of 8
Novel sulfur isotope analyses constrain sulfurized porewater
fl
uxes as a minor component of marine dissolved
organic matter
Alexandra A. Phillips
a,1,2
, Margot E. White
b
, Michael Seidel
c
, Fenfang Wu
a
, Frank F. Pavia
a
, Preston C. Kemeny
a
, Audrey C. Ma
d
,
Lihini I. Aluwihare
b
, Thorsten Dittmar
c,e
, and Alex L. Sessions
a
Edited by Franc ̧ois Morel, Princeton University, Princeton, NJ; received June 19, 2022; accepted September 2, 2022
Marine dissolved organic matter (DOM) is a major reservoir that links global carbon,
nitrogen, and phosphorus. DOM is also important for marine sulfur biogeochemistry
as the largest water column reservoir of organic sulfur. Dissolved organic sulfur (DOS)
can originate from phytoplankton-derived biomolecules in the surface ocean or from
abiotically
sulfurized
organic matter diffusing from sul
fi
dic sediments. These sources
differ in
34
S/
32
S isotope ratios (
δ
34
S values), with phytoplankton-produced DOS track-
ing marine sulfate (21
) and sulfurized DOS mirroring sedimentary porewater sul
fi
de
(
0to
10
). We measured the
δ
34
S values of solid-phase extracted (SPE) DOM
from marine water columns and porewater from sul
fi
dic sediments. Marine DOM
SPE
δ
34
S values ranged from 14.9
to 19.9
and C:S ratios from 153 to 303, with lower
δ
34
S values corresponding to higher C:S ratios. Marine DOM
SPE
samples showed con-
sistent trends with depth:
δ
34
S values decreased, C:S ratios increased, and
δ
13
C values
were constant. Porewater DOM
SPE
was
34
S-depleted (
-0.6
) and sulfur-rich (C:S
37) compared with water column samples. We interpret these trends as re
fl
ecting at
most 20% (and on average
8%) contribution of abiotic sulfurized sources to marine
DOS
SPE
and conclude that sulfurized porewater is not a main component of oceanic
DOS and DOM. We hypothesize that heterogeneity in
δ
34
S values and C:S ratios
re
fl
ects the combination of sulfurized porewater inputs and preferential microbial scav-
enging of sulfur relative to carbon without isotope fractionation. Our
fi
ndings
strengthen links between oceanic sulfur and carbon cycling, supporting a realization
that organic sulfur, not just sulfate, is important to marine biogeochemistry.
dissolved organic matter
j
dissolved organic sulfur
j
stable isotopes
j
marine sulfur cycle
j
sulfurization
Dissolved organic matter (DOM) is the largest inventory of
fi
xed carbon in the ocean
(
662 Pg carbon) and is a critical component of marine food webs and nutrient
cycling (1). DOM has been hypothesized to impact climate over geological time scales
via carbon sequestration (1), as a highly recalcitrant subset of DOM persists for many
thousands of years, surviving multiple mixing cycles of the ocean for poorly understood
reasons (2
4). Therefore, despite decades of intensive study, fundamental questions
remain regarding DOM sources and sinks in the modern ocean.
Ksionzek et al. demonstrated that solid-phase extracted DOM (DOM
SPE
) contains a
substantial quantity of organic sulfur (5). The marine dissolved organic sulfur (DOS)
pool is estimated to contain
7 Pg sulfur, more than 10 times that in phytoplankton,
bacteria, and particulate organic sulfur (POS) combined (6). Although estimates of DOS
concentration vary (5, 7), it is nevertheless clear that DOS is central to marine sulfur
cycling (6), with growing evidence for important links to carbon cycling. For example,
reduced sulfur compounds within DOS lower trace metal availability by tightly binding
free zinc and copper and potentially limiting primary production (8). Concentrations of
alkyl thiols, such as the amino acid cysteine, have been correlated to chlorophyll concen-
trations, implying further connections to phytoplankton growth (9, 10). DOS metabo-
lites may also limit the growth of some marine heterotrophs, as clades of the ubiquitous
SAR11 and SAR86 bacteria are unable to assimilate sulfate and must rely on scavenging
reduced OS from the water column (11, 12). It remains unknown whether this subset of
S-containing molecules (i.e., DOS) within DOM behaves similarly to the larger dissolved
organic carbon (DOC) pool or has unique origins and/or dynamics.
A
fi
rst-order question regarding DOS dynamics is the origin of the organic com-
pounds (Fig. 1). Ksionzek et al. proposed a DOS cycle that mirrors DOC, with DOS
produced mainly by phytoplankton in the sunlit ocean. Under this hypothesis, microbial
reworking during the aging of DOS, such as heterotrophic uptake for growth or remi-
neralization back to sulfate, leaves remaining DOS compounds increasingly recalcitrant.
Signi
fi
cance
Marine dissolved organic matter
(DOM) is a vast reservoir of
enigmatically old carbon with
important connections to the
global carbon cycle and climate.
Previous work hypothesized that
highly recalcitrant,
sulfurized
organic matter from sul
fi
dic
sediments could potentially
account for this long-lived carbon.
To quantify the contribution of
this source, we made sulfur
isotope measurements of marine
DOM, measuring samples across
the Paci
fi
c and Atlantic Oceans as
well as from the porewaters of
sul
fi
dic sediments. We found
δ
34
S
values and C:S ratios that were
consistent with
8% contribution
of this abiotic source and conclude
that these sulfurized porewater
fl
uxes are not a main component
of oceanic DOM budgets.
Author contributions: A.A.P. and A.L.S. designed research;
A.A.P., M.E.W., M.S., F.F.P., P.C.K., L.I.A., and T.D.
performed research; A.A.P., F.W., and A.L.S. contributed
new reagents/analytic tools; A.A.P., F.W., A.C.M., and A.L.S.
analyzed data; and A.A.P., M.E.W., M.S., L.I.A., T.D., and
A.L.S. wrote the paper.
The authors declare no competing interest.
This article is a PNAS Direct Submission.
Copyright © 2022 the Author(s). Published by PNAS.
This article is distributed under
Creative Commons
Attribution-NonCommercial-NoDerivatives License 4.0
(CC BY-NC-ND)
.
1
Present address: Earth Sciences Department, University
of California Santa Barbara, Santa Barbara, CA 93016.
2
To whom correspondence may be addressed. Email:
phillips.alexandra.a@gmail.com.
This article contains supporting information online at
http://www.pnas.org/lookup/suppl/doi:10.1073/pnas.
2209152119/-/DCSupplemental
.
Published October 6, 2022.
PNAS
2022 Vol. 119 No. 41 e2209152119
https://doi.org/10.1073/pnas.2209152119
1of8
RESEARCH ARTICLE
|
EARTH, ATMOSPHERIC, AND PLANETARY SCIENCES
DOS may therefore offer a unique lens to DOM cycling more
broadly (5). A second hypothesis by Pohlabeln et al. posits that a
signi
fi
cant portion of DOS originates in euxinic sediments (13).
Here, sul
fi
de produced via microbial sulfate reduction reacts abi-
otically with organic molecules to
sulfurize
organic matter
(14
16). The resulting covalent C-S bonds are thought to be
resistant to microbial degradation as a result of stable S-S cross-
linking and replace otherwise more labile functional groups
(17
19). As such, sulfurization reactions have been recognized as
an important pathway for sedimentary organic matter preserva-
tion (20
22) and implicated in the carbon cycles of the ancient
ocean (e.g., during ocean anoxic events (20, 23)). In modern
euxinic sediments, these reactions are a major process: in a study
of sedimentary porewater from the Santa Barbara Basin, 70% of
detected DOS
SPE
formulas were products of sul
fi
de and polysul-
fi
de sulfurization reactions (24). Pohlabeln et al. calculated the
fl
ux of these highly recalcitrant DOS species as a signi
fi
cant
source to benthic DOS
SPE
and by extension to water column
DOM
SPE
(13). While the proportion of DOM molecules that
contain sulfur is not known precisely, estimates from molecular
formulas of SPE DOM imply it could be
5
10% (7). Such
numbers suggest that porewater-sourced, sulfurized molecules
could represent an overlooked subcycle within DOM and might
also help to explain why some components of DOM
SPE
have
surprisingly long lifetimes, clarifying connections between DOC
and DOS cycles in the ocean (25).
The sulfur isotopic composition of DOS
SPE
can distinguish
between organic matter produced by phytoplankton or by pore-
water reactions because these sources differ in
δ
34
S values by
30
(Fig. 1). This signal is easily resolved given typical mea-
surement errors on organic sulfur of
±
0.2
(26). Although
carbon and nitrogen isotopic measurements have previously
proven useful for studying marine DOM
SPE
(e.g., (27)), to our
knowledge, no such measurements have been made for sulfur,
likely for two reasons. First, dissolved inorganic sulfate, at 28
mM, is 4
5 orders of magnitude higher in concentration than
DOS
SPE
(
100 nM). To isolate organic sulfur compounds
from this high salt background, studies rely on SPE on a
styrene-divinylbenzene stationary phase (Bond Elute PPL (28))
that is considered to impart negligible isotope fractionations for
Fig. 1.
A simpli
fi
ed marine organic sulfur cycle highlighting processes that may impact the sulfur isotope composition and sulfur content of dissolved
organic sulfur (DOS). Numbers underneath each reservoir give the approximate
δ
34
S value and molar C:S ratio, based on initial studies of organic sulfur in
phytoplankton (39, 40), water column DOS (5), and particulate organic sulfur (POS) (42
44), porewater DOS (13), and porewater sul
fi
des (54). Results from
this study are highlighted in pink. Through lysis, exudation, and senescenc
e, phytoplankton biomass enters the DOS pool. DOS may also originate from
sedi-
ments, where sul
fi
de is incorporated into sedimentary organic matter to form sulfurized DOS. The sulfur isotopic composition of DOS
SPE
indicates the rela-
tive balance of these two sources.
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https://doi.org/10.1073/pnas.2209152119
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organic compounds (29
31) and should be negligible for sulfur
atoms that do not participate in hydrophobic binding interac-
tions. For example, hydrophobic separation of volatile organic
sulfur compounds by gas chromatography does not yield frac-
tionation of sulfur isotopes across peaks (32). PPL resins isolate
DOM with moderate yields for DOC (
60%), low (
21%)
yields for DON, and unknown yields for DOS (33). However,
given that abiotically sulfurized organic matter typically has sulf-
hydryl groups and hydrophobic hydrocarbon regions (24), and
given the associated mechanism of retention on SPE columns,
PPL should be well suited for retention of sulfurized DOM.
Indeed, in a study of dozens of model organic sulfur com-
pounds, extraction ef
fi
ciency was highest for uncharged, slightly
polar, medium-sized analytes (34). Furthermore, both experimen-
tally sulfurized organic matter (13) and sulfurized organic matter
from euxinic sediments (24) have been shown to be retained on
PPL resins for molecular characterization. We therefore expect
δ
34
SratiosandC:SratiosofDOS
SPE
to preferentially retain sulfu-
rized components of bulk DOM. Here, we show that SPE also
reduces sulfate contamination to nondetectable levels, allowing
accurate isotopic measurements of DOS
SPE
. The second problem
is that conventional isotope ratio mass spectrometry (IRMS)
methods have required much more sulfur (
70
μ
g) than carbon
(
20
μ
g). Given that DOM
SPE
has high C:S ratios (
150
300),
traditional techniques would require extraction from hundreds
of liters of seawater per measurement. Recent developments in
combustion elemental analysis IRMS (EA-IRMS) have enabled
much lower sample sizes (1-10
μ
g sulfur (26)) for organic sulfur
compounds. Here, we used the SPE method and adapted our
EA-IRMS measurements to allow simultaneous determination of
δ
13
Cand
δ
34
S values, and C:S molar ratios on samples of
350
μ
gDOM
SPE
. We applied this approach to extracts from the
Paci
fi
c and Atlantic coastal zones and ocean basins, generating
pro
fi
les of
δ
34
SvaluesofmarineDOM
SPE
. Our data indicate
that porewater sulfurization reactions contribute minimally to
the marine DOS
SPE
pool, and by extension, DOS and DOM.
Results
A global sample suite of 90 marine,
fi
ve estuarine, and
fi
ve pore-
water DOM
SPE
samples were analyzed for
δ
13
Cand
δ
34
Svalues,
and C:S molar ratios (Fig. 2
A
and
SI Appendix
,TableS1
). Sam-
ples spanned gyres, shelves, restricted basins, oxygen minimum
zones (OMZs), and coastal oceans.
Porewater and Estuary Samples.
Porewater DOM
SPE
was ana-
lyzed from sul
fi
dic sediments in the back barrier tidal
fl
ats of
the North Sea, yielding a
δ
34
S value of
0.2
, C:S molar ratio
of 18, and
δ
13
C value of
23.3
. Meanwhile, porewater
DOM
SPE
samples from sul
fi
dic sediments in the mangrove
tidal creek within the Caet

e Estuary ranged in
δ
34
S values from
2.7 to 0.7
, with C:S molar ratios between 40 and 45 (Fig.
2
B
) and
δ
13
C values between
27.1 and
26.8
. DOM
SPE
surface water samples from the Caet

e Estuary were analyzed
across a transect from the coastal ocean to the mangrove-
fringed estuary. C:S ratios ranged from 74 to 117, with
δ
34
S
values between 4.2 and 8.7
.
δ
13
C values spanned
28.6 to
24.2
across the transect.
A
BC
Fig. 2.
(
A
) Sample locations spanned gyres (N Atlantic: pink triangles, N Paci
fi
c: green triangles, S Paci
fi
c: dark blue triangles), shelves (NE Paci
fi
c Shelf:
yellow circles), mangrove-fringed estuaries (Caet

e Estuary: light blue left-facing triangles), restricted hypoxic basins (San Pedro Basin: turquoise diamonds),
oxygen minimum zones (NE Paci
fi
c OMZ: magenta squares), coastal settings (NE Paci
fi
c: light pink right-facing triangles), and sul
fi
dic porewater (North Sea:
dark gray down-facing triangles). (
B
)
δ
34
S values against C:S ratios of all analyzed DOM
SPE
samples (
n
=
100). (C) Expanded view of marine DOM
SPE
samples,
showing a negative correlation between DOM
SPE
δ
34
S values and C:S ratios (
R
2
=
0.24,
P
<
0.001). 1
σ
SEs are shown for all samples in (
B
) and (C), but in
many cases, are within the size of the symbol. VCDT, Vienna Canyon Diablo Troilite.
PNAS
2022 Vol. 119 No. 41 e2209152119
https://doi.org/10.1073/pnas.2209152119
3of8
Marine Samples.
Marine DOM
SPE
ranged in
δ
34
S values from
15 to 20
and in molar C:S from 150 to 300. We recognized
three distinct behaviors over different depth intervals for
DOM
SPE
measurements, across all sampling locations (Fig. 3 and
Table 1). For the purpose of calculating quantitative statistics, we
chose typical cutoffs for epipelagic (150 m) and bathypelagic
(750 m) zones, while recognizing that such sharp boundaries are
somewhat arbitrary and may vary throughout the world
s oceans.
In the epipelagic shallow samples between 0 and 150 m , C:S
ratios of DOM
SPE
increased (
R
2
=
0.23;
P
<
0.005), resulting in
DOC (
R
2
=
0.48;
P
<
0.001) and apparent (see
Materials and
Methods
)DOS
SPE
concentrations (
R
2
=
0.39;
P
<
0.005) that
decreased sharply with depth, and
δ
34
Sand
δ
13
Cvaluesdidnot
change signi
fi
cantly. Average
δ
34
SvaluesandC:Sratioswere
18.6
±
0.8
and 213
±
32, respectively, in this interval. At
mesopelagic depths, between 150 and 750 m, the C:S ratios did
not change. Because DOC decreased gradually, apparent DOS
SPE
also decreased gradually.
δ
34
S values decreased signi
fi
cantly (
R
2
=
0.32;
P
<
0.005), while
δ
13
C values did not change. Average
δ
34
S values and C:S ratios were 17.8
±
0.8
and 236
±
24,
respectively. In the bathypelagic samples, between 750 and
5,000 m, none of the parameters showed statistically signi
fi
cant
Table 1. Properties of marine DOM
SPE
samples binned by depth
Depth range (m)
DOM
SPE
C:S (molar)
DOM
SPE
δ
34
S(
)
DOM
SPE
δ
13
C(
)
DOC (
μ
M)
DOS (nM)
0
150
213
±
32
18.6
±
0.8

22.4
±
0.3
62
±
13
283
±
66
150
750
236
±
24
17.8
±
0.8

22.2
±
0.3
46
±
6
192
±
33
750
5,000
252
±
27
17.1
±
1.1

22.2
±
0.3
41
±
3
163
±
19
Averages are reported with 1
σ
SDs.
AB
DE
C
Fig. 3.
DOM
SPE
properties plotted against depth for (
A
) C:S ratios, (
B
)
δ
34
S values (
C
)
δ
13
C values, (
D
) DOC concentration, and (
E
) calculated DOS concentra-
tion. Note the scale breaks at 150 m, 750 m on the
y
axis. Colors and symbols for stations are the same as in Fig. 2; signi
fi
cant correlations are marked in
gray. 1
σ
SEs are shown for
δ
34
S values, but error bars for C:S,
δ
13
C values, DOC, and DOS are within the size of the symbol. DOM
SPE
C:S ratios slightly
increased with depth in the
fi
rst 150 m, but did not change signi
fi
cantly between 150 and 5,000 m.
δ
34
S values averaged 18.6
in the
fi
rst 150 m and
decreased between 150 and 750 m to an average of 17.1
. DOM
SPE
δ
13
C values did not change systematically with depth. Both DOC and DOS concentra-
tions decreased within the
fi
rst 150 m, but did not vary further with depth. For station-speci
fi
c plots, see
SI Appendix
(
SI Appendix
, Figs. S8, S9, S11
S14
).
4of8
https://doi.org/10.1073/pnas.2209152119
pnas.org
correlations with depth. Average
δ
34
SvaluesandC:Sratiosinthe
deepest samples were 17.1
±
1.1
and 252
±
27, respectively.
DOM
SPE
δ
13
C values were constant throughout the water col-
umn, with an average of
22.3
±
0.3
.DOM
SPE
δ
34
S values
also had statistically signi
fi
cant positive correlations with DOC
concentration (
R
2
=
0.25;
P
<
0.001) and, therefore, apparent
DOS
SPE
concentration (
R
2
=
0.38;
P
<
0.001) and tempera-
ture (
R
2
=
0.28;
P
<
0.001), although all these parameters
covaried with depth (
SI Appendix
,Fig.S7
).
Discussion
To assess the possible contribution of sulfurized porewater
DOS sources to the open ocean using a two-parameter (
δ
34
S,
C:S), two-endmember mixing calculation, we
fi
rst constrained
1) the composition of biotic DOS
SPE
in the surface ocean,
which we de
fi
ned as the upper 50 m of the water column, and
2) the composition of abiotic DOS
SPE
in sul
fi
dic porewaters.
The results of 1) and 2) allow us to conclude that 3) there is
limited isotopic evidence for porewater sources to global marine
DOS
SPE
and more broadly, to DOS and DOM. Finally, we
discuss 4) potential mechanisms for observed sulfur isotope het-
erogeneity with depth.
Composition of Biotic DOS in the Surface Ocean.
Primary pro-
ducers in the photic zone invest energy to transform inorganic sul-
fate into biomass through assimilatory sulfate reduction (6). Very
few studies have examined the consequences of these reactions for
the sulfur isotope composition of organic matter in phytoplank-
ton; preliminary measurements of marine algae found that bulk
biomass was minimally (by 0.8
)
34
S-depleted from marine sul-
fate (35), which is a nearly constant 21
(36). Further work on
phytoplankton dimethylsulfoniopropionate and dimethyl sul
fi
de
(DMS) found
34
S-depletions from marine sulfate by
1
3
(37
39). Our dataset of surface DOM
SPE
δ
34
S(
<
50 m depth)
values averaged 18.6
±
0.6
, which aligns with these studies
and supports the idea that phytoplankton-derived organic sulfur
in the surface oceans is only slightly fractionated (by up to
3
) relative to marine sulfate.
There are few studies that have investigated C:S ratios of
organic matter from primary producers, but most converge on
similar amounts of organic sulfur as phosphorous (i.e., S:P
1).
Laboratory experiments found cultures of
Synechococcus
incor-
porating carbon, nitrogen, and sulfur at a ratio of 95:16:1 (40).
A study of 15 marine eukaryotic phytoplankton found average
stoichiometries for C:N:P:S of 124:16:1:1.3 (41). Meanwhile,
suspended marine POS, which is assumed to derive from phy-
toplankton, has C:N:S ratios of
110
187:27:1 in the North
Paci
fi
c (42
44). Euphotic zone DOM
SPE
(
<
50 m depth) C:S
ratios in this study were similar, averaging 192
±
25 and rang-
ing between 153
243. This aligns with previous measurements
of DOM
SPE
C:S ratios, which ranged between 188 and 290 in
the upper 100 m of the Eastern Atlantic and Southern Ocean
(5). Higher C:S ratios in DOM/POM versus phytoplankton
suggest substantial losses of relatively sulfur-rich compounds.
This presumably includes volatile species like DMS (C:S
=
2),
which accounts for 40% of the atmospheric sulfur
fl
ux from
the ocean (45). In summary, we take our phytoplankton-
derived surface DOS
SPE
endmember to have a
δ
34
S value of
18.6
±
0.6
and a C:S ratio between 153 and 243.
Composition of Abiotic DOS in Sulfidic Porewater.
Porewater
sul
fi
de and polysul
fi
des react abiotically with organic functional
groups to form new C-S bonds in a process called sulfurization
(16). The sul
fi
de derives from dissimilatory sulfate reduction
(DSR), which, unlike the assimilatory pathway, strongly frac-
tionates sulfur isotopes and results in porewater sul
fi
de
δ
34
S
values as low as
45
(46
48). DOS compounds formed by
this pathway are thus also expected to have very low
δ
34
S val-
ues. We analyzed porewater samples from tidal
fl
ats with high
rates of sulfate reduction and organic matter sulfurization: the
mangrove-fringed Caet

e Estuary and the North Sea (49
51).
Because the magnitude of sulfur isotope fractionation by DSR
is generally inversely correlated with the sulfate reduction rate
(52, 53), these samples should provide an upper bound on
porewater sul
fi
de and thus sulfurized DOS
SPE
δ
34
S values.
Our data provide direct constraints on porewater DOS
SPE
sulfur isotope compositions and indicate that sulfurization is a
major process in these sediments. The
δ
34
S values of DOM
SPE
in porewaters ranged from
2.7 to 0.7
,
34
S-depleted by
almost 20
relative to phytoplankton organic sulfur, but rela-
tively
34
S-enriched compared with most porewater H
2
S meas-
urements (46, 54). DOM
SPE
C:S ratios ranged between 18 and
45, with much higher sulfur contents than phytoplankton-
derived DOS in the surface ocean. These values align with both
laboratory studies that incubated DOM
SPE
in sul
fi
dic water,
fi
nding post-sulfurization C:S ratios
15 and previous measure-
ments of North Sea porewaters with a C:S ratio of
27 (13).
Porewater DOM
SPE
δ
13
C values differed in the Caet

e Estuary
(
26.9
±
0.1
) and the North Sea (
23.3
±
0.2
), likely
re
fl
ecting higher terrestrial in
fl
uences in the mangrove-fringed
estuary. Notably, while terrestrial OS is poorly constrained for
δ
34
S ratios, C:S values are generally higher (55); therefore,
while we see in
fl
uences of terrestrial carbon, no such inputs of
terrestrial sulfur are observed. We therefore assume a sul
fi
dic
porewater-derived sedimentary endmember to have a
δ
34
S value
of
2.7 to 0.7
with C:S ratios between 18 and 45.
Limited Evidence for Porewater Sources to DOS.
Mixing calcu-
lations using the
δ
34
S and C:S ratios for the two-endmember
sources described above and the measured
δ
34
S and C:S ratios
of DOM
SPE
indicate that sulfurized porewater sources cannot
contribute more than
20% of the DOS
SPE
in any one sample
from our open-marine dataset, and no more than
8% on
average for the deep-ocean samples (Fig. 4). Given that other
processes could also lead to
δ
34
S depletion (see below) and that
our porewater samples are, if anything, more
34
S-enriched than
sulfurized porewater DOS
SPE
from typical marine sediments
(which have more
34
S-depleted sul
fi
des), this calculation repre-
sents a very conservative maximum estimate (that is, any value
<
20% is plausible, including 0%). Only samples from the
mangrove-fringed Caet

e Estuary were within a range of signi
fi
-
cant contributions (50
80%) from sulfurized organic matter;
however, this contribution appears short-lived, likely due to
rapid (i.e., weeks to months) photochemical oxidation of and
removal from the DOM
SPE
pool in the estuary before reaching
the open ocean (56). Without more data to examine differences
between ocean basins, we are unable to address the long-term
accumulation of sulfurized porewater DOS
SPE
, which is
assumed to persist in the ocean over multiple mixing cycles.
However, the few deep Atlantic data that we do have do not
support this hypothesis, as samples from the Bermuda Atlantic
Time-Series (BATS) are more
34
S-depleted (Figs. 2 and 3; pink
triangles) than those from the (older) deep Paci
fi
c Ocean.
Thus, we can conclude that marine DOS has a dominantly
(
>
92%) biotic origin, that is, presumably produced by micro-
organisms in the sunlit surface ocean.
Sulfurization reactions have also been documented to occur
within anoxic microenvironments in the pelagic ocean, such as
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sinking particles in OMZs, where genomic studies found active
transcription of genes for sulfate reduction (57, 58), and incuba-
tion studies with radioactively labeled sulfur con
fi
rmed that partic-
ulate organic matter sulfurization was occurring (59). It remains
uncertain if this process translates from the particulate to the dis-
solved sulfur pool. Our data from the NE Paci
fi
cOMZ(
n
=
31;
magenta squares, Figs. 2
4) were collected from adjacent stations
to Raven et al. (59) and spanned dissolved O
2
concentrations
from 0 to 250
μ
M. Yet, we observed no signi
fi
cant changes to
either C:S ratios or
δ
34
S values with dissolved oxygen (
SI
Appendix
,Fig.S10
). This suggests that sulfurization reactions in
that anoxic water column minimally or negligibly contribute to
marine DOS; globally signi
fi
cant contributions from other, more
sul
fi
dic water bodies, seem unlikely (60).
The conclusion that porewater
fl
uxes of sulfurized organic
matter do not greatly impact the present marine global DOS
inventory was somewhat unexpected, given previous estimates of
large benthic
fl
uxes (30-200 Tg sulfur yr

1
(13)), which are cal-
culated by dividing DOC
fl
uxes by porewater DOM
SPE
C:S
ratios. There are several potential explanations for this discrep-
ancy, including incorrect estimates of 1) DOM
SPE
C:S ratios,
and/or 2) porewater DOC
fl
uxes. Existing measurements of
porewater DOM
SPE
C:S ratios are highly biased toward pore-
water samples and environments with known sulfurization
if
global average porewater DOM
SPE
C:S ratios are much higher,
then calculated DOS
fl
uxes would decrease. Notably, DOC
fl
uxes are highest in areas with high rates of sulfate reduction
(61), i.e., continental margin sediments (121-233 Tg carbon
yr

1
(62, 63)) and intertidal sediments (106-416 Tg carbon
yr

1
, ref (64). Given that
70% of porewater DOC
fl
ux is
estimated to occur from sediments that have active sulfate reduc-
tion, the bias in porewater DOM
SPE
C:S ratios is likely only
minor. Alternatively, calculated DOC
fl
uxes might be overesti-
mated. Our dataset offers a window to sedimentary DOS/DOC
fl
uxes for comparison: Given a conservative maximum of 20%
(Fig. 4) of the
>
6,700 Tg sulfur DOS inventory that was
initially estimated to derive from porewater
fl
uxes, and an aver-
age lifetime for DOS of
4,000 y (5) assuming that DOS com-
pounds share the same average radiocarbon age as bulk DOC,
the sedimentary
fl
ux of DOS to the global ocean is
<
0.4 Tg sul-
fur yr

1
.PorewaterC:Sratios(
10
50) further imply DOC
fl
uxes of 1.6
7.6 Tg carbon yr

1
, orders of magnitude below
those reported from either intertidal or continental margin sedi-
ments. Although it is possible to invoke a DOC
fl
ux with little
concurrent DOS
fl
ux, such a scenario would require C:S ratios
>
2,500 that are dif
fi
cult to imagine from areas with active sulfur
cycling (and notably, much higher than the highest recorded
value of 1,472 (7)). Either sulfurized DOS suffers extreme pref-
erential loss over DOC or porewaters are orders of magnitude
less signi
fi
cant sources of marine DOM than previously thought.
Finally, if the lifetime of porewater-derived DOS in the water
column is signi
fi
cantly shorter than the average radiocarbon age
of DOC used above (
4,000 y), then sedimentary porewater
fl
uxes could be higher, but this would mean that porewater
DOS does not contribute to the refractory DOM reservoir.
Causes of Spatial
δ
34
S Heterogeneity in DOM.
We next turn to
the observed decrease in
δ
34
S and increase in C:S ratios of
DOM
SPE
with depth (Figs. 2
C
and 3). In shallow (0-150 m
depth) waters, the loss of apparent DOS
SPE
and DOC, increase
in C:S ratios, and near-constant
δ
34
S and
δ
13
C values with
depth can be readily explained by the rapid uptake and/or
remineralization of phytoplankton-derived labile DOS com-
pounds without fractionation. The preferential loss of sulfur
relative to carbon is similar to that observed for nitrogen and
phosphorous over the same depth by other studies (1, 65) and
is unsurprising given that a majority of organic sulfur is present
as diverse bioavailable components like thiols, sulfonates, or thio-
phenes (6, 7). The minimal isotopic fractionation also agrees
with studies of both speci
fi
c degradation reactions (38) and bulk
trophic level effects (66, 67). In contrast, DOS
SPE
in the deep
ocean is lower in concentration (163
±
19 versus 283
±
66 nM),
has higher C:S ratio (252
±
27 versus 213
±
32), and lower
δ
34
S
value (17.1
±
1.1
versus 18.6
±
0.8
; Table 1). Changes in
DOS
SPE
concentration and C:S ratios can be explained as the
continuous degradation of semilabile and semirefractory com-
pounds. The lower
δ
34
S values of deep water DOM
SPE
cannot,
however, be easily explained by a simple degradation model (Fig.
4) because the shift is in the opposite direction of that expected
from a normal isotope effect.
Strong intramolecular heterogeneity in
δ
34
S of DOS
SPE
compounds could potentially yield the observed isotopic pat-
terns if the DOS
SPE
that is removed with depth is signi
fi
cantly
34
S-enriched, relative to the remaining DOS
SPE
.Forexample,
modeling studies and initial data hint that semilabile, reduced
organic sulfur compounds like amino acids are more
34
S-enriched
relative to more recalcitrant, oxidized organic sulfur (26, 55).
However, at present there is little direct compound-speci
fi
csulfur
isotope data to either support or reject this hypothesis. Generation
of DOS compounds via the hydrolysis of sinking particles could
leave POS
34
S-enriched and DOS
SPE
34
S-depleted, but such a sce-
nario would require large isotope fractionations or active turnover
of a large proportion of the deep DOS pool. Finally, addition of
terrestrial DOS (generally high in C:S and lower in
δ
34
S) to the
deep ocean could explain lower
δ
34
Swithdepthbutisinconsis-
tent with our nearly invariant
δ
13
Cvalues(Fig.3
C
).
Alternatively, deep-ocean DOS
SPE
could simply be
34
S-depleted
due to mixing with porewater sulfurized compounds, as discussed
above. While this should add S-rich compounds that lower the
Fig. 4.
DOM
SPE
samples plotted in the same coordinate space and color
scheme as Fig. 1
B
, with C:S molar ratios on the
x
axis and
δ
34
S values on
the
y
axis. A linear mixing model is superimposed in the white- to blue-
colored polygon, with dashed lines at 10% intervals. Endmembers for the
mixing space were inferred from marine surface (
<
50 m) extracts and pore-
water samples and are detailed in the discussion. Marine samples have, on
average,
8% DOS contributions from porewater sources and at maximum
20% (two samples). We hypothesize that heterogeneity in
δ
34
Svaluesand
C:S ratios is a combination of both mixing from porewater sources that low-
ers
δ
34
S values, and organic sulfur removal without fractionation that
increases C:S ratios (gray arrows). VCDT, Vienna Canyon Diablo Troilite.
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https://doi.org/10.1073/pnas.2209152119
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C:S ratios, the large
δ
34
S contrast between surface and porewater
DOS
SPE
means that the isotopic composition is much more sensi-
tive to this addition than the elemental ratio (Fig. 4). If this mech-
anistic explanation is correct, the trends of decreasing apparent
DOS, increasing C:S ratios, and decreasing
δ
34
Svaluesobserved
in intermediate-depth waters can be understood as the superposi-
tion of two processes (Fig. 4, gray arrows). Thus, we hypothesize
that C:S ratios of DOM
SPE
increase with depth (up to
750 m)
due to mixing with older water masses and concurrent slow degra-
dation, but without appreciable isotopic fractionation. Meanwhile,
the
δ
34
S of deep DOS
SPE
is lower due to the addition of small
amounts of
34
S-depleted sulfurized DOM
SPE
from porewaters and
possibly other sources.
Conclusions.
We developed an improved (
10x more sensitive
for sulfur) analytical measurement for marine DOM
SPE
,
enabling concurrent measurements of
δ
34
Svalues,
δ
13
Cvalues,
and C:S ratios on
350
μ
gDOM
SPE
. We used this technique
to produce a global survey of marine DOM
SPE
δ
34
S values
and show that abiotically sulfurized organic matter from sul
fi
-
dic porewater is on average
<
8% of the marine DOS
SPE
pool.
As this is a conservative upper bound, we conclude that sulfu-
rized porewater DOS is only a small component of the oceanic
DOM inventory. The accumulation of refractory, sulfurized
porewater is therefore not a main process that could explain
the old radiocarbon ages of oceanic DOM
SPE
.Instead,DOS
apparently derives mostly from biological assimilation of sul-
fate in the sunlit surface ocean. Trends of increasing C:S ratios
and decreasing
δ
34
S values with depth could re
fl
ect the contin-
uous removal of surface-derived DOM
SPE
superimposed on a
background of this small inventory of sulfurized DOS
SPE
.
Materials and Methods
Sample Collection.
DOM
SPE
samples were collected between 2016 and 2021
on 10 cruises (see
SI Appendix
for details), including the BATS and the Hawaii
Ocean Time-Series, that covered the following regions: N Paci
fi
c Gyre, N Atlantic
Gyre, S Paci
fi
c Gyre, NE Paci
fi
c, NE Paci
fi
cShelf,NEPaci
fi
c OMZ, San Pedro Basin
(coastal California), and the Caet

e Estuary (Amazonian mangroves). Porewater
DOM
SPE
samples were collected from the intertidal sediments of the mangrove-
fringed Caet

e Estuary, south of the Amazon Estuary in North Brazil, and a North
Sea intertidal
fl
at in Germany. For marine samples, conductivity, temperature,
and density casts for physical parameters (i.e., dissolved oxygen, salinity,
fl
uores-
cence, temperature) were taken at each station and can be found in the
SI
Appendix
(
SI Appendix
,Figs.S1
S7
). Seawater (
5
20 L samples) was collected
from Niskin bottles into acid-washed polyethylene containers and
fi
ltered
through a 0.80/0.45
μ
mcapsule
fi
lter (AcroPak 500) prior to acidi
fi
cation to pH
2 with reagent grade 12 N hydrochloric acid. DOC concentrations were measured
prior to SPE via high-temperature combustion on a Shimadzu Total Organic Car-
bon Analyzer (Shimadzu Corp). Nutrients (nitrate, phosphate, and silicate) were
measured via colorimetry on an AutoAnalyzer II (Seal Analytical; see
SI Appendix
for station-speci
fi
c methods details and references).
DOM
SPE
Isolation.
DOM
SPE
was concentrated using SPE with Bond Elute PPL
cartridges (Agilent; 1 g, 6 mL size) following Dittmar et al. (28). DOM
SPE
samples
were eluted in GC-grade methanol (28). Extracts were dried under a stream
of N
2
gas and transferred to 2 mL GC vials and then to 150
μ
L glass inserts.
Aliquots corresponding to
4.5
μ
gsulfur(
350
μ
g DOC) were transferred in
methanol from 2 mL GC vials into smooth-walled tin EA capsules (6
×
2.9 mm,
OEA Laboratories). Methanol was evaporated at room temperature (
2h)prior
to folding.
EA-IRMS Measurements.
Tin capsules containing dried DOM
SPE
were folded
closed, loaded into an autosampler, and then combusted and analyzed in a
Thermo Scienti
fi
c EA IsoLink IRMS System for determination of C:S molar ratios,
δ
34
S values, and
δ
13
C values. The system comprised a Flash combustion EA
coupled to a Delta V Plus IRMS via a ConFlo IV Universal Interface. Carbon and
sulfur isotope analysis and data processing followed a previously published
method (26). Due to the high C:S molar ratios of DOM
SPE
,CO
2
was diluted by
88.4% following combustion via the ConFlo. Urea standards were run at the
same settings to account for any possible fractionation of
13
Cbythisdilution.
Sulfur isotope and concentration standards included a methionine working
standard, seawater sulfate, and silver sul
fi
de reference materials (IAEA S1, S2,
S3). Additionally, a working standard of DOM
SPE
extracted in a large batch
(
200 L) from the Scripps Institution of Oceanography (SIO) pier was run in at
least triplicate with each sample set. Sample
δ
34
S values were corrected for lin-
earity (peak height) effects and then calibrated to IAEA reference materials. sul-
fur content (
<
0.10
μ
g sulfur) and
δ
34
Svalues(
8
) of tin capsules were also
measured by EA-IRMS and used to correct subsequent analyses for the blank
contribution (68).
δ
34
S values are reported as permil (
) variations relative to
the Vienna Canyon Diablo Troilite reference frame, while
δ
13
Cvaluesare
reported relative to Vienna Pee Dee Belemnite. C:S ratios were obtained by
dividing corrected carbon and sulfur amounts (molar ratio), as calculated from
EA peak areas. Extracts supplied by collaborators were often limited by sample
size to single or duplicate analyses, so we could not estimate precision directly
for each sample. Instead, uncertainties in isotopic compositions and C:S ratios
for samples are reported using the SD of our DOM
SPE
SIO pier standard
measurements, divided by the square root of sample replicates analyzed. These
SEs (1
σ
)were
0.2
for
δ
34
Svaluesand
δ
13
Cvaluesand
6forC:Sratios.
DOS
SPE
concentrations were calculated as the product of measured total DOC
concentration and DOM
SPE
C:S ratio, and we therefore refer to DOS
SPE
concen-
trations as
apparent
throughout.
Sulfate Carryover.
We also considered the carryover of seawater sulfate in
DOM
SPE
extracts as a potential source of systematic error. Blank extractions
using 28 mM Na
2
SO
4
in deionized water on the PPL SPE cartridges showed
no measurable sulfur above the capsule blank (0.10
μ
g sulfur) via EA-IRMS.
Taking this as the upper limit for sulfate blank, and assuming a
δ
34
S value
of
+
21
(36), we calculated a worst-case error (for a sample with just 1
μ
g
sulfur and measured
δ
34
Sof15
)of0.6
. For a sulfate blank half that
size, and a more typical sample of 4
μ
g sulfur and
δ
34
S
=
17.5
, the effect
would be just 0.05
. There was no correlation between SO
2
peak size in the
EA and measured
δ
34
S(
R
2
=
0.0004), so we conclude that sulfate contami-
nation is very unlikely to have caused either the relative
34
S enrichments or
the depth-related trends in our dataset. DOM
SPE
samples with peak sizes that
corresponded to
<
1
μ
g sulfur were not reported to further minimize any
possibility of blank-related artifacts.
Data, Materials, and Software Availability.
All study data are included in
the article and/or supporting information.
ACKNOWLEDGMENTS.
We thank the crew, administrative teams, and science
parties of the
R/V Atlantic Explorer
and the
R/V Kilo Moana
for their assistance
during the Bermuda Atlantic Time-Series and Hawaii Ocean Time-Series cruises,
especially Rod Johnson and Carolina Funkey. We thank Daniela Osorio Rodriguez
and Sijia Dong for their assistance in sample collection aboard the
R/V Sally Ride
andJess Adkins from Caltech. We thank Troy Gunderson from the San Pedro
Ocean Time-Series and the crew of the
R/V Yellow
fi
n.
We acknowledge Mike
Beman for inviting our participation on cruises that provided the NE Paci
fi
cOMZ
samples and Ken Smith for supporting the acquisition of the Station M NE Paci
fi
c
samples. We are grateful to members and technicians in the Aluwihare Lab at
Scripps Institution of Oceanography, especially Brandon Stephens, Irina Koester,
and Tran Nguyen. We acknowledge Usha Lingappa for drafting Figure 1. We
thank colleagues for early reviews and conversations about the manuscript,
including Tony Wang, Hannah Dion-Kirschner, Morgan Raven, and Ted Present,
and other members of the Adkins and Sessions Labs at Caltech. We thank
University of California Santa Cruz Professor Matthew McCarthy for early conversa-
tions and support for the project. Color-blind-friendly palettes were generated
from Paul Tol
s online resource. Funding for this work was provided by NSF
OCE (Division of Ocean Sciences) Grant 2023676 to A.L.S. and A.A.P.; M.S. and
T.D. acknowledge funding by the DFG-FAPERJ (German Research Foundation)
cooperative project (DI 842/6-1) and within the Cluster of Excellence EXC
2077
The Ocean Floor - Earth
s Uncharted Interface
(DFG Project number
PNAS
2022 Vol. 119 No. 41 e2209152119
https://doi.org/10.1073/pnas.2209152119
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