentrations suitable for growth (MSCg) of P. halocryophilus expressed as
wt% (A) and total molar concentration (sum of cation and anion concentration) (B), and the molar
anion concentrations at the corresponding MSCg (C). Transparent parts of the bars represent the
salinity range for which neither growth nor complete demise of the culture could be determined
after 150 experimental days (see chapter 4.2.2). The water activities and ionic strengths at the MSCg
are shown in Fig. 7-16.
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4.3.1.2 EFFECT OF THE INOCULATION METHOD (IM) ON THE MSCG: The applied IM effects the
growth curves and the resulting MSCg values in the following ways:
(1) At 25°C, the MSCg values could only be reached with IM 2 (progressive culture
adaptation at 25°C) but not with IM 1 (inoculation with stock culture) where cell death
occurs already at lower salt concentrations. For example, the MSCg for MgCl2 was 9 wt% at
25°C when the media was inoculated with the stock culture (IM 1), however, a stepwise (1
wt%) increase in the MgCl2 concentration (IM 2) resulted in a MSCg of 11 wt% MgCl2 (Fig.
7-6). It is notable that the length of the growth curve lag phase (occasionally including an
initial CFU reduction) is enhanced with increasing salt concentration and decreasing
temperatures (e.g. Fig. 4-1, 7-4).
(2) Appling IM 3 (4°C25°C inoculation) resulted in an increase of the MSCg values at
25°C only in the case of Ca(ClO4)2 samples. Here, growth in 3 wt% Ca(ClO4)2 was not
detected after inoculation with the stock solution (IM 1) nor with a 2 wt% Ca(ClO4)2 culture
grown at 25°C (IM 2), but only after inoculation with a 3 wt% Ca(ClO4)2 culture grown at 4°C
(IM3) (Fig. 7-14).
(3) At 4°C, a higher MSCg value was reached by applying IM 2 (progressive culture
adaptation at 4°C) than by applying IM 4 (25°C4°C inoculation). For example, at 4°C
inoculation of 2 wt% Mg(ClO4)2 medium with a 5 wt% Mg(ClO4)2 culture grown at 25°C did
not show growth, indicating a MSCg < 2 wt% Mg(ClO4)2 when IM 4 is applied. However, a
1 wt% stepwise increase in Mg(ClO4)2 concentration at 4°C (IM 2) resulted in an culture able
to growth at 4 wt% Mg(ClO4)2 (Fig. 7-13). This data suggests that for growth at 4°C an
adaption to the cold first has to take place before P. halocryophilus can adapt stepwise to
higher salt concentrations at that temperature.
4.3.1.3 TEMPERATURE EFFECT ON THE MSCG: The relative shift in the MSCg that occurs by
lowering the incubation temperature from 25°C to 4°C is visualized in Figure 4-3. Among all
six salts investigated in this study, only cells in CaCl2 containing media show an enhanced
salt tolerance at lower temperature, where growth at 9 wt% and 10 wt% CaCl2 did not occur
at 25°C but only at 4°C (Fig. 4-1).
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FIG. 4-3: Relative changes in the MSCg induced by lowering the incubation temperature from 25°C
to 4°C.
Nevertheless, the observation that only IM 4 (4°C25°C inoculation) resulted in
growth at the MSCg for Ca(ClO4)2 (3 wt%) at 25°C (see point (2) of section 4.3.1.2) provides
evidence that also the tolerance to Ca(ClO4)2 is increased at 4°C, however, to a lower extent
than the 1 wt% salt concentration incremental steps used in this study (section 2.1). This
suggests a general increase in the calcium (Ca2+) tolerance of P. halocryophilus at lower
temperatures.
In contrast, the sodium (Na+) tolerance is decreased at lower temperatures for both
anions, Cl- and ClO4- (Fig. 4-3). The tolerances to magnesium (Mg2+) are only slightly reduced
at 4°C (1 wt% also for both anions, Cl- and ClO4-). The reduction in the Na+ tolerance at 4°C
on the one hand and the increased Ca2+ tolerance at 4°C on the other hand led to an
equalization of the anion (Cl- or ClO4-) concentration at the MSCg at C, while at 25°C the
differences between the anion concentrations for the three different cations (Na+, Mg2+ and
Ca2+) salts are more pronounced (Fig. 4-2).
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4.3.2 Cellular and colonial phenotypic salt-stress adaptations
4.3.2.1 COLONIAL PHENOTYPIC ADAPTATIONS: P. halocryophilus cells grown in liquid cultures
exhibit with an increase in salt concentration, particularly for perchlorate salts, the
tendency to develop macroscopic cohesive biofilms that could only be disrupted by intense
shaking or vortexing (Fig. 4-4A).
Furthermore, it was observed that a novel colony phenotype (type II) appears only on
plates inoculated with aliquots from cells grown in ClO4--rich medium (especially with > 9
wt% NaClO4 at 25°C). This type II colony is paler and duller then the usual colonies (type I)
that are shiny and orange (Fig. 4-4) and does not occur in cultures grown in salt-free or Cl-
containing media. Occasionally both colony types occurred on plates inoculated with
aliquots from cells grown in media with perchlorate concentrations of a few wt% below the
MSCg (Fig. 4-4B). Sporadically such colonies underwent a transformation from the type II
back to the type I after approx. 2 weeks of growth on the agar plates (Fig. 4-4C).
Contamination was ruled out through 16S sequencing of both colony types (99.90%
sequence similarity of type I vs type II, data not shown), suggesting that the colony type II
represents a reversible multi-generational phenotypic adaptation of P. halocryophilus to
high perchlorate salt stress. Type II colonies needed 3 to 5 times longer than type I colonies
to reach comparable colony sizes.
Two additional colony phenotypes were observed on agar plates: Type III colonies are
irregular jagged in shape and occurred on agar plates inoculated with magnesium-rich (Cl-
and ClO4-) cultures (Fig. 7-17). Type IV colonies are mucoidal and shiny, merge rapidly during
growth and occurred on agar plates inoculated with CaCl2-rich cultures (Fig. 7-18).
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FIG. 4-4: Macroscopically visible salt stress responses: (A) Biofilm-like cell clumping occurring in a
10 wt% NaClO
4
culture after 1 month of growth. (B) Two different colony morphologies of P.
halocryophilus observed one week after plating a 9 wt% NaClO
4
culture at 25°C. The shiny intense-
orange colonies (type I) represent the colony morphology typical for P. halocryophilus grown in
medium with low salt concentrations. The paler and smaller colonies (type II) only occurred after
plating perchlorate-rich cultures. (C) Transformation of a type II colony into type I after two weeks
of colony growth.
4.3.2.2 CELLULAR PHENOTYPIC ADAPTATIONS: P. halocryophilus cells grown in liquid media
containing no additional salts, seen under the light and fluorescence microscope as well as
in SEM images, occur predominantly as single cells, diplococci, or small cell aggregates (Fig
5A-C) and have an overall smooth surface with nodules occurring largely along the cell
division plane (Fig. 5B) as previously described (Mykytczuk et al., 2016).
Cells however, grown in Cl--rich media occur predominantly in larger clusters of ~100
cells (Fig. 4-5 D-F); and moreover, cells grown in perchlorate-rich media cluster into even
larger aggregates of >1,000 cells (Fig. 4-5 G-I). These clusters, containing living and dead
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cells (Fig. 4-5G), are highly cohesive and could not be disrupted by 5 minutes of ultra-
sonication nor by washing with 100% ethanol and killing all cells (Fig. 7-19). The cell
clustering predominantly occurring in perchlorate-rich media led to higher uncertainties
and irregularities in the growth curves of these samples (e.g. Fig. 7-10, 7-14). Concurrent
with cell clustering under salt-stress conditions is the development of intercellular
nanofilaments within a cluster (Fig. 4-5E). Additionally, cells in CaCl2-rich media developed
surface encrustation (Fig. 4-5F).
FIG. 4-5: Light microscopy (A, D), fluorescence microscopy (after life/dead staining) (G) and SEM (B-
C, E-F, H-I) images of P. halocryophilus after growth in media containing no salts (A-C), chlorides (D-
F), and perchlorates (G-I) at 25°C. Cells grown in salt-free media developed smooth surfaces with
some nodular features (n) and occurred as single cells, dimers, or smaller cell aggregates (A-C).
Several salt stress responses were observed including formation of cell clusters (G-I) and filaments
(f) (E), and encrustation (en) of some cells in CaCl
2
containing cultures (F).
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4.4 Discussion
4.4.1 Salt-stress response and phenotypic adaptation
Microbial salt-stress responses and multi-generational adaptations such as microbial
cell aggregation and biofilm formation have been observed for various stress conditions
such as desiccation (Monier and Lindow, 2003), UV radiation (Fröls et al., 2008), or NaCl
exposure (Philips et al., 2017). Thus far, NaCl was the only salt for which the salt-stress
response of P. halocryophilus has been investigated, showing that the cells developed an
EPS-like coating with short filament-like features if grown in 15 wt% (18 wt/vol%) NaCl
media at -5°C (see Fig. 1e, f in Mykytczuk et al., 2016).
For our experimental growth conditions we show a similar trend for P. halocryophilus
at high NaCl concentrations, where the cells developed even longer nanofilaments (Fig.
4-5E). The formation of similar nanofilaments linking cells within one cluster has also been
observed previously, e.g. for the halophilic archaeon Halococcus salifodinae (see Fig. 2 in
Legat et al., 2013). Furthermore, we conducted experiments with two additional Cl- and
three ClO4- salts showing that P. halocryophilus develops particularly large and highly
cohesive clusters especially if grown in perchlorate-rich media (Fig. 4-5 G-I). Previous studies
on Hydrogenothermus marinus have shown a formation of cell chains under increased
perchlorate concentrations which has been speculated to result from inchoate cell division
(Beblo-Vranesevic et al., 2017); a physiological effect of perchlorate that could be similar
for P. halocryophilus. Such a mechanism would be in accordance with our observation that
cell clusters could neither be destroyed through ultrasonication nor through killing the cells
with ethanol treatment (Fig. 7-19).
Furthermore, our results show the development of cohesive biofilms in perchlorate-
rich media (Fig. 4-4A), and if transferred to agar plates, the occurrence of an additional
colony morphology (type II, Fig. 4-4B). These are both macroscopic phenotypes consistent
with the microscopic development of large cell clusters linked by numerous nanofilaments.
Such stress-induced changes in colony morphology are also known for other stressor than
high salinity; e.g. under nutrient starvation Vibrio cholerae colonies change from the normal
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translucent to a rugose type (Wai et al., 1998), or with a pH shift Bacillus subtilis colonies
change from the normal notched 'volcano-like' to round and front-elevated 'crater-like'
shapes (Tasaki et al., 2017).
The phenotypic responses described above demonstrate that organisms like P.
halocryophilus can develop perchlorate-specific stress adaptations that are not (or only to
a lower extent) used to counteract high chloride concentrations. This is an important finding
for all extraterrestrial environments with natural occurring perchlorates. This might not only
include Mars, but any planetary bodies with a relatively dry surface (to avoid leaching of
salts) and increased UV radiation (to oxidize chlorides (Carrier and Kounaves, 2015)). For
example, spectral data indicates the presence of perchlorates at the surface of the icy moon
Europa (Ligier et al., 2016), which could entail delivery of perchlorates to Europa´s
subsurface ocean (Hand et al. 2007). Also, based on the observed phenotypic adaptations
of P. halocryophilus, microfossils of such organisms found in perchlorate-rich environments
might rather be present in form of cell clusters or biofilms rather than in form of single cells.
4.4.2 Halotolerances of P. halocryophilus at 25°C and 4°C
To our knowledge, the only MSCg data for P. halocryophilus has been reported for NaCl
being 16 wt% (19 wt/vol%) at 25°C (Mykytczuk et al., 2012) and 15 wt% (18 wt/vol%) + 7
wt/vol% glycerol at -15°C (Mykytczuk et al., 2013; Mykytczuk et al., 2016). In contrast, we
found a lower NaCl-halotolerance of 14 wt% and 11 wt% at 25°C and 4°, respectively, which
can have various causes e.g.: (1) Mutation of the lab culture and loss of part of its
physiological abilities since isolation from its natural environment and first description
(Mykytczuk et al., 2012); (2) Different, and commonly not or only partially reported,
preconditioning and adaptation procedures for cell growth such as the increment size of
salt increase, growth curve phase used for transfer inoculation, and transfer or culture
volume and agitation; (3) Use of a different growth media: while we used DMSZ growth
media #92 containing Tryptic Soy Broth (TSB) and yeast extract, Mykytczuk (2013) and
Mykytczuk (2016) used a growth media containing TSB and glycerol to maintain the medium
liquid down to temperatures of -15°C. Glycerol is known to be an osmoprotectant and, thus,
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might have caused the elevated NaCl tolerance at low temperatures. Whether this
difference in halotolerance would have also applied to other salts remains unknown, since
no other salts than NaCl have been investigated for P. halocryophilus prior to this study.
The determination of MSCg values for multiple salts, as presented here for the first
time for P. halocryophilus, provides the opportunity to test if any single physicochemical
aspect of saline solutions is a limiting factor for growth. Our data however, does not indicate
that any individual factor (incl. total ion or anion concentration, ionic strength, water
activity, see Tab. 4-1, Fig. 4-2, and Fig. 7-16) to be responsible for the growth limitation of
P. halocryophilus in saline solutions. Otherwise, the values of one of these physicochemical
factors (e.g. water activity) would be similar for all salts, which is not the case.
However, our data indicates the following ion species-dependent halotolerances for P.
halocryophilus:
(1) The anion species, here Cl- vs. ClO4-, plays the most dominant role determining the
MSCg values independent of physicochemical unit, showing an overall at least 2.5-fold
higher tolerance to Cl- than to ClO4- salts with the same cation. Nevertheless, the MSCg of
NaClO4 (12 wt%; 1.1 M) is comparatively high and exceeds earlier findings for other
organisms such as Haloferax mediterranei (0.6 M) (Oren et al., 2014), Halomonas venusta
(1.0 M) (Al Soudi et al., 2017), Hydrogenothermus marinus (0.44 M) (Beblo-Vranesevic et
al., 2017) different bacterial isolates from Big Soda Lake in Nevada, USA (0.17 M)
(Matsubara et al., 2017), and Halorubrum lacusprofundi (0.8 M) (Laye and DasSarma, 2018).
It should be noted that it is not clear how P. halocryophilus developed such high perchlorate
tolerances. Perchlorates are rare in natural terrestrial environments and often coupled to
the occurrences of nitrates, e.g. in the Atacama Desert, Chile (Dasgupta et al., 2005). No
nitrates have been detected in the permafrost samples P. halocryophilus has been isolated
from (Steven et al., 2007), thus it appears likely that this strain has never been exposed to
environmental perchlorates and did not derive its resistance to perchlorate that way.
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(2) A similar role plays the cation species for growth at 25°C, where Na+ is the most
tolerated cation for each group of anions, i.e. NaCl among the chlorides and NaClO4 among
the perchlorates.
In summary, for growth at 25°C, Na+ and Cl- ions are individually the most tolerated
ions and NaCl is the salt to which P. halocryophilus has the highest halotolerance (2.8 M) at
the lowest water activity (0.90). Life on Earth has generally adapted to those factors most
efficiently that are the most common and/or abundant in nature; for salt this is NaCl. Hence,
our data suggests, that the limitation of growth for P. halocryophilus is to a large degree
based on evolutionary adaptations to brine veins (most likely consisting of NaCl) present in
permafrost soil (Steven et al., 2007). Also, all members of the genus Planococcus are
halotolerant and have been isolated predominantly from cold and/or saline environments
like the Arctic, Antarctic, or marine habitats (Mykytczuk et al., 2012).
Perchlorate ions in aqueous solutions are relatively inert and non-oxidizing due to
kinetic barriers (Urbansky, 1998), but rare in Earths nature and therefore presumably
exhibit an enhanced toxicity compared to chlorides. Thus, it seems plausible that putative
Martian microbes could adapt to natural occurring perchlorate-rich environments to the
same extent as Earth microbes such as Planococcus sp. did adapt to NaCl-enriched habitats.
This idea is consistent with our finding that the tolerance to high salt concentrations can be
increased through a step-wise inoculation toward higher concentrations. At low
temperatures (4°C in this study) longer lag phases would provide even more time for
adaption to higher salt concentrations to occur.
Additional to the ion species-dependent halotolerance, a temperature-dependent
halotolerance of P. halocryophilus was observed, where at 25°C the MSCg values are
different for each cation species, while at 4°C the cation species is less relevant and the
MSCg values are more similar (Fig. 2). This MSCg value alignment at low temperatures
appears to be largely caused by two separate trends:
(1) Na+ containing salts (i.e. NaCl and NaClO4) can be tolerated by P. halocryophilus to
higher concentrations at higher temperatures. Possibly, the elaborate biochemical
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machinery evolved to cope with high Na+ concentrations is kinetically more effective at
optimal growth temperatures enhancing the overall halotolerance.
(2) In the case of CaCl2 we observe the opposite effect, where lowering the
temperature increases the halotolerance to this salt. This observation is in accordance with
previous studies showing that with decreasing temperature the survival of P. halocryophilus
in eutectic CaCl2 brines is enhanced to a significantly larger degree than in NaCl, MgCl2 or
NaClO4 brines (Heinz et al., 2018). A low temperature induced halotolerance enhancement
has been described for example for the bacterial strain Clostridium sp. isolated from brine
lenses in the Siberian permafrost (Gilichinsky et al., 2003) and for M. soligelidi (Morozova
and Wagner, 2007) in NaCl-rich media. However, to our knowledge, P. halocryophilus is the
first organism described thus far that shows an increased CaCl2 tolerance at lower
temperatures and can grow at salt concentrations up to 10 wt% (1 M) CaCl2 at 4°C in the
absence of kosmotropic ions which otherwise could compensate the chaotropic stress
caused by calcium ions (Oren, 2013).
However, it remains unclear what mechanism causes the enhanced CaCl2 tolerance of
P. halocryophilus at 4°C, perhaps a psychrophilic optimization of the relevant biochemical
machinery for coping with Ca2+ or simply the lethal effect of calcium being decreased at
lower temperatures. It has been proposed that the increased CaCl2 tolerance at lower
temperatures might be due to the formation of larger and more stable hydration shells
around calcium ions with decreasing temperature (Heinz et al., 2018). A possible biological
explanation is a beneficial effect caused by cellular encrustation, which was only observed
in CaCl2-rich media in this study (Fig. 4-5F). Correspondingly, cellular encrustation
containing 20 % calcium carbonate has been documented previously for P. halocryophilus
cells grown at subzero temperatures in NaCl-rich media (Mykytczuk et al., 2016). Similar
encrustation might be triggered in the presence of high Ca2+ amounts and might provide an
efficient calcium resistance strategy due to the microbial mediated calcium carbonate
precipitation. This positive effect might be increased at lower temperatures.
Another factor that might play a role on the enhanced Ca2+ tolerance at lower
temperatures is the chaotropicity of Ca2+. Chaotropic compounds increase the flexibility of
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macromolecules like proteins and, thus, can limit life at high temperatures (Hallsworth et
al., 2007), but they can also benefit microbial growth at low temperatures (Chin et al., 2010;
Rummel et al., 2014). Cray et al. (2013) found that the chaotropic activity for CaCl2 (92.2 kJ
kg-1 mol-1) is significantly higher than for MgCl2 (54.0 kJ kg-1 mol-1) while NaCl is a
kosmotropic compound (-11.0 kJ kg-1 mol-1). These data suggest that the high chaotropicity
of CaCl2 (and potentially also of Ca(ClO4)2, but data for perchlorates are lacking) might
contribute to the enhanced microbial Ca2+ tolerance at low temperatures.
Additional work is needed to better understand the observed general trends in the
habitability of Mars-analogue brines in dependence on the type of salt, its concentration
and temperature. Additional long-term studies under subzero temperatures, similar to
Martian environments, should be conducted, especially since studies have shown that P.
halocryophilus is able to grow under these conditions (Mykytczuk et al., 2013; Mykytczuk et
al., 2016). It is possible that lowering the experimental temperature to subzero values will
further increase the tolerance of P. halocryophilus to Ca2+. We also recommend that other
microbial strains (including anaerobic ones) or communities should be investigated under
similar experimental conditions to widen our understanding of life in cold brines.
4.5 Conclusion
For the first time, this study provides insights into the extremophilic bacterium P.
halocryophilus, well-known for its tolerance to both cold temperatures and high
concentration of salts, on how it survives and adapts not only to NaCl solutions, but all Mars-
relevant Cl- and ClO4- salts solutions at different temperatures. Although growth in highly
concentrated eutectic brines is not possible (Heinz et al., 2018), the tolerance to the salts
investigated in this study is intriguing and can be even enhanced by a stepwise increase in
the salt concentration. For example, with 12 wt% (1.1 M) NaClO4 we found the highest
bacterial tolerance to ClO4- reported to date. For CaCl2 containing cell cultures we could
show that by lowering the temperature from 25°C to 4°C the halotolerance increases from
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8 wt% (0.8 M) to 10 wt% (1.0 M), respectively, while tolerances to Na+ and Mg2+ are
decreased for the same temperature decline.
The increased Ca2+ tolerance at lower temperatures corresponds well to the previously
described enhanced survival in low temperature brines (Heinz et al., 2018) and plays an
important role for the habitability of Martian environments where Ca2+-rich brines might
be present in the shallow subsurface (Burt, 2003). Furthermore, Ca2+ is thought to be the
main counter ion in ClO4- salts (Kounaves et al., 2014b) and Ca(ClO4)2 might be a main
component of the recently discovered subsurface lake near the Martian south pole and
could be responsible for its freezing point depression (Orosei et al., 2018).
Additionally, we described several salt adaption mechanisms like cell clustering, the
formation of nanofilaments, encrustation of cells and changes in the cell colony
morphology. This data provides insight into how life could adapt to such high salt
concentrations necessary for a sufficient freezing point depression allowing liquid water to
be stable close to the Martian surface.
Acknowledgments
This project was funded by European Research Council Advanced Grant Habitability
of Martian Environments” (HOME, no. 339231). All of the numerical data for this paper are
provided in the figures, tables and supplementary information and are also available in
tabular form from the authors upon request (sc[email protected]). We would like
express our thanks to two anonymous reviewers whose comments and suggestions have
helped to improve this manuscript.
Author Disclosure Statement
No competing financial interests exist.
Conclusions and Outlook
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5. Conclusions and Outlook
To better understand the potential of Martian environments in being inhabited by
microorganisms one has to focus on both the environmental conditions of the putative
Martian habitats, especial in regards of the occurrence of liquid water, as well as the limits
of life in these environments. That is why this study investigated the formation of brines via
deliquescence and their potential in being involved in the formation of RSL on the hand,
and, on the other hand, the effect of these brines on growth and survival of microorganisms,
exemplarily represented by P. halocryophilus in this study.
Publication I was focused on investigating the formation process of RSL through
deliquescence of Cl- and ClO4- salts interspersed in Mars-analogue soil. The main idea of this
study was to demonstrate the benefits of using EC measurements to follow the
deliquescence process and quantify the deliquescence rate compared to prior used
techniques like Raman spectroscopy (Gough et al., 2011; Gough et al., 2014; Nuding et al.,
2014; Nikolakakos and Whiteway, 2015; Nuding et al., 2015; Gough et al., 2016). While in
these Raman-spectroscopical experiments a laser beam was directly focused on small salt
particles to investigate deliquescence-induced phase changes caused by variations in
temperature and RH, the conductivity method presented here provides an experimental
approach closer related to realistic environmental conditions (large-scaled experiments
including Mars-analog soil). A first set of field experiments in the Atacama Desert, Chile
(chapter 7.2), has already shown that the conductivity method is an excellent technique to
investigate deliquescence-induced RSL formation.
In the future, similar EC measurements could also be conducted on Mars, e.g. with
sensors like the Thermal and Electrical Conductivity Probe (TECP) designed for the Phoenix
lander (Zent et al., 2009). Furthermore, additional lab experiments should be carried out to
examine which influence parameters like pressure, temperature, RH, type of soil and salts,
particle sizes, salt concentration, hydration states, atmospheric composition, and air
circulation have on the deliquescence rate. To increase the similarity to RSL these
experiments could also be conducted at artificial slopes similar to the hills where RSL can
Conclusions and Outlook
69
be observed on Mars (McEwen et al., 2011a). First follow-up experiments in our lab
investigating the effect of the salt concentration in the soil on the deliquescence process
revealed that already 1 wt% CaCl2 is enough to result in a measurable soil wetting caused
by deliquescence (unpublished data, chapter 7.1).
After addressing the formation of brines in Publication I the next logical step from an
astrobiological viewpoint was to investigate the habitability of these brines in the
Publications II and III. The combined findings of those two publications revealed that
halotolerant microorganisms like P. halocryophilus cannot survive the salt stress in eutectic
brines but their survivability can be increased significantly by lowering the temperature to
subzero values. To enable bacterial growth a dilution of the eutectic brines is needed, where
the extent of the dilution depends on the type of salt and the temperature. Although ClO4-
salts can only be tolerated at lower concentrations than Cl- salts there seems to be no
reason why putative microbes on Mars should have been unable to adapt to higher ClO4-
concentrations.
It is likely that in a realistic Martian environment with diurnal and seasonal changes of
environmental conditions microorganisms would be exposed temporally to both scenarios:
life-inhibiting (low temperatures, concentrated brines) and life-promoting (elevated
temperatures, diluted brines) conditions. The results of Publication II indicated that at cold
temperatures close to the eutectic point of the brine, e.g. -77.5°C for Ca(ClO4)2,
microorganisms might not be able to thrive but to survive until temperatures rise (up to
+30°C at the Martian surface). At these higher temperatures also life-promoting low-
concentrated brines, e.g. 12 wt% NaClO4 for growth of P. halocryophilus (see Publication
III), could be stable. These diluted salt solutions might form through proceeding water
absorption of the hygroscopic concentrated brine or when the brine gets in direct contact
with water ice. The low atmospheric pressure on Mars seems not to be a limiting factor for
the stability of the diluted brines since the water vapor pressure at the triple point of pure
water (6.1 mbar)
is below the atmospheric pressure on the lowest regions of Mars (Martínez
and Renno, 2013). The water vapor pressure of brines is always below the one of pure
water. Halotolerant microorganisms like P. halocryophilus could grow in these diluted
Conclusions and Outlook
70
brines readily when applying salt stress defense mechanisms like the accumulation of
osmolytes, e.g. betaine or proline (chapter 7.3), or cell clustering (Publication III).
Additional to the enhanced survivability at subzero temperatures found in the
experiments presented in Publication II, results from the experiments of Publication III
showed an increase in the maximum CaCl2 concentration suitable for growth of P.
halocryophilus with decreasing temperature while tolerances to other salts are similar or
lower at 4°C compared to 25°C. This complex behavior demonstrates that more research is
needed to better understand general aspects of the habitability of brines, especially at cold
temperatures and including non-NaCl salts. These experiments might also include other
halotolerant or halophilic species or microbial communities and additional Mars-relevant
salts like iron sulfates or salt mixtures like “Instant Mars” consisting of Na+, K+, Mg2+, Ca2+,
Cl-, ClO4-, and SO42- ions (Nuding et al., 2015). Since results of Publication III have shown
that cells grown in ClO4- solutions form different cell colony morphologies on agar plates
than cells grown in Cl- solutions the investigation of differences in the transcriptome and
proteome from both cell types would be of special interest for astrobiological research.
Experiments for this purpose are already ongoing in our labs and will hopefully soon provide
new and intriguing knowledge about life in brines.
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Supplementary Information
90
7. Supplementary Information
7.1 Effect of the salt/soil ratio on the deliquescence process
7.1.1 Materials and methods
The experimental setup for measuring deliquescence-induced soil wetting is described
in Publication I, chapter 2. To investigate the effect of the salt/soil ratio on the
deliquescence process the same experimental approach was used but with different
concentrations of CaCl2 in the soil (JSC-Mars-1a). To check reproducibility of the
measurements three samples with 5 wt% CaCl2 were prepared and measured separately.
7.1.2 Results and discussion
The measured normalized conductivity values (N) as function of time and salt
concentration are given in Figure 7-1. The results show nicely that higher CaCl2
concentrations yield higher deliquescence rates.
FIG. 7-1: Increasing EC caused by deliquescence-induced water absorption of the soil (A). Magnified
segment of Fig. A showing curves for samples with concentrations of ≤ 5 wt% CaCl
2
(B).
Supplementary Information
91
Deliquescence was detectable via EC measurements down to a salt content of 1 wt%
CaCl2 which is comparable to overall salt concentrations in the Martian regolith (Toner et
al., 2014a). The overlapping of the curves for the 5 wt% CaCl2 triplicates demonstrates the
good reproducibility of this technique. Weighing of the samples could be used to correlate
the measured EC values with the amount of absorbed water.
7.2 RSL-simulating field experiments in the Atacama Desert, Chile
7.2.1 Materials and methods
During the field trip in 2018 experiments were conducted that were dedicated to
simulate Martian RSL on steep-sloped hills in the Yungay Valley of the Atacama Desert,
Chile. For this purpose 10 kg NaCl (technical grade) were dissolved in water to gain a nearly
saturated solution. This briny solution was gently poured down a hill. Photos were taken
and HOBO and CR10 data logger (more details on the data loggers are available in
Publication I, chapter 2) were used to determine the atmospheric RH and temperature as
well as the EC of the wetted soil, respectively.
7.2.2 Results and discussion
The NaCl solution poured down the hill resulted in a darkened wet brine track similar
to RSL on Mars (Fig. 7-2A). During daytime the high temperatures and low RH resulted in a
continuous evaporation of the water correlating with a decrease in the relative EC while the
increased RH in the night and morning caused a deliquescence-induced water absorption
coinciding with an increase in the EC (Fig. 7-3). Since the amount of water evaporating
during daytime is exceeding the water amount absorbed during the night and morning
hours the net water balance is negative. Thus, no growth of the simulated RSL could be
observed but only a slow fading within 4 days (Fig. 7-2B). In future field experiments the
NaCl could be replaced by more hygroscopic ClO4- salts with a lower DRH. This might result
in a positive net water balance and, therefore, in a down-slope growth of the simulated RSL.
Supplementary Information
92
FIG. 7-2: Simulated RSL directly after pouring a saturated NaCl solution down the hill (A). Nearly
completely faded RSL after 3 days (B).
FIG. 7-3: Temperature, RH and relative EC data collected during the RSL-simulating field experiment
in the Atacama Desert. When the RH increased during night and morning hours the NaCl in the RSL-
like track absorbed water from the atmosphere correlating with an increase in the EC. The data gap
in the EC measurements during the first day of the experiment resulted from connection problems
with the data logger.
Supplementary Information
93
7.3 Metabolomics studies on P. halocryophilus
7.3.1 Materials and Methods
Cells of P. halocryophilus were grown at 25°C in 1.2 ml DMSZ growth media #92
(biological duplicates) under three different culture conditions:
(1) without additional salts for 2 days
(2) with additional 13 wt% NaCl for 13 days
(3) with additional 11 wt% NaClO4 for 8 days
After the noted time of growth the cells reached the late exponential growth phase.
The total cell number was determined under the light microscope in a Thoma cell counting
chamber for all three samples. Afterward, the cell suspensions were centrifuged at 1000 xg
for 5 minutes. The cell pellets were washed first with PBS containing 10 wt% NaCl and then
a second time with PBS without additional NaCl. Both washing steps were performed at 4°C.
To lyse the cells the pellets were treated with a 20/80 mixture of water and acetonitrile (LC-
MS grade) followed by 5 minutes of ultrasonication. After 10 minutes of centrifugation at
16,000 xg the supernatant was transferred to mass spectrometry auto sampler vials and
measured in an untargeted approach with an ultra-high performance liquid
chromatography linked mass spectrometry. Analytes were separated in HILIC (hydrophilic
interaction liquid chromatography) mode with a gradient of acetonitrile and buffered water
(5% 10mM ammonium carbonate in water to 65% after 20 minutes, flow rate 200µL per
minute) on the Acquity UPLC BEH amide 1,7 µm and measured with both positive and
negative electron spray ionization. The Full-Scan mode had a resolution of 75000, whilst the
MS2 spectra were generated with a collision energy of 50 eV and a resolution of 35000. Data
analysis was performed with Compound Discoverer 2.1 by comparing acquired MS2 spectra
against mzCloud.
Supplementary Information
94
7.3.2 Results and Discussion
The following cell numbers were determined:
(1) 1.1·108 cells per ml for the sample with no additional salt
(2) 2.3·107 cells per ml for the sample with 13 wt% NaCl
(3) 5.3·106 cells per ml for the sample with 11 wt% NaClO4
In total, 4041 compounds where detected. 187 of those were annotated. Among those,
23 were defined as validated hits (high quality MS² spectra, bell shaped XIC traces, confident
quantification) which are summarized in table 7-1. It is clearly recognizable that in all three
samples betaine occurred at highest concentrations. It was enriched in the salty samples (2
log2-fold-change NaCl/no salt; 4 log2-fold-change NaClO4/no salt), however, enrichment
occurred for nearly all metabolites that were detected in all three samples. Most likely, the
reason for that phenomenon is that the cell density is 4.8 and 20.8 times higher in the salt-
free samples than in samples containing NaCl or NaClO4, respectively. In samples with a
lower cell density metabolite extraction is more efficient due to matrix effects.
Nevertheless, the large quantities found for betaine are a strong indication that this
substance serves as osmolyte as it does in many other halotolerant microorganisms
(Roberts, 2005). Furthermore, proline (and the related substances 4- and 5-oxoproline)
were detected which might contribute to the osmoprotection machinery of P.
halocryophilus as well. These findings fit well to the detection of several betaine and proline
transport proteins that are expressed under osmotic stress (Mykytczuk et al., 2013).
Another interesting metabolite detected is azobenzene, an orange-red azo-dye which might
contribute to the orange color of P. halocryophilus.
Supplementary Information
95
TAB. 7-1: Metabolites detected in lysed samples of P. halocryophilus grown in medium containing
no additional salt, 13 wt% NaCl, or 11 wt% NaClO
4
. Intensities (peak areas) are normalized to the
cell number.
Metabolite no salt
(Intensity)
13% NaCl
(Intensity)
NaCl
log2-fold
change
11% NaClO
4
(Intensity)
NaClO
4
log2-fold
change
Betaine 170129729 934061711 2 2555292664 4
Ethyl myristate 31794337 176551054 2 584343423 4
Stearic acid 19792209 128830432 3 381791994 4
5-Oxoproline 10856047 2936027 -2 26519143 1
Proline 8374058 113501747 4 589835936 6
4-Oxoproline 2601005 66510510 5 90532035 5
Nonanoic acid 1825810 13855231 3 51466229 5
Decanoic acid 919838 6795369 3 24838118 5
Pipecolinic acid 753501 14421527 4 47824413 6
Lauric acid 687274 2591367 2 29161925 5
Nicotinic acid 501591 6614138 4 24916096 6
Cetrimonium 452594 2491578 2 3496061 3
Bis(2-
ethylhexyl)adipate 101277 658426 3 2026420 4
2,4-Bis(2-phenyl-2-
propanyl)phenol 96310 641106 3 2127732 4
2,3,5,6-Tetra-
methylpyrazine 75384 545395 3 734724 3
Norharman 50771 2060568 5 6206966 7
N,N-Dimethylaniline 50355 401886 3 1289555 5
Cyclo(phenylalanyl-
prolyl) 42344 2410753 6 3220598 6
Cyclo(leucylprolyl) 37765 2446710 6 4022057 7
Citrulline 36953 310218 3 34410231 10
6-Methylquinoline 24740 395596 4 749027 5
Palmitoyl
ethanolamide 23551 129598 2 622668 5
Azobenzene 13741 467517 5 1315308 7
Supplementary Information
96
7.4 Supplementary Information on Publication III
7.4.1 Growth curves of Planococcus halocryophilus
All growth curves were obtained as described in chapter 2 of the main text
Cells were grown aerobically in liquid growth medium (DMSZ #92) containing salt
amounts as indicated within the figure legends
All curves obtained as biological duplicates (samples [A] and [B])
Dashed lines indicate a 2nd run of a specific experiment
X indicates the detection limit (no detectable CFU within 100 µl sample)
Negative error bars reaching values of y ≤ 0 CFU/ml were removed.
IM – Inoculation method as described in section 2.2 of the main text
Supplementary Information
97
FIG. 7-4: Growth curves in NaCl containing media at 25°C. NaCl 14% (IM 2) (sample B) got
contaminated.
Supplementary Information
98
FIG. 7-5: Growth curves in NaCl containing media at 4°C. Biological duplicates A and B were not
averaged for 9%- and 10%-samples due to differences in growth. No detectable CFUs in the 12%
NaCl sample after 200 days.
Supplementary Information
99
FIG. 7-6: Growth curves in MgCl
2
containing media at 25°C. MgCl
2
10% (IM 2) (sample B) did not
show growth.
Supplementary Information
100
FIG. 7-7: Growth curves in MgCl
2
containing media at 4°C. Biological duplicates A and B were not
averaged for 10%-samples due to differences in growth.
Supplementary Information
101
FIG. 7-8: Growth curves in CaCl
2
containing media at 25°C. (See also Fig. 4-1 in the main text).
Supplementary Information
102
FIG. 7-9: Growth curves in CaCl
2
containing media at 4°C. Biological duplicates A and B were not
averaged for 10%-samples due to differences in growth. See also Fig. 4-1 in the main text.
Supplementary Information
103
FIG. 7-10: Growth curves in NaClO
4
containing media at 25°C.
Supplementary Information
104
FIG. 7-11: Growth curves in NaClO
4
containing media at 4°C. NaClO
4
2% (IM 2) was inoculated with
culture grown in media with 3 wt% Ca(ClO
4
)
2
at 4°C. No detectable CFUs in NaClO
4
9% after 207
days.
Supplementary Information
105
FIG. 7-12: Growth curves in Mg(ClO
4
)
2
containing media at 25°C. Biological duplicates A and B were
not averaged for 4%- and 5%-samples due differences in growth.
Supplementary Information
106
FIG. 7-13: Growth curves in Mg(ClO
4
)
2
containing media at 4°C. Mg(ClO
4
)
2
2% (IM 2) was inoculated
with a culture grown in media with 3 wt% Ca(ClO4)2 at 4°C since inoculation with a culture grown
in 5% Mg(ClO
4
)
2
medium at 25°C (IM 4) did not result in growth.
Supplementary Information
107
FIG. 7-14: Growth curves in Ca(ClO
4
)
2
containing media at 25°C.
Supplementary Information
108
FIG. 7-15: Growth curves in Ca(ClO
4
)
2
containing media at 4°C.
Supplementary Information
109
7.4.2 Ionic strengths and water activities at the MSCg (additionally to Fig. 4-2 in the
main text)
FIG. 7-16: Ionic strengths (A) and water activities (B) at the MSCg. See also Tab. 4-1 and Fig. 4-2 in
the main text.
Supplementary Information
110
7.4.3 Cell colony morphologies of P. halocryophilus grown under salt stress conditions
(additionally to Fig. 4-4 in the main text)
FIG. 7-17: Irregular jagged colonies (type III) of P. halocryophilus occurring after bacterial growth in
medium containing 9 wt% MgCl
2
(A) or 4 wt% Mg(ClO
4
)
2
(B).
FIG. 7-18: Mucoid and shiny colonies (type IV) that merge easily during colony growth occurring
after bacterial growth in medium containing 6 wt% CaCl
2
(A) or 8 wt% CaCl
2
(B).
Supplementary Information
111
7.4.4 Fluorescence microscopy images (additionally to Fig. 4-5 in the main text)
FIG. 7-19: Fluorescence microscopy images (after life/dead staining) of cell clusters of P.
halocryophilus in 10 wt% NaClO
4
medium before (A) and after (B) killing all cells within one cluster
through ethanol treatment.
List of Publications
112
8. List of Publications
Publication I:
Title: Deliquescence-induced wetting and RSL-like darkening of a
Mars analogue soil containing various perchlorate and
chloride salts.
Authors: Jacob Heinz, Dirk Schulze-Makuch, Samuel P. Kounaves
Journal: Geophysical Research Letters (2016), 43(10), 4880–4884,
https://doi.org/10.1002/2016GL068919
Version: Postprint
License: CC BY-NC-ND 4.0 license (license terms cf.
http://creativecommons.org/licenses/by-nc-nd/4.0/)
Embedded in Dissertation: Chapter 2, pages 16 – 26.
Publication II:
Title: Enhanced Microbial Survivability in Subzero Brines.
Authors: Jacob Heinz, Janosch Schirmack, Alessandro Airo, Samuel P.
Kounaves, Dirk Schulze-Makuch
Journal: Astrobiology (2018), 18(9), 1171–1180,
https://doi.org/10.1089/ast.2017.1805
Version: Postprint
License: CC BY 4.0 license (license terms cf.
https://creativecommons.org/licenses/by/4.0/)
Embedded in Dissertation: Chapter 3, pages 27 – 45.
Title: Bacterial growth in chloride and perchlorate brines: Halotolerances and salt stress
responses of Planococcus halocryophilus.
Authors: Jacob Heinz, Annemiek C. Waajen, Alessandro Airo, Armando Alibrandi,
Janosch Schirmack, Dirk Schulze-Makuch
Journal: Astrobiology (2019), Epup ahead of print, https://doi.org/10.1089/
ast.2019.2069
Version: Postprint
License: CC BY-NC 4.0 license (license terms cf. https://creativecommons.org/
licenses/by-nc/4.0/)
Embedded in Dissertation: Chapter 4, 46 – 67.
List of Publications
Publication III:
Title: Bacterial growth in chloride and perchlorate brines:
Halotolerances and salt stress responses of Planococcus
halocryophilus.
Authors: Jacob Heinz, Annemiek C. Waajen, Alessandro Airo,
Armando Alibrandi, Janosch Schirmack, Dirk Schulze-
Makuch
Journal: Astrobiology (2019), Epup ahead of print,
https://doi.org/10.1089/ast.2019.2069
Version: Postprint
Licence: CC BY-NC 4.0 license (license terms cf.
https://creativecommons.org/licenses/by-nc/4.0/)
Embedded in Dissertation: Chapter 4, pages 46 – 67.
113