of 29
Supp
orting
Information for
Glycine synthesis from nitrate and glyoxylate mediated by ferroan brucite: a
new integrated pathway for
abiotic amine synthesis.
Chimiak, L.
1
; Hara, E.
1
; Sessions, A.
2
; Templeton, A.S
.
1
1
Department of Geological Sciences, University of Colorado, Boulder, CO
2
Department of Geological and Planetary Sciences, California Institute of Technology, Pasadena, CA
C
orresponding author
: Laura Chimiak
Email:
laura.chimiak@colorado.edu
This PDF file includes:
Supporting
text
Table S1
Figures S1 to S
14
SI References
Supporting
Information Text
Materials and methods
Synthesis
Syntheses were carried out in 30
-
mL serum vials, in an
anaerobic chamber (‘Coy chamber’). All
glassware was combusted at 450
C for eight hours prior to use. Brucite was synthesized from iron(II)
chloride tetrahydrate (Sigma Aldrich, Part#220299, 98% purity), magnesium hexahydrate (Sigma Aldrich,
Part#M9272, 99.0
-
102.0% purity), Iron (0) (VWR, Part#
AA00170
-
14, Lot#
G19X048), 12N hydrochloric
acid (Sigma Aldrich, Part#258148, 37%), potassium hydroxide (Sigma Aldrich), and water from a MilliQ
filtration system (18.3
,
hereafter, ‘water’). Water was vigorously bu
bbled for 30 minutes with pure N
2
(Airgas), put in the Coy chamber with a loose cap, and allowed to equilibrate for at least 24 hours prior to
use. For ferroan brucite synthesis, a 1.0 M magnesium hexahydrate solution and a 0.5 M iron chloride
tetrahydrate solution with 0.02 M Fe(0) and 0
.0008% HCl were made and equilibrated in a Coy chamber
for 24 hours prior to use. These were combined in a 1:1 volume to create a metal solution and 5.0 mL
were added to each serum vial. Brucite was precipitated by adding 6
mL of 2N KOH to each vial and
gently swirling the vials. The pH adjusted to 10 with 2N KOH. Minerals were left for one hour to settle after
which the aqueous phase was decanted and replaced with water that had been adjusted to pH 10 with 2N
KOH. This proc
ess was repeated 2 times, after which the pH was measured on an electronic pH meter
(Horiba LAQUAtwin pH
-
22 digital pH meter) and adjusted to pH 9.5 if needed. The magnesium hydroxide
brucite control followed the same protocol but used a 0.75M magnesium he
xahydrate solution instead of
the metal solution.
Directly after brucite synthesis, a 0.5 mL aqueous aliquot was drawn using a 25
-
gauge needle (BD, part
#305125) and 1.0 mL syringe (BD, Part #309628) for an initial pH measurement on a Horiba LAQUAtwin
pH
-
22 digital pH meter.
Following 24 hours, a second 0.5 mL aqueous aliquot was drawn, and a pH measurement was taken. The
pH was adjusted to 9.0 when samples were below this value
.
Reactant stock solutions were first constituted as separate solutions from water with glyoxylate
monohydrate (Sigma Aldrich, Part G10601, Lot WXBD7215V), potassium nitrate (Sigma Aldrich, Part#
221295), and ammonium chloride (VWR). To create reactant solutions,
5 mL of a 1.6 M glyoxylate
monohydrate stock solution and 5 mL of a
1.6 M nitrogen solution (
e.g.,
ammonium chloride or potassium
nitrate) were combined into a combusted glass vial. 2.50 mL of the reactant solution was added to the
brucite
-
containing vials via borosilicate glass pipette. Vials were capped with 20 mm blue butyl stoppers
(Fischer Science,
Item#
50
-
194
-
5347, multiple lots) and crimped with aluminum crimps (Sigma Aldrich,
multiple lots). Prior to use, butyl stoppers were washed three times with a 2N NaOH solution and
autoclaved.
Sampling
After two weeks, a 2.0 mL aliquot was taken from each sample using a using a 25
-
gauge needle and 3.0
mL syringe (BD, 309657). Prior to each extraction, the syringe was flushed with Argon (Airgas). The
aliquot was subsampled into three 2.0 mL microfuge tube
s (Eppendorf, EP022363344): 0.5 mL for a pH
measurement, 0.5 mL for NMR analysis, and 1.0 mL to be desalted and analyzed via LC
-
and GC
-
MS.
After six weeks, sample vials were taken into a Coy chamber, shaken, and decanted into a 50 mL Falcon
tube (Corning, CLS352070). Falcon tubes were subsequently capped, removed from the Coy chamber,
and put on a centrifuge at 1800 rpm for 3 minutes. Samples
were then transported back into the
anaerobic chamber, uncapped, and the aqueous phase was decanted into a new 50 mL Falcon Tube.
Aqueous fractions were subsampled into 2.0 mL microfuge tubes as follows: pH samples (0.5 mL), NMR
and IC samples (1.0 mL), a
nd two sets of archived samples (2.0 mL). The remaining aqueous fraction
was saved in the original Falcon tubes for cation columns. Mineral fractions had 1.0 mL subsampled into
microfuge tubes for column chemistry. The rest of the mineral fractions were sa
ved in the initial tubes for
XRD. All samples were capped inside of the anaerobic chamber, transported outside of the chamber, and
immediately placed in a
-
20
C freezer.
Amine Purification
Amine samples were purified and desalted for GC
-
MS and LC
-
MS analysis.
Prior to use, 5 mL Dowex X8
-
50W 50
-
100 mesh columns (Part: 44509, Sigma Aldrich, hereafter ‘Dowex’) were prepared by washing
with at least the following: 25 mL water, 25 mL 2N NH
4
OH (diluted from 37% NH
4
OH, Sigma Aldrich,
multiple lots), 25 mL water, 25 mL 4N HCl (diluted from 28
-
30% HCl, Sigma Aldrich, Part# 258148,
Multiple Lots), and finally, water until pH reached 5.
Aliquots of sample set aside for LC
-
and GC
-
MS
analyses were thawed and immediately partitioned into 1.0 mL samples for concentration analysis and
the rest for speciation and isotope analysis. The 1.0 mL samples were frozen until needed. Thawed
samples wer
e acidified to pH 2 or lower and loaded dropwise on a Dowex column. Columns were rinsed
with 25 mL of water, which was collected as a load fraction in a 50 mL Falcon tube. Then, a 40 mL glass
vial was placed under the column and amines were eluted with 25
mL of 2N NH
4
OH, which was collected
and dried to completion under N
2
. Following its dry down, samples were reconstituted in 0.5 to1.0 mL
water and partitioned between LC
-
MS and GC
-
MS analyses.
Analyses
NMR
NMR was conducted on samples in 10% D
2
O
(Sigma Aldrich)/90% H
2
O on a Bruker 400 MHz
spectrometer using 5 mm Bruker SampleJet NMR tubes (Wilmad, Part WG
-
1000
-
7
-
SJ, Multiple Lots). A
subset of samples was analyzed using a 10% D
2
O, 0.1% DSS solution in water (Sigma Aldrich, Part
373773, diluted with D
2
O above). Glycine, glycolic acid (Sigma Aldrich), glyoxylate, diglycine, triglycine,
tartarate, and DL
-
threo
-
β
-
hydroxyaspartic acid peaks were identified NMR spectra through standards
using a 10% D
2
O, 0.1% DSS solution in water (Figures S3
-
9).
These standards were added to tubes of
the sample solutions that had already been analyzed via NMR such that the matrix would be identical to
samples measured. Peaks were identified via subtraction. To constrain peaks from imine species,
glyoxylate was equ
ilibrated with NH
4
Cl for 24 hours in the matrix from a brucite sample that had had no
organics added (Sample 24) and had previously been processed for NMR. This imine sample was run in
10% D
2
O and peaks were compared to the initial brucite sample’s NMR and
the NMR from the glyoxylate
that had polymerized.
Samples were prepared for NMR using methods from Barge
et al
(201
9
). In short, 0.050 mL of 2N NaOH
was added to a 2.0 mL a microfuge tube containing 0.5 mL of each 2
-
week sample or 1.0 mL of each 6
-
week sample. Tubes were centrifuged at 1800 rpm for 3 minutes. When a mineral precipitated, the
sample’s supernatant was dec
anted into another microfuge tube containing 0.050 mL of 2N NaOH. This
process was repeated until no mineral precipitated from the sample. At this point, samples were frozen
until they neede
d to be analyzed via NMR. For NMR analysis, samples were thawed, and 0.400 mL was
pipetted into an NMR tube to which 0.040 mL of D
2
O or D
2
O with a DSS spike was added.
IC
An aliquot of samples prepared for NMR were analyzed on a Thermo Scientific Dionex ICS
-
5000 HPIC
system in anion mode for NO
3
-
and glyoxylate and in cation mode for NH
3
. For anion mode, samples were
first diluted to 1 part in 100 in water and analyzed against a suite of standards including NO
3
-
and
glyoxylate at concentrations ranging from 10
μ
M to 1000
μ
M. Standards were analyzed both in water at
1000
μ
M and in the same matrix as the samples. Samples and standards were measured on the IC using
an isocratic
gradient of 36.00 mM KOH
pumping at 1 mL/min, a Dionex IonPac AS25 column, and UV
-
Vis
detection at 214 cm
-
1
. For cation mode, samples were diluted to between 3 and 40 parts in 1000 in a 3
mM methylsulfonic acid solution. Standard solutions consisted of NH
3
ranging from 2
μ
M to 2000
μ
M in a
3 mM methylsulfonic acid solution. Samples and standards were analyzed on the same data on the IC
using an isocratic gradient of 3 mM methylsulfonic acid pumping at 1 mL/min, a Dionex Ionpac CS12A
column, and conductivity detection.
LC
-
MS
LC
-
MS analysis was performed on a Thermo Fisher Dionex UltiMate 3000 UHPLC system with an ISQ
EM single quadrupole mass spectrometer and Newchrom AH column (Newchrom, Part#, NAH
-
46.250.0510). Eluents were acetonitrile (Supelco OmniSolv, Part# 62258, Multip
le Lots), water, and formic
acid (Sigma Aldrich, Part# 33015, Lot# STBH6997). For preparation, all lines leading to the column were
washed with methanol for 10 minutes at a flow rate of 1.0 mL/min and then with the eluent for another 10
minutes at a flow r
ate of 1.0 mL/min. At the start of each measurement day, a 45
-
minute run of 95%
acetonitrile and 10% water was performed to remove any bubbles in the line. Measurements were made
with an isocratic pump method with 10.0% acetonitrile, 89.9% water, and 0.1%
formic acid. Standards
used to confirm retention times and key masses for glycine, diglycine (Sigma Aldrich, Item: 50199),
triglycine (Sigma Aldrich, Item: 50239), iminodiacetate, and DL
-
threo
-
β
-
hydroxyaspartic acid (Sigma
Aldrich, Item: h2775). These comp
ounds were prepared in water at concentrations of 6.6 mM to 6.6 x 10
-
5
mM. Samples were run in duplicate for 20 minutes each. Analyses were performed using Chromeleon
Software (Thermo Fischer).
GC
-
MS
For GC
-
MS analysis, samples were derivatized as N
-
trifluoroacetyl
-
O
-
methyl esters. To do so, they were
dried under N
2
in GC vials. A procedural blank with water and a glycine standard were concurrently
derivatized. Vials were placed in an ice bath, 400 uL of methanol (Sigma
-
Aldrich, Part# 322415) were
added to them, and then 100 uL of acetyl chloride (Sigma
-
Aldrich, Part
# 00990, Lot#BCCG5173) was
added dropwise while the vial was continuously swirled. Vials were then capped and heated to 70
C for 1
hour. Vi
als were allowed to cool, uncapped, and samples were dried to completion under N
2
. To these,
400 uL of hexane (Sigma Aldrich) and 200 uL of trifluoroacetic anhydride (Part# 106232, Lot# BCCH1476)
were added. Vials were capped and heated to 80
C for 30 minutes. Samples were dried to 25% of their
volume, 1.0 mL of hexane was added, and then samples were dried until ~50 uL remained. These
samples were transferred into 200 uL inserts (Thermo Scientific, Part # C4012
-
529) to which 100 uL of
hexane w
as added. The
glycine standard was not transferred into an insert but instead diluted 4 mM and
serially diluted by factors of 10 down to 4 x 10
-
5
mM.
GC
-
MS analyses of sample’s amine fractions N
-
trifluoroacetyl
-
O
-
methyl esters for 2
-
week samples were
performed on a Q
-
Exactive Orbitrap Mass Spectrometer with a 30 m TG
-
5SILMS column (Thermo
Scientific, Part# 26096
-
1420). Six
-
week samples were measured on
a Thermo Trace 1310 connected to a
TSQ 9000 with a 30 m Restek Column (Rxi
-
XLB, Part# 13708). All measurements were run with a
temperature ramp that started at 50
C and increased to 120
C. For standards, this final temperature was
held for 5 minutes. For s
amples, it was held for 25 minutes. Standards were run at the beginning and end
of measurement sessions and analytical blanks of hexane were run throughout. To decrease changes of
contamination, two hexane blanks were run after the initial standard measurements.
Analyses of GCMS data was done using XCalibur software (Thermo Fisher) and the NIST webbook for
peak identification. Excel was used to analyze
concentration data.
XRD
To prepare samples for analysis, minerals were thawed in a Coy chamber, pulled into a 5 mL syringe, and
filtered using a polypropylene syringe filter holder with a 0.20
μ
m hydrophilic filter (Millipore, Part#
GTTP02500, Lot# RODB51339) backed by a glass fiber filter (Whatman, Part# 1825
-
024, Lot# 9752460).
Filter paper with the mineral on it was transferred into a weigh boat, lightly capped with aluminum foil, and
left to
dry overnight in a desiccator in a Coy chamber. Once dried, samples were crushed using
an agate
mortar and pestle and transferred to a zero blank XRD plate (MTI Corporation, Item#ZeroSi24D10C1US)
in an anaerobic holder (Bruker, Item#
A100B33). To prevent the minerals from orienting in one direction,
samples were spread on the plates by using the narrow side of a spatula to lightly cut into the powder and
gently push it in a direction. This motion was done at multiple orientations until
the sample was spread out
over the plate. At this point, the holder was sealed and removed from the Coy cha
mber for immediate
XRD analysis on a Bruker X
-
Ray Diffractometer with a 0.1 mm divergence slit and the air scatter
suppressor seated on top of the sample holder. Samples were analyzed from a 2
of 5
to 65
or 75
with
a step increment of 0.0206 and a 2.0 second dwell time. An analytical blank of the sample holder with no
mineral was run to collect a background spectrum. Data were analyzed on Diffrac.Suite software (Bruker)
and on Excel by comparing output spectra
to mineral spectra on RRUFF
(
2
)
.
Raman Spectroscopy
After being analyzed
on the XRD,
Raman spectroscopy was conducted
on a subsample of the dried and
filtered mineral
at the Raman Microspectroscopy Laboratory, Department of Geological Sciences,
University of Colorado
-
Boulder (RRID:SCR_019305) on a Horiba LabRAM HR Evolution Raman
spectrometer equipped with a 100mW 532 nm excitation laser
with both a 50x and 100x objective, a
spectral range from 10
0
-
3000 cm
-
1
and a laser power of 25%. Specific points for spectral analysis were
selected in a manner to sample a
ll visually distinct mineral phases at least once. Minerals were identified
by comparison to known standards on the RRUFF database
(2)
.
Fourier
-
Transform Infrared Spectroscopy
A subsample of each dried and filtered mineral analyzed on XRD was mixed
with KBr powder and
pressed into pellets. These pellets were measured on a Thermo
-
Nicolet Nexus 670 FTIR spectrometer
with 128 spectral measurements per sample. Peak positions were compared to various literature sources
including the NIST database
(3)
.
Dilution and concentration corrections
Amine concentrations were corrected to be presented as millimolar values. To this end, glycine
concentrations were calculated according to the calibration curve on the GC
-
MS. Then, background
concentrations were subtracted. For aqueous samples, all samples
were taken from an initial 1 mL, so no
further corrections were required. Most mineral samples had overlying aqueous solution, amounts of
minerals hydrolyzed varied, and only some of the amine fraction was partitioned for GC analysis. To this
end, concent
rations for mineral samples were further corrected as follows. Firstly, the glycine
concentration in the sample was multiplied by the inverse of the fraction partitioned for GC analysis (
e.g.
,
if ½ was set aside for analyses, the concentration was multiplied by 2). Then, the contribution from the
aqueous portion was subtracted. This was found by taking the initial volume of solution in the mineral
sample (between 0 and 1 mL) and multiplying it
by the concentration of glycine per mL in the aqueous
samples. F
inally, mineral samples were normalized to 1 mL, which was accomplished by multiplying by
the inverse the of total volume of minerals in milliliters. These steps are summarized in Equation S1:
푓푖푛푎푙
=
(
푢푛푐표푟푟
푏푘푔푟푑
푎푚푖푛푒
푎푞
푎푞
)
1
푚푖푛
(Eqn. S1)
where C
final
is the final glycine concentration in mol/mL, C
uncorr
is the uncorrected measured concentration
of glycine in mol/mL, C
bkgrd
is the background concentration of glycine in the GC
-
MS, f
amine
is the fraction
of the amine sample used in the measurement,
V
aq
is the volume of aqueous solution purified with the
mineral fraction in mL, C
aq
is the background corrected concentration of glycine in the aqueous sample in
mol/mL, and V
min
is the volume of minerals that were hydrolyzed and purified.
A secondary check on hydrolyzed mineral samples was performed by using a portion of the samples for
XRD that had been put in an anaerobic chamber where they were filtered, rinsed with degassed MilliQ
water, and dried. These samples were purified in the sam
e manner as the previous aqueous and mineral
samples and measured on a GC
-
MS. These samples, shown in Figure S4d, had slightly higher glycine
concentrations than the samples used in the manuscript thereby confirming that the glycine was sorbed
on the miner
al and not created by an aerobic reaction between constituents in the aqueous and mineral
phases during sample processing.
All samples were assigned standard deviation by adding in quadrature the standard deviation from two to
four replicate measurements of the area under the glycine peak in a given sample with that of the
procedural blank. As mineral fractions only had one me
asurement, the standard deviation of glycine
concentration in these were assumed equal their aqueous counterparts. For total glycine concentration
error, therefore, the standard deviation of the aqueous measurement was added in quadrature with itself.
Iron Concentration Calculation
In the work here, the limiting
reagent is always the concentration of Fe(OH)
2
, which at most has a 125
mM concentration. This concentration is found by taking the 5 mL of 0.75 M Fe
0.33
,Mg
0.66
Cl
2
that is initially
added to vials. We assume that the Fe
2+
will be in brucite before the overlying water is washed. If all 1.25
mmol of Fe
2+
remains, this in 20 mL of solution gives the 62.5 mM concentration used in the calculations
below when determining the maximum possible yield of glycine.
In all samples, the imine must be reduced to an amino acid via a 2
-
electron transfer, so for each glycine
made, at least 2 equivalents of Fe
2+
must be oxidized, resulting in a maximum of 31.25 mM glycine
production possible. However, samples that use nitrate also require an 8
-
electron transfer to reduce
nitrate into ammonia. Due to all samples having the same amount of brucite, the nitrate syste
m samples
are 4
-
fold more Fe
2+
-
limited, so at most could produce a 6.25 mM glycine concentration. That one sample
achieves this, rather than forming high abundances of glycolate, leads to the possibility that the high local
negative change from the nitrate while bound to iron sites on the brucite might have led to less glyoxylate
reducing to form glycolate and therefo
re being available for reductive amination.
Mineralogical analyses
Ferroan brucite is more stable above pH 8.5
(
4
), so samples from the ammonia system, whose final pH
were circumneutral (Table 1), had a noisier XRD pattern due to partial dissolution of the mineral during
the experiments. These
experiments’ XRD spectra have only one potential additional feature at 2
θ
of 35°,
which could indicate a minor magnetite component (Figure S12). Samples from the nitrate system have
multiple new peaks including those at 2
θ
of 12°, 23°, 34°, 46°, 60°, and 61°, which suggest the presence
of pyroaurite or iowaite (
Mg
6
Fe
2
(OH)
16
[CO
3
]·4H
2
O,
Mg
6
Fe
3+
2
(OH)
16
Cl
2
·4H
2
O
) and those at 30°, 36°, and
43° which suggest the presence of magnetite (
Fe
2+
Fe
3+
2
O
4
)
(Figure S4). Peaks at 2
θ
of 18° and 38° could
indicate magnetite and pyroaurite or iowaite respectively; however, they are also indicative of ferroan
brucite so are not unique identifiers.
FTIR analysis also detects the minor new mineral components the nitrate systems and not the ammonia
systems (Figure S13). FTIR spectra of ammonia system minerals matched those of the magnesium
brucite and the unreacted ferroan brucite controls. Conversely,
spectra of nitrate system minerals had
peaks at 837, 1320, and 1630 cm
-
1
which correspond to Fe(NO
3
)
3
(
3
)
and at 1107 and 1373 cm
-
1
which
corresponds to the Fe
2+
and NO
3
-
components as determined by comparison to spectra of Fe(NO
3
)
2
complexed to NiO
(
5
)
(Figure S12). The broad FTIR peak near 568 cm
-
1
also support the presence of
magnetite
(
6
)
(Figure S13). While the bulk minerals in the ammonia system predominantly had brucite,
those in the nitrate system sequester nitrate ions as a nitrate
-
substituted pyroaurite, which demonstrates
a clear interaction with the mineral and the reactant ions.
Raman spectra were measured on the oxidized mineral samples to perform an investigation of minor
mineral components that might be overshadowed during the above analyses. Raman spectra of ammonia
system mineral samples broadly matched those of the ferroan b
rucite control and showed no strong
indication of organics present on the mineral surfaces studied (Figure S14a). The oxidized samples had
peaks at 214, 280, 384, 415 and a shoulder at 600 cm
-
1
, which matched spectra of hematite
(
7,8
)
(Figure
S13a). An additional peak at 684 cm
-
1
could indicate the presence of magnetite
(
7,8
)
(Figure S14a).
On the other hand, nitrate samples had variable spectra depending on the grain type. Most grains in the
oxidized nitrate samples matched those of the ammonia samples with 214, 280, 391, 598 cm
-
1
peaks
matching spectra of hematite and a 655 cm
-
1
peak indicative of magnetite
(
7,8
)
. However, the dark grains
showed different spectra with peaks at 224 and 526 cm
-
1
, which match spectra of lepidocrocite
(
9
)
(Figure
S14b). This mineral is associated with organics as indicated the peaks from a C
-
C stretching mode at 918
and 951 cm
-
1
, a CH
3
bending mode at 1443 cm
-
1
, and C
-
O stretch at 1637 and 1662 cm
-
1
, and a CH
3
stretching mode at 2905 cm
-
1
. Furthermore, the spectrum has minor peaks at
1057 1092 (NO
3
-
stretching
mode) and 1443 (NO
2
stretching mode), which indicate the presence of nitrate (Figure S14b).
Mechanism
We posit that in ammonia systems, the canonical reductive scheme amination occurs (Figure 4, Main
text). Ammonia attacks the carbonyl carbon is the
α
-
C on glyoxylate to form 2
-
amino
-
2
-
hydroxyacetic
acid, which is in equilibrium with both glyoxylate and 2
-
i
minoacetic acid. Either 2
-
amino
-
2
-
hydroxyacetic
acid or 2
-
iminoacetic acid can be reduced to glycine (Gomez
et al
, 2002). In nitrate systems, nitrate is first
reduced to nitrite from which it can either become nitrous oxide or hydroxylamine and then ammoni
a
(Wong
et al
, 2023). The ammonia can then follow canonical reductive amination and results in glycine
that is associated with the mineral such that only acid hydrolysis fully liberates it. Due to the association
between organics, nitrogen species, and FeO(OH), we posi
t that this binding occurs at Fe
3+
sites (Figure
4b main text, Figure S14).
As noted in the text the ammonia systems produce more glycine than should be feasible given the
electrons available in ferroan brucite for reductive amination. Given that a small amount of glycine is also
detected in both the aqueous phase of the magnesium
brucite control and also in the non
-
mineral
controls in Barge
et al
(2020), we assume that this result points to a real side reaction. The NMR and IC
results in this study demonstrate that formate is present. Barge
et al
(2020) also find this in their wor
k.
The Leuckart reaction uses ammonium formate or formamide to perform reductive amination as depicted
in Schemes S1 and S2 (11). Here, formate acts as the reductant. While this synthesis typically requires
temperatures higher than those used in this experiment (120°C and above), the presence of certain metal
complexes can reduce these temperatures to roughly 50°C (11,12).
Here, at 6 weeks, the ammonia system experiments have a pH below 9.2
the pK
a
of ammonium
and
have excess ammonium, glyoxylate, and formate. Consequently, if the minerals present can in the
ammonium system can allow Leuckart reaction to proceed at roughly 20°C even at a slow rate, it could
explain the additional 38 ± 15 % and 21 ±
4 % yields relative to the 100 mM glyoxylate and 100 mM
ammonia here. This proposed mechanism is speculative, and further work needs to occur in order
ascertain the mechanism by wh
ich glycine is formed when iron cannot provide adequate electrons and
formate is present.
Table
S
1:
Concentrations of glycine, aqueous phase reactants, and pH of samples at 6 weeks. Glyox refers to glyoxylate. Yield versus Fe
2+
total glycine that
could be produced from the 62.5 mM Fe(OH)
2
, which is 31.25 mM glycine in ammonia systems and 6.25 mM glycine in nitrate systems.
N
Source
mineral
pH
6
wks
[NO
3
-
]
0 wks
(mM)
[NO
3
-
]
6 wks
(mM)
[NH
3
]
0 wks
(mM)
[NH
3
]
2 wks
(mM)
[NH
3
]
6
wks
(mM)
[Glyox]
0 wks
(mM)
[Glycine]
aqueous
(mM)
St
Dev
[Glycine]
mineral
(mM)
[Glycine]
total
(mM)
yield vs
glyox
and N
(%)
yield vs
Fe
2+
(%)
NH
3
Fe,Mg(OH)
2
7.81
0
0
1E+02
2E+01
3E+01
1E+02
4.3E+01
2.0E+00
8.8E+00
5.2E+01
52 ± 4
167 ± 13
NH
3
Fe,Mg(OH)
2
7.89
0
0
1E+02
2E+01
3E+01
1E+02
5.1E+01
7.7E+00
1.8E+01
6.9E+01
69 ± 15
222 ± 50
NO
3
-
Fe,Mg(OH)
2
9.07
1E+02
5E+01
0
6E+01
3E
-
01
1E+02
2.9E
-
02
4.7E
-
03
7.3E
-
02
1.0E
-
01
0.1 ± 0.1
1.6 ± 0.3
NO
3
-
Fe,Mg(OH)
2
8.28
1E+02
5E+01
0
6E+01
0
1E+02
1.1E
-
01
4.5E
-
02
3.0E+01
3.1E+01
3.1 ± 0.2
50 ± 1
NO
3
-
Mg(OH)
2
9.43
1E+02
4E+01
0
0
0
1E+02
2.3E
-
02
3.5E
-
03
0.0
2.7E
-
02
0.4 ± 0.1
0.4 ± 0.2
None
Fe,Mg(OH)
2
9.41
0
0
0
0
0
0
0.0
3.7E
-
03
N/A
0.0
0.0
0.0
Fig. S1.
Depiction of methods used in this study. Processes on the right
-
hand side of the dotted line are
performed in anaerobic conditions under a 95% N2/5% H2
atmosphere. Raman and FTIR are exceptions
to this and are performed in aerobic conditions. All processes on the lefthand side of dotted line are
performed in aerobic conditions.
Figure c
reated with BioRender.com
.
Fig. S2.
GC
-
MS of
N
-
trifluoroacetic
-
O
-
methyl ester of glycine at (a) 2 weeks on the Orbitrap GC
-
IRMS
where glycine elutes at 4.60 minutes and at (b) 6 weeks on a GC
-
MS where glycine elutes at 3.65
minutes. Panel (c) is the same data as (b) but zoomed in to see the nitrate s
ystem and control peaks.
Panel (d) is from mineral samples with no overlying aqueous phase. Aq samples are from the aqueous
phase and mins samples are from hydrolyzed minerals. In panel (b), 45 and 57% of the glycine in the
mineral samples for the NH
3
syst
ems were from overlying aqueous phase. This contribution has not been
removed from the figure as the additional glycine explains the peak shape (i.e., the column overloading).
All NH3 system samples are in green,
NO
3
-
system samples are in blue,
magnesium brucite controls are
in plum, and ferroan brucite controls are in orange. Mineral samples are lighter in color than their aqueous
counterparts.