Subscriber access provided by Columbia University Libraries
Environmental Processes
Identification of steps in the pathway of arsenosugar biosynthesis Xi-Mei Xue, Jun Ye, Georg Raber, Barry P. Rosen, Kevin A. Francesconi, Chan Xiong, Zhe Zhu, Christopher Rensing, and Yong-Guan Zhu Environ. Sci. Technol., Just Accepted Manuscript • DOI: 10.1021/acs.est.8b04389 • Publication Date (Web): 10 Dec 2018 Downloaded from http://pubs.acs.org on December 12, 2018
Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.
is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.
Page 1 of 33
Environmental Science & Technology
1
Identification of steps in the pathway of arsenosugar
2
biosynthesis
3
Xi-Mei Xue,1 Jun Ye,1 Georg Raber,2 Barry P. Rosen,3 Kevin Francesconi,2 Chan
4
Xiong,2 Zhe Zhu,4 Christopher Rensing,5 Yong-Guan Zhu 1,6*
5 6
1
7
Chinese Academy of Sciences, Xiamen 361021, China
8
2 Institute
9
3
Key Laboratory of Urban Environment and Health, Institute of Urban Environment,
of Chemistry, NAWI Graz, University of Graz, Graz 8010, Austria
Department of Cellular Biology and Pharmacology, Herbert Wertheim College of
10
Medicine, Florida International University, Miami, FL 33199
11
4
12
Engineering, University of Nottingham, Ningbo 315100, China
13
5
14
Fuzhou 350002, China
15
6
16
Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China
Department of Chemical and Environmental Engineering, Faculty of Science and
College of Resources and Environment, Fujian Agriculture and Forestry University,
State Key Laboratory of Urban and Regional Ecology, Research Center for Eco-
17 18 19
*Address Correspondence to Yong-Guan Zhu,
20
Address: Institute of Urban Environment, Chinese Academy of Sciences, 1799 Jimei
21
Road, Xiamen 361021, China
1
ACS Paragon Plus Environment
Environmental Science & Technology
22
Phone number: +86(0)592 6190997
23
Fax number: +86(0)592 6190977
24
Email address:
[email protected] Page 2 of 33
25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60 61 62 2
ACS Paragon Plus Environment
Page 3 of 33
Environmental Science & Technology
63 64
Abstract
65
Arsenosugars are arsenic-containing ribosides that play a substantial role in arsenic
66
biogeochemical cycles. Arsenosugars were identified more than thirty years ago, and
67
yet their mechanism of biosynthesis remains unknown. In this study we report
68
identification of the arsS gene from the cyanobacterium Synechocystis sp. PCC 6803
69
and show that it is involved in arsenosugar biosynthesis. In the Synechocystis sp. PCC
70
6803 ars operon, arsS is adjacent to the arsM gene that encodes an As(III) S-
71
adenosylmethionine (SAM) methyltransferase. The gene product, ArsS, contains a
72
characteristic CX3CX2C motif which is typical for the radical SAM superfamily. The
73
function of ArsS was identified from a combination of arsS disruption in Synechocystis
74
sp. PCC 6803 and heterologous expression of arsM and arsS in Escherichia coli. Both
75
genes are necessary, indicating a multi-step pathway of arsenosugar biosynthesis. In
76
addition, we demonstrate that ArsS orthologs from three other freshwater cyanobacteria
77
and one picocyanobacterium are involved in arsenosugar biosynthesis in those
78
microbes. This study represents the identification of the first two steps in the pathway
79
of arsenosugar biosynthesis. Our discovery expands the catalytic repertoire of the
80
diverse radical SAM enzyme superfamily and provides a basis for studying the
81
biogeochemistry of complex organoarsenicals.
82 83 84 85 86 87 3
ACS Paragon Plus Environment
Environmental Science & Technology
Page 4 of 33
88 89
Introduction
90
Arsenoribosides, commonly known as arsenosugars, were first isolated from the brown
91
kelp, Ecklonia radiata, and chemically identified in 1981.1 More than 20 arsenosugars
92
consisting of dimethylated arsenosugars, dimethylated thio-arsenosugars, and
93
trimethylated arsenosugars are known to occur primarily in marine organisms but also
94
in some terrestrial organisms (Figure S1).2, 3 They are natural constituents of marine
95
organisms and not toxic to marine plants or animals. Thus the synthesis of arsenosguars
96
represents a mechanism of arsenic detoxification. Arsenosugars also appear to play a
97
central role in the pathway of arsenic biotransformation in marine systems. First, they
98
are likely intermediates in the biosynthesis of the osmolyte arsenobetaine, which is the
99
dominant arsenical in marine organisms and is nontoxic in humans.1 Edmonds &
100
Francesconi proposed that arsenosugars can be converted to arsenocholine by the
101
cleavage of the C3-C4 bond of the sugar residue and methylation of the arsenic atom.
102
Further oxidation at the C-4 of the sugar residue results in the production of
103
arsenobetaine.1, 4 The enzymes for glycine betaine synthesis (GbsB/GbsA) have been
104
shown to be involved in the biosynthesis of arsenobetaine from arsenocholine.5 Second,
105
arsenosugars are also the likely precursors of arsenosugar phospholipids,6, 7 which may
106
be components of the algal cell membrane.8 Incorporation of arsenolipids increases
107
under low phosphate conditions and may represent a phosphate-sparing mechanism
108
under those conditions.9
109
Dimethylated arsenosugars consist of a dimethylarsinoyl moiety, in which 4
ACS Paragon Plus Environment
Page 5 of 33
Environmental Science & Technology
110
pentavalent arsenic is bound to one oxygen, to two methyl groups and to a 5'-
111
deoxyriboside (Figure S1). The dimethylated arsenosugars differ from one another only
112
in structure of the side chains at the 5'-deoxyriboside C1 position. A proposed pathway
113
for arsenic transformation in the marine environment suggests that SAM is the source
114
of both the methyl groups and the 5'-deoxyribose group of arsenosugars.4
115
In this study, the arsS (hereafter referred to as SsarsS) and arsM (hereafter referred
116
to as SsarsM) genes from Synechocystis were disrupted to examine their function in
117
arsenosugar biosynthesis. Either disruption mutant was unable to synthesize
118
arsenosugars, indicating that both genes are involved in the biosynthetic pathway. The
119
SsarsM and SsarsS genes were heterologously expressed in E. coli. Cells expressing
120
SsarsM could synthesize dimethylarsenate but not arsenosugar, while cells expressing
121
both genes produced dimethylarsenoriboside derivatives. Our results elucidate the first
122
two steps in the pathway of arsenosugar biosynthesis. The first step is addition of
123
methyl groups from SAM to As(III) by the SAM methyltranserase SsArsM. The second
124
step is addition of the deoxyribose moiety by the radical SAM enzyme SsArsS. This
125
study demonstrates the first two steps in the pathway of arsenosugars and puts the
126
synthesis of complex organoarsenical on a firm biochemical basis.
127
Materials and Methods
128
Strains and plasmids
129
Unless otherwise indicated, E. coli was cultured aerobically in Luria − Bertani (LB)
130
medium at 37°C containing 100 μg mL-1 ampicillin, 50 μg mL-1 kanamycin, or 30 μg
131
mL-1 chloramphenicol, as required. E. coli AW3110 (DE3) (ΔarsRBC) 10 was used for 5
ACS Paragon Plus Environment
Environmental Science & Technology
Page 6 of 33
132
resistance assays. Plasmids pET-28a-SsarsS, pET-22b-SsarsS, pETDuet-SsarsS or/and
133
pET-28a-SsarsM were transformed into E. coli BL21 (DE3) or Rosetta (DE3) for
134
expression of SsArsM and SsArsS and for production of arsenical products. All strains
135
and plasmids are shown in Table S1.
136
Disruption of SsarsS and SsarsM in Synechocystis sp. PCC 6803
137
A mutant of Synechocystis with a disruption of the SsarsM gene has been described.11
138
Mutagenesis of SsarsS (Synechocystis ΔarsS) was performed (Figure S3A) as follows:
139
(a) SsarsS was amplified with primers SsarsSF and SsarsSR (Table S2); (b) the purified
140
SsarsS fragment after PCR was cloned into pMD19T simple vector (TaKaRa, Dalian,
141
China) to yield plasmid pMD-arsS; (c) a kanamycin resistance (KanR) cassette cut from
142
pKW1188 12 with EcoRI was inserted into the EcoRV site of pMD-arsS to create gene-
143
disruption KanR-insertion cassette, pMDarsSkan; (d) the plasmid was transformed into
144
Synechocystis WT according to a previous description;13 (e) Synechocystis ΔarsS was
145
obtained after three serial isolation of single colonies on BG11 agar plates containing
146
30 μg mL-1 kanamycin; (f) PCR with diagnostic primers (Table S2) was used to confirm
147
that the SsarsS gene was completely replaced. Synechocystis ΔarsS was cultivated in
148
100 mL of BG11 medium supplemented with 50 μg mL-1 kanamycin at 30oC.
149
Complementation of SsarsS in Synechocystis sp. PCC 6803
150
Complementation of the Synechocystis ΔarsS mutant (Synechocystis ΔarsS::arsS)
151
(Figure S3A) was achieved by “knock-in” of intact SsarsS containing the rbcL2A
152
promoter with a chloramphenicol resistance (CamR) gene. An intact SsarsS was
153
amplified using primers arsSc-F and arsSc-R (Table S2). The rbcL2A promoter, PrbcL2A, 6
ACS Paragon Plus Environment
Page 7 of 33
Environmental Science & Technology
154
was produced with primers FP_CO2noEcoRI and RP_BBRBS.14 The above PCR
155
products were cloned into pMD19T simple vector to produce plasmid pMarsSc and
156
pMpromoter respectively, sequenced to confirm the integrity of the cloned flanking
157
DNA. The plasmid containing SsarsS with the promoter was constructed by inserting
158
PrbcL2A into the EcoRI and SpeI sites of the plasmid pMarsSc. A CamR gene amplified
159
from pACYCDuet-1 (Novagen, Madison, WI) using primers cmr-F and cmr-R was
160
digested with NheI and HindIII, cloned into the upstream of PrbcL2A. Finally, the
161
fragment consisting of a CamR gene, PrbcL2A, and SsarsS was linked with a plasmid
162
pKW1188 without KanR by T4 DNA ligase (MBI Fermentas, Flamborough, ON,
163
Canada) to prepare plasmid pKcmrparsS. This plasmid was used to transform
164
Synechocystis ΔarsS, and the above fragment was inserted into the neutral site slr0168.
165
In all cases, Synechocystis ΔarsS::arsS was selected on BG11 agar plates containing 30
166
μg mL-1 kanamycin and 15 μg mL-1 chloramphenicol. PCR amplification with the
167
genomic DNA from Synechocystis ΔarsS::arsS as templates and the primers gp267-9
168
and gp267-10
169
Synechocystis ΔarsS::arsS (Figure S3B). The resulting Synechocystis ΔarsS::arsS
170
strain was cultivated in 100 mL of BG11 medium with 50 μg mL-1 kanamycin and 30
171
μg mL-1 chloramphenicol.
172
As(III) transformation assays
173
After one or two weeks of continuous illumination culture, 50 or 100 mL of
174
cyanobacteria (Synechocystis WT, Synechocystis ΔarsS, and Synechocystis ΔarsS::arsS)
175
were collected by centrifuging and washing twice with cold MES buffer. 16 About 20
15
was carried out to confirm that an intact SsarsS was present in
7
ACS Paragon Plus Environment
Environmental Science & Technology
Page 8 of 33
176
mg of lyophilized cells were added into 1.5 mL Eppendorf tubes with 1 mL of a mixture
177
of CH3OH(MeOH)/H2O (1+1, v/v). The cells were extracted by placing the tubes in an
178
ultrasonic bath for 20 minutes followed by rotating on a rotary wheel overnight. The
179
extracts were centrifuged for 10 min at 13520 g. The supernatant was purged with N2
180
to remove MeOH, and then filtered through a 0.22 µm membrane filter into 1 mL
181
crimp/snap polypropylene vials (Agilent Technologies, Palo Alto, CA, USA) for
182
arsenic species analysis.
183
The transformation of As(III) under the control of ArsS or/and ArsM was assayed
184
in vivo. The assays were performed with Rosetta bearing pET-28a-SsarsM, Rosetta
185
bearing pETDuet-SsarsS, Rosetta bearing empty pETDuet-1 and pET-28a, or Rosetta
186
bearing pET-28a-SsarsM and pETDuet-SsarsS. Cells were grown overnight at 37oC
187
with shaking (200 rpm) in LB medium containing corresponding antibiotic, diluted
188
100-fold into 5 mL of fresh LB medium. After incubation at an OD
189
carried out with 0.5 mM IPTG for 3 h, cells were treated with 1 µM, 10 µM, 100 µM,
190
1 mM or 3 µM of either As(III) or As(V). At the indicated times, the cells and culture
191
medium were collected.
192
Arsenic species analysis
193
High performance liquid chromatography - inductively coupled plasma mass
194
spectrometry (HPLC-ICP-MS) measurements on arsenic species were performed using
195
an Agilent 7500cx ICP-MS (Agilent Technologies, California, USA) for element
196
detection coupled with an Agilent 1200 HPLC system. Anion-exchange
197
chromatography separation was performed using PRP-X100 with a guard column
600 nm
of 0.5 was
8
ACS Paragon Plus Environment
Page 9 of 33
Environmental Science & Technology
198
(Hamilton, Reno, NV, USA). A Shiseido CAPCELL PAK C18 MGII (Shiseido, Tokyo)
199
with a matching guard column was employed for ion-pair reversed-phase
200
chromatographic separation. All chromatography parameters are shown in Table S3.
201
Unknown arsenic compounds were identified using HPLC-ICP-MS/electrospray
202
ionization tandem mass spectrometry (ESI-MS-MS, Agilent 6460, Agilent
203
Technologies, Waldbronn, Germany), and higher solution accurate mass (HPLC-ESI-
204
HR-MS-MS) measurements which were performed in positive mode on a Q-Exactive
205
Hybrid Quadrupole-Orbitrap MS after arsenic species were separated on a Dionex
206
Ultimate 3000 series instrument (Thermo Fischer Scientific, Erlangen, Germany).
207
Results
208
The arsS gene is involved in arsenosugar biosynthesis.
209
Our search for candidate genes involved in arsenosugar biosynthesis was guided by the
210
hypothesis that oxidation of DMAs(III) by addition of the deoxyadenosyl radical group
211
from SAM and enzymatic hydrolytic removal of adenine would result in the formation
212
of arsenosugars in marine algae.4 Synechocystis produces two species of arsenosugars,
213
indicating that this microbe has the biosynthetic enzymes for arsenosugar synthesis.11,
214
17
215
methyltransferase in Synechocystis.16 The SsarsM gene is adjacent to two other open
216
reading frames, slr0304 and slr0305 (Figure 1). A protein BLAST search using
217
SLR0304, which we termed as SsArsS, as a query revealed the presence of regions
218
conserved in the radical SAM superfamily, in particular iron-sulfur cluster (FeS) and
219
SAM binding sites. The SsarsM and SsarsS genes comprise an ars operon (Figure S2).
We previously identified the enzyme SsArsM as an As(III) S-adenosylmethionine
9
ACS Paragon Plus Environment
Environmental Science & Technology
Page 10 of 33
220
SLR0305 is related to the family of SNARE-associated Golgi membrane proteins, and
221
this gene is co-transcribed with the other two genes, but it is not clear if it has an arsenic-
222
related function. Nostoc sp. PCC 7120, which also produces arsenosugars,18 has a
223
putative arsMarsS operon. The Nostoc operon lacks a gene corresponding to SLR0305,
224
indicating that the latter does not have an arsenic-related function. We hypothesize from
225
the linkage of the arsM and arsS genes in more than one arsenosugar producers that
226
these two genes have related functions encoding a biosynthetic pathway for arsenosugar
227
biosynthesis (Figure 1). We previously demonstrated that a strain in which SsarsM was
228
disrupted cannot synthesize arsenosugars, supporting our hypothesis that DMAs
229
production by ArsM is the first step in arsenosugar synthesis.11
230
We hypothesize that ArsS catalyzes the second step in arsenosugar biosynthesis by
231
transfer of a deoxyadenosyl group from SAM to DMAs. This could be the first
232
committed step in the biosynthetic pathway because the product of ArsM, DMAs can
233
have other biosynthetic fates. ArsS is a member of the radical SAM superfamily.
234
Radical SAM enzymes are characterized by a CX3CX2C motif that provides co-
235
ordinations for binding of a unique four iron-four sulfur ([4Fe-4S]) cluster, although
236
the spacing of the cysteines in this motif can vary.19 Both the alignment of SsArsS with
237
those of functionally characterized radical SAM enzymes and construction of a
238
molecular phylogenetic tree indicate that SsArsS is closely related to MoaA (Figure S4),
239
which harbors an N-terminal [4Fe-4S] cluster involved in a 5’-deoxyadenosyl radical
240
generation and a C-terminal [4Fe-4S] cluster involved in substrate binding and/or
241
activation in conversion of 5’-GTP to an oxygen-sensitive tetrahydropyranopterin.20 10
ACS Paragon Plus Environment
Page 11 of 33
Environmental Science & Technology
242
We have used UV/visible spectroscopy to examine a visible absorption band at 410 nm
243
for the [4Fe-4S]2+ protein (Figure S5).21
244
SsArsS is involved in the biosynthesis of arsenosugars
245
To examine the involvement of ArsS in arsenosugar biosynthesis, we disrupted the
246
SsarsS gene of Synechocystis by inserting a KanR cassette inside SsarsS. We evaluated
247
the ability of the parental wild type strains and its derivatives to grow. No difference in
248
growth rate in the absence of As(III) was observed among wild type, Synechocystis
249
ΔarsS and Synechocystis ΔarsS::arsS strains (Figure S3C), indicating that ArsS is not
250
required for viability under these growth conditions. The production of arsenosugars by
251
wild type and mutant strains in medium containing different arsenic species was
252
determined by HPLC-ICP-MS analysis. Consistent with earlier studies,11, 17 wild type
253
Synechocystis exposed to As(III) produces As(V) as the predominant soluble arsenic
254
species, and small amounts of MAs(V), DMAs(V) and arsenosugars (Figure 2a). Again,
255
it is not possible to deduce whether the products of the reaction were trivalent species
256
that oxidized in air to their pentavalent forms. In addition, wild type Synechocystis
257
transforms MAs(V) or DMAs(V) into arsenosugars (Figure 2 c, e). Synechocystis ΔarsS
258
was unable to generate arsenosugars in medium containing either As(III) or pentavalent
259
methylated arsenic species (Figure 2b, d, f). The Synechocystis ΔarsS::arsS strain
260
regained the ability to produce arsenosugars (Figure S3D). These results clearly showed
261
that SsArsS is likely involved in arsenosugar biosynthesis.
262
Heterologous expression of SsarsS and SsarsM
263
To demonstrate the linked function of SsarsM and SsarsS in arsenosugar production, 11
ACS Paragon Plus Environment
Environmental Science & Technology
Page 12 of 33
264
the SsarsS and SsarsM genes were heterologously expressed alone or in combination
265
in E. coli Rosetta (DE3), which has neither in its genome (Figure 3A and Figure S6A).
266
Heterologous expression of arsM genes in E. coli strain AW3110 (DE3), in which the
267
chromosomal ars operon was deleted 10 has been shown to confer As(III) resistance.22,
268
23
269
resistance to As(III) (Figure S7). Surprisingly, expression of SsarsS alone conferred
270
As(III) resistance (Figure S7). SsArsS has 11 cysteine residues that might bind
271
sufficient As(III) to confer moderate resistance or some free radicals generated by the
272
process of As(III) oxidation to As(V) by SsArsS when the gene is expressed at high
273
levels.
Similarly, expression of SsarsM alone in E. coli strain AW3110 (DE3) conferred
274
ICP-MS was also used to quantify total arsenic in E. coli Rosetta cells (Figure S8A)
275
treated with 0.5 mM IPTG and 1 μM As(III) for 20 h. Rosetta cells expressing SsarsS
276
accumulated the most arsenic, up to 83 mg kg-1. Cells expressing SsarsM alone
277
accumulated less (44 mg As kg-1), which was similar to cells expressing both genes (39
278
mg As kg-1). The arsenic content of cells expressing both SsarsM and SsarsS peaked
279
after exposure for 3 h, and subsequently declined, suggesting that they expelled their
280
arsenic compounds from the cells (Figure S8B).
281
The arsenic species in medium were analyzed by HPLC-ICP-MS after E. coli
282
Rosetta cells were exposed to 3 μM As(III) for 12 h. No arsenosugars were identified
283
in Rosetta expressing both SsarsM and SsarsS. The major arsenic species found in
284
medium of Rosetta cells expressing both SsarsM and SsarsS or SsarsM alone was
285
DMAs(V) (Figure 3). As(III) dominated in medium of Rosetta expressing SsarsS alone. 12
ACS Paragon Plus Environment
Page 13 of 33
Environmental Science & Technology
286
Comparative analysis of the aqueous fraction of Rosetta cells expressing SsarsM alone,
287
or SsarsS alone, or both SsarsM and SsarsS revealed that Rosetta cells expressing both
288
SsarsM and SsarsS generated unknown arsenic compounds (Figure 3B), indicating that
289
biosynthesis of these species requires the concerted action of ArsM and ArsS. These
290
unknown compounds were identified by HPLC-ESI-HR-MS-MS after Rosetta cells
291
expressing both SsarsM and SsarsS were incubated with 3 μM arsenic for 72 h, and
292
they were a group of dimethylarsinoyl-hydroxycarboxylic acids (DMA-HA, Figure S9
293
and S10).
294
None of the unknown arsenic compounds that cells expressing SsarsM and SsarsS
295
together produced eluted at the same position as 5'-deoxy-5'-dimethylarsinoyl-
296
adenosine, which is a predicted intermediate in the arsenosugar synthesis pathway
297
proposed by Edmonds and Francesconi 4 (Table 1). The results of HPLC-ICP-MS/ESI-
298
MS-MS and HPLC-ESI-HR-MS-MS measurements suggested the presence of
299
additional dimethylarsinoyl-hydroxycarboxylic acids such as 3′-dimethylarsinoyl-2′-
300
hydroxypropionic
301
dimethylarsinoyl-2′-hydroxypentanonic acid and 5′-dimethylarsinoyl-2′, 3′, 4′-
302
trihydroxypentanonic acid, as well as two unidentified arsenic compounds which could
303
not be characterized due to low concentrations (Table 1 and Figure S10). A compound
304
with the predicted composition C7H16O5As (m/z 255.02079) was also detected by
305
HPLC-ESI-HR-MS-MS, but the structure could not be confirmed (Figure S10). Figure
306
S10 shows that in addition to the four dimethylarsinoyl-hydroxycarboxylic acids
307
(except 5-dimethylarsinoyl-2 ′ -hydroxypentanonic acid) identified in incubation
acid,
4′-dimethylarsinoyl-2′,
3′-dihydroxybutyric
acid,
5′-
13
ACS Paragon Plus Environment
Environmental Science & Technology
Page 14 of 33
308
medium, cells expressing SsarsM and SsarsS also contained the four corresponding
309
thio-arsenic compounds. There are several possible reasons why dimethylarsinoyl-
310
hydroxycarboxylic acids were produced rather than 5'-deoxy-5'-dimethylarsinoyl-
311
adenosine in E. coli expressing both SsarsM and SsarsS. First, there might be additional
312
steps catalyzed by as-yet unidentified Synechocystis enzymes not present in E. coli.
313
Second, most of the ArsS produced in E. coli may be partly active, consistent with our
314
observation that purified ArsS is extremely oxygen sensitive. Oxygen induces the
315
switch from [4Fe-4S]+ to [4Fe-4S]2+, [3Fe-4S]2+, or [2Fe-2S]2+ with loss of biological
316
activity. A future goal is to express the genes under anaerobic growth conditions.
317
The roles of cysteine residues in SsarsS
318
Assuming that the production of dimethylarsinoyl-hydroxycarboxylic acids reflects a
319
partial activity of SsArsS, the role of cysteine residues in that activity was examined.
320
Thiol chemistry plays an important role in arsenic metabolism
321
processes
322
proteins. Each of the eleven cysteine residues in SsArsS protein, Cys41, Cys45, Cys48,
323
Cys65, Cys129, Cys142, Cys264, Cys279, Cys320, Cys323, Cys331, were individually changed
324
to serine residues. Single mutants in SsarsS and SsarsM were co-transformed into E.
325
coli strain Rosetta (DE3) which were treated with As(III) (Figure S11). Three mutant
326
proteins, C65S, C129S, C142S, were able to produce unknown organoarsenicals. Cells
327
expressing the other eight mutants and SsarsM lost the ability to produce the
328
unidentified arsenic compounds. The three cysteine residues, Cys41, Cys45, Cys48, in the
329
N-terminal region of SsArsS correspond to the canonical radical SAM cysteine motif
26
24, 25
and transport
through formation of metalloid-sulfur bonds between arsenic and related
14
ACS Paragon Plus Environment
Page 15 of 33
Environmental Science & Technology
330
CX3CX2C, while other three cysteine residues, Cys320, Cys323, Cys331, in the C-terminal
331
region of SsArsS are conserved among ArsSs.
332
The function of microbial arsS genes in arsenic transformation.
333
We identified putative ArsS orthologs with eight conserved cysteine residues and a
334
radical SAM domain in other microbes. Genes encoding for ArsS from four other
335
cyanobacteria and one eukaryotic green alga (Table S4) were co-expressed with SsarsM
336
in E. coli. The cyanobacteria Nostoc sp. PCC 7120
337
Chlorella
338
was identified in the picocyanobacterium P. marinus str. MIT 9313,29 although it has
339
not been demonstrated if this species generates arsenosugars. Cyanobacteria A.
340
platensis NIES-39 and S. elongatus PCC 6301, which have genes encoding ArsS
341
orthologs were chosen as representative cyanobacteria. Arsenic transformation was
342
analyzed in cells of E. coli co-expressing genes for orthologs of SsArsS in pETDuet-
343
arsS together with pET-28a-SsarsM. E. coli co-expressing SsarsM and NsarsS from
344
Nostoc sp. PCC 7120 produced the dimethylarsinoyl-hydroxycarboxylic acids observed
345
in E. coli expressing SsarsM and SsarsS (Figure 4 and Figure S6B). ArsSs from
346
cyanobacteria A. platensis NIES-39, S. elongatus PCC 6301, and P. marinus str. MIT
347
9313, organisms that have not been previously reported to generate arsenosugars, also
348
synthesized dimethylarsinoyl-hydroxycarboxylic acids (Figure 4). Only SsArsM and
349
CvArsS from the eukaryotic algae C. variabilis did not synthesize 5'-
350
dimethylarsenoriboside derivatives when co-expressed in E. coli. The reason for this
351
negative result is unknown, but perhaps CvArsS, which undergoes extensive post-
28
18, 27
and the eukaryotic alga
have been reported to produce arsenosugars. Recently, a putative ArsM
15
ACS Paragon Plus Environment
Environmental Science & Technology
Page 16 of 33
352
translational processing in C. variabilis, is not modified to an active enzyme in E. coli.,
353
or perhaps those gene products did not fold properly in E. coli.
354
Discussion
355
The most abundant arsenic compounds identified in marine algae are arsenosugars.30
356
Prokaryotic cyanobacteria,
357
reported to produce arsenosugars.32 Arsenosugars have also been found in underwater
358
plants as well;33 their source, however, is likely to be epiphytic algae or bacteria because
359
plants cannot methylate arsenic
360
immediate precursor of arsenosugars.11 Moreover, the physiological role of
361
arsenosugars is still unclear. For the oxo-arsenosguars, it’s known to be non-toxic to
362
humans, one arsenosugar (Oxo-Gly) was shown to be nontoxic to murine peritoneal
363
macrophages and alveolar macrophages at micromolar levels.35 The toxicity of thio-
364
arsenosugars whose bioaccessibility are much higher than the oxo-analogs, and
365
trimethylated arsenosugars haven’t been proved yet. Arsenosugar biosynthesis may
366
serve both as a detoxification process for the organisms which generate them, and as a
367
precursor for more complex organoarsenicals. Unraveling the mechanism of
368
arsenosugar biosynthesis will help determine toxicity of arsenosugars to human and the
369
physiological role of arsenosugars in arsenic biogeochemical cycling.
27
eukaryotic green algae
34
28, 31
and fungi all have been
and dimethylarsenic has been postulated to be the
370
Until our study, the pathway of arsenosugar biosynthesis was unknown. Edmonds
371
and Francesconi 4 proposed a pathway in marine alga in which DMAs(V) is reduced to
372
DMAs(III), which is then oxidized by addition of the deoxyadenosyl group from SAM
373
to yield the intermediate 5'-deoxy-5'-dimethylarsinoyl-adenosine. Enzymatic, 16
ACS Paragon Plus Environment
Page 17 of 33
Environmental Science & Technology
374
hydrolytic removal of adenine would be followed by formation of arsenosugars. This
375
proposal is supported by the identification of the proposed intermediate 5'-deoxy-5'-
376
dimethylarsinoyl-adenosine in the kidney of the giant clam Tridacna maxima,36 which
377
contains large quantities of arsenosugars owing to symbiotic algae growing in the
378
mantle of the clam. However, the product of arsenic methylation by ArsM enzymes is
379
almost certainly DMAs(III) and not DMAs(V),37, 38 so reduction of DMAs(V) is not
380
required. The ArsM reaction is required for producing the substrate of ArsS, but DMAs
381
has other fates such as further methylation to TMAs, so it is not a committed step in the
382
reaction pathway. Moreover, we show that co-expression of ArsM and ArsS in E. coli
383
produced many dimethylarsinoyl-hydroxycarboxylic acids but not 5'-deoxy-5'-
384
dimethylarsinoyl-adenosine. We are considering two possible pathways for
385
arsenosugar biosynthesis to account for the compounds produced by E. coli. Regardless
386
of the actual pathway, our data strongly support our hypothesis that the ArsS reaction
387
catalyzes the first committed step in arsenosugar biosynthesis.
17
ACS Paragon Plus Environment
Environmental Science & Technology
Page 18 of 33
388 389
The likely reason that arsenosugars are not generated by E. coli co-expressing
390
SsarsS and SsarsM is that the intermediate of arsenosugar biosynthesis cannot be
391
further transformed into arsenosugars because E. coli does not have the genes involved
392
in arsenosugar biosynthesis. An alternative fate for this intermediate, however, could
393
be that it is rapidly degraded in vivo to small arsenic-containing compounds such as
394
those that we found produced by the transgenic E. coli constructed for this study.
395
It is notable that the Synechocystis ars operon containing arsM and arsS is not
396
induced by As(III) or As(V), and the operon does not contain an arsR gene for an
397
As(III)-responsive transcription factor.39 Consistent with our observation of
398
constitutive expression of the arsM and arsS genes, the amount of arsenosugars and 18
ACS Paragon Plus Environment
Page 19 of 33
Environmental Science & Technology
399
arsenosugar phospholipids in Synechocystis treated with different concentrations of
400
As(V) did not significantly increase with increasing arsenic concentations.17 The
401
greater accumulation in Synechocystis of arsenosugar phospholipid compared with
402
arsenosugars suggests that arsenosugars are the precursors of arsenosugar
403
phospholipids and not the end products. The absence of arsenosugar intermediates in
404
Synechocystis suggests that DMAs is rapidly transformed into arsenosugars in those
405
cells, and that the arsenosugar intermediates, DMAs(III) and MAs(III), are probably
406
transient intermediates that do not accumulate in the cells.
407
Thus, we hypothesize that SsArsS, a putative radical SAM enzyme, adds a 5'-
408
deoxyadenosyl radical (dAdo·) to DMAs(III) and hydrolyzes the adenine from 5'-
409
deoxyadenosine simultaneously to generate 5'-deoxy -5'-dimethylarsinoyl-ribose.
410
SsArsS has a CX3CX2C motif similar to the assembly site for the [4Fe-4S] cluster found
411
in radical SAM enzymes. In addition, SsArsS has the other three cysteine residues in
412
the C-terminal region of SsArsS, Cys320, Cys323, Cys331, a CX2CX7C motif that
413
binds another putative [4Fe-4S] cluster (Figure S12), which would put it in a subgroup
414
of radical SAM enzymes that bind two [4Fe-4S] clusters, including MoaA,20 BioB,40
415
FbiC,41 LipA,42 TYW1.43 However, this CX2CX7C motif in the C-terminal region of
416
the SsArsS protein, which is not conserved in all radical SAM enzymes, is 5'-deoxy-5'-
417
not similar to other proteins that contained two or more iron-sulfur clusters.19 Mutations
418
in any of the cysteine residues in the CX2CX7C motif resulted in the loss of the function
419
for arsenosugar synthesis, consistent with a role for that motif in ArsS function.
420
Moreover, none of the cysteine mutants in either motif produced 5'-deoxy-5'19
ACS Paragon Plus Environment
Environmental Science & Technology
(Figure
S11),
indicating
Page 20 of 33
421
dimethylarsinoyl-adenosine
that
the
5'-deoxy-5'-
422
dimethylarsinoyl-riboside derivative was formed before 5'-deoxy-5'dimethylarsinoyl-
423
adenosine.
424
In summary, ArsS is the only member of the radical SAM superfamily shown to
425
be involved in arsenosugar synthesis. This study adds a new function to the repertoire
426
of enzymes of organoarsenical biotransformations and the radical SAM superfamily.
427
Further biochemical analysis of complex arsenic species and their molecular
428
mechanisms of biosynthesis and degradation will enable a better understanding for the
429
ecological roles of these complex organoarsenicals.
430 431
Acknowledgments
432
Our research is supported by the National Natural Science foundation of China
433
(41877422 and 21507125), Crossing-Group Project of KLUEH (KLUEH-201802), the
434
Austrian Science Fund (FWF) project number I2412-B21, and National Institutes of
435
Health Grants R01 GM55425 and ES023779 to bpr.
436 437
References
438
(1)
439 440
Edmonds, J. S.; Francesconi, K. A. Arseno-Sugars from Brown Kelp (Ecklonia Radiata) as Intermediates in Cycling of Arsenic in a Marine Ecosystem. Nature. 1981, pp 602–604.
(2)
Nischwitz, V.; Pergantis, S. A. Mapping of Arsenic Species and Identification of a Novel
441
Arsenosugar in Giant Clams Tridacna Maxima and Tridacna Derasa Using Advanced Mass
442
Spectrometric Techniques. Environ. Chem .2007, 4 (3), 187–196.
443
(3)
444 445
to the Cycling of Arsenic in Marine Ecosystems. Environ. Sci. Technol. 2015, 49 (1), 33–50. (4)
446 447 448
Duncan, E. G.; Maher, W. A.; Foster, S. D. Contribution of Arsenic Species in Unicellular Algae Edmonds, J. S.; Francesconi, K. A. Transformation of Arsenic in the Marine Environment. Experienta 1987, 43, 553–557.
(5)
Hoffmann, T.; Warmbold, B.; Smits, S. H. J.; Tschapek, B.; Ronzheimer, S.; Bashir, A.; Chen, C.; Rolbetzki, A.; Pittelkow, M.; Jebbar, M.; Seubert, A.; Schmitt, L.; Bremer, E. Arsenobetaine: 20
ACS Paragon Plus Environment
Page 21 of 33
Environmental Science & Technology
449
An Ecophysiologically Important Organoarsenical Confers Cytoprotection against Osmotic
450
Stress and Growth Temperature Extremes. Environ. Microbiol. 2018, 20 (1), 305–323.
451
(6)
452 453
Annu. Rev. Earth Planet. Sci. 2014, 42 (1), 443–467. (7)
454 455
Zhu, Y.; Xue, X.; Kappler, A.; Rosen, B. P.; Meharg, A. A. Linking Genes to Microbial Biogeochemical Cycling : Lessons from Arsenic. Environ. Sci. Technol. 2017, 51, 7326–7339.
(8)
456
Garcıi´a-Salgadoı, S.; Raber, G.; Raml, R.; Magnes, C.; Francesconi, K. A. Arsenosugar Phospholipids and Arsenic Hydrocarbons in Two Species of Brown Macroalgae. Environ. Chem.
457 458
Zhu, Y.-G.; Yoshinaga, M.; Zhao, F.-J.; Rosen, B. P. Earth Abides Arsenic Biotransformations.
2012, 9, 63–66. (9)
Petursdottir, A. H.; Fletcher, K.; Gunnlaugsdottir, H.; Krupp, E.; Kupper, F. C.; Feldmann, J.
459
Environmental Effects on Arsenosugars and Arsenolipids in Ectocarpus (Phaeophyta). Environ.
460
Chem. 2016, 13 (1), 21–33.
461
(10)
Carlin, A.; Shi, W.; Dey, S.; Rosen, B. P.; Carlin, A.; Shi, W.; Dey, S.; Rosen, B. P. The Ars
462
Operon of Escherichia Coli Confers Arsenical and Antimonial Resistance. J. Bacteriol. 1995,
463
177 (4), 981–986.
464
(11)
Xue, X.-M.; Ye, J.; Raber, G.; Francesconi, K. A.; Li, G.; Gao, H.; Yan, Y.; Rensing, C.; Zhu,
465
Y.-G. Arsenic Methyltransferase Is Involved in Arsenosugar Biosynthesis by Providing DMA.
466
Environ. Sci. Technol. 2017, 51 (3), 1224–1230.
467
(12)
John G. K. Williams. Construction of Specific Mutations in Photosystem II Photosynthetic
468
Reaction Center by Genetic Engineering Methods in Synechocystis 6803. Methods Enzymol.
469
1988, 167, 766–778.
470
(13)
471 472
Zang, X.; Liu, B.; Liu, S.; Arunakumara, K. K. I. U.; Zhang, X. Optimum Conditions for Transformation of Synechocystis sp. PCC 6803. J. Microbiol. 2007, 45 (3), 241–245.
(14)
Huang, H. H.; Camsund, D.; Lindblad, P.; Heidorn, T. Design and Characterization of Molecular
473
Tools for a Synthetic Biology Approach towards Developing Cyanobacterial Biotechnology.
474
Nucleic Acids Res. 2010, 38 (8), 2577–2593.
475
(15)
476 477
Gao, H.; Tang, Q.; Xu, X.-D. Construction of Copper-Induced Gene Expresson Platform in Synechocystis sp. PCC 6803. Acta Hydrobiol. Sin. 2006, 31 (2), 240–244.
(16)
Yin, X.-X.; Chen, J.; Qin, J.; Sun, G.-X.; Rosen, B. P.; Zhu, Y.-G. Biotransformation and
478
Volatilization of Arsenic by Three Photosynthetic Cyanobacteria. Plant Physiol. 2011, 156 (3),
479
1631–1638.
480
(17)
Xue, X.-M.; Raber, G.; Foster, S.; Chen, S.-C.; Francesconi, K. A.; Zhu, Y.-G. Biosynthesis of
481
Arsenolipids by the Cyanobacterium Synechocystis sp. PCC 6803. Environ. Chem. 2014, 11 (5),
482
506–513.
483
(18)
Xue, X.-M.; Yan, Y.; Xiong, C.; Raber, G.; Francesconi, K.; Pan, T.; Ye, J.; Zhu, Y.-G. Arsenic
484
Biotransformation by a Cyanobacterium Nostoc sp. PCC 7120. Environ. Pollut. 2017, 228, 111–
485
117.
486
(19)
487 488
Broderick, J. B.; Duffus, B. R.; Duschene, K. S.; Shepard, E. M. Radical S
‑
Adenosylmethionine Enzymes. Chem. Rev. 2014, 114, 4229–4317. (20)
Hänzelmann, P.; Schindelin, H. Binding of 5’-GTP to the C-Terminal FeS Cluster of the Radical
489
S-Adenosylmethionine Enzyme MoaA Provides Insights into Its Mechanism. Proc. Natl. Acad.
490
Sci. U. S. A. 2006, 103 (18), 6829–6834.
491 492
(21)
Ugulava, N. B.; Gibney, B. R.; Jarrett, J. T. Iron-Sulfur Cluster Interconversions in Biotin Synthase: Dissociation and Reassociation of Iron during Conversion of [2Fe-2S] to [4Fe-4S] 21
ACS Paragon Plus Environment
Environmental Science & Technology
493 494
Page 22 of 33
Clusters. Biochemistry 2000, 39, 5206–5214. (22)
Qin, J.; Rosen, B. P.; Zhang, Y.; Wang, G.; Franke, S.; Rensing, C. Arsenic Detoxification and
495
Evolution of Trimethylarsine Gas by a Microbial Arsenite S-Adenosylmethionine
496
Methyltransferase. Proc. Natl. Acad. Sci.U. S. A. 2006, 103 (7), 2075–2080.
497
(23)
Qin, J.; Lehr, C. R.; Yuan, C.; Le, X. C.; McDermott, T. R.; Rosen, B. P. Biotransformation of
498
Arsenic by a Yellowstone Thermoacidophilic Eukaryotic Alga. Proc. Natl. Acad. Sci. U. S. A.
499
2009, 106 (13), 5213–5217.
500
(24)
501 502
Liu, J.; Gladysheva, T. B.; Lee, L.; Rosen, B. P. Identification of an Essential Cysteinyl Residue in the ArsC Arsenate Reductase of Plasmid R773. Biochemistry 1995, 34, 13472–13476.
(25)
Wang, P. P.; Sun, G. X.; Zhu, Y. G. Identification and Characterization of Arsenite
503
Methyltransferase from an Archaeon, Methanosarcina Acetivorans C2A. Environ. Sci. Technol.
504
2014, 48 (21), 12706–12713.
505
(26)
506 507
Metalloactivation Domain of the ArsA ATPase. J. Biol. Chem. 1996, 271 (40), 24465–24470. (27)
508 509
(28)
Kuroiwa, T.; Ohki, A.; Naka, K.; Maeda, S. Biomethylation and Biotransformation of Arsenic in a Freshwater Food Chain: Green Alga (Chlorella Vulgaris)-Shrimp (Neocaridina
511
Denticulata)-Killifish (Oryzias Latipes). Appl. Organomet. Chem. 1994, 8, 325–333. (29)
513 514
Miyashita, S. I.; Fujiwara, S.; Tsuzuki, M.; Kaise, T. Cyanobacteria Produce Arsenosugars. Environ. Chem. 2012, 9 (5), 474–484.
510 512
Bhattacharjee, H.; Rosen, B. P. Spatial Proximity of Cys113, Cys172, and Cys422 in the
Saunders, J. K.; Rocap, G. Genomic Potential for Arsenic Efflux and Methylation Varies among Global Prochlorococcus Populations. ISME J. 2015, 10 (1), 197–209.
(30)
Edmonds, J. S.; Francesconi, K. A. Organoarsenic Compounds in the Marine Environment. In
515
Organometallic compounds in the environment; Craig, P. J., Ed.; Wiley: Chichester, 2013; pp
516
195–222.
517
(31)
Myashita, S.; Fujiwara, S.; Tsuzuki, M.; Kaise, T. Rapid Biotransformation of Arsenate into
518
Oxo-Arsenosugars by a Freshwater Unicellular Green Alga, Chlamydomonas Reinhardtii. Biosci.
519
Biotechnol. Biochem. 2011, 75 (3), 522–530.
520
(32)
Koch, I.; Feldmann, J.; Wang, L.; Andrewes, P.; Reimer, K. J.; Cullen, W. R. Arsenic in the
521
Meager Creek Hot Springs Environment, British Columbia, Canada. Sci. Total Environ. 1999,
522
236 (1–3), 101–117.
523
(33)
Koch, I.; Wang, L.; Ollson, C. A.; Cullen, W. R.; Reimer, K. J. The Predominance of Inorganic
524
Arsenic Species in Plants from Yellowknife, Northwest Territories, Canada. Environ. Sci.
525
Technol. 2000, 34 (1), 22–26.
526
(34)
Lomax, C.; Liu, W. J.; Wu, L.; Xue, K.; Xiong, J.; Zhou, J.; McGrath, S. P.; Meharg, A. A.;
527
Miller, A. J.; Zhao, F. J. Methylated Arsenic Species in Plants Originate from Soil
528
Microorganisms. New Phytol. 2012, 193 (3), 665–672.
529
(35)
530 531
Sakurai, T. Biological Effects of Organic Arsenic Compounds in Seafood. Appl. Organomet. Chem. 2002, 16 (8), 401–405.
(36)
Francesconi, K. A.; Edmondsa, J. S.; Stick, R. V. Arsenic Compounds from the Kidney of the
532
Giant Clam Tridacna Maxima: Isolation and Identification of an Arsenic-Containing Nucleoside.
533
J. Chem. Soc. Perkin Trans. 1 1992, 11, 1349–1357.
534
(37)
535 536
Dheeman, D. S.; Packianathan, C.; Pillai, J. K.; Rosen, B. P. Pathway of Human AS3MT Arsenic Methylation. Chem. Res. Toxicol. 2014, 27 (11), 1979–1989.
(38)
Marapakala, K.; Packianathan, C.; Ajees, A. A.; Dheeman, D. S.; Sankaran, B.; Kandavelu, P.; 22
ACS Paragon Plus Environment
Page 23 of 33
Environmental Science & Technology
537
Rosen, B. P. A Disulfide-Bond Cascade Mechanism for Arsenic(III) S-Adenosylmethionine
538
Methyltransferase. Acta Crystallogr. Sect. D Biol. Crystallogr. 2015, 71 (Iii), 505–515.
539
(39)
540 541
Sa´nchez-Riego, A. M.; Pez-Maury, L. L.; Florencio, F. J. Genomic Responses to Arsenic in the Cyanobacterium Synechocystis sp. PCC 6803. PLoS One 2014, 9 (5), e96826.
(40)
Sanyal, I.; Cohen, G.; Flint, D. H. Biotin Synthase: Purification, Characterization as a [2Fe-2S]
542
Cluster Protein, and in Vitro Activity of the Escherichia Coli BioB Gene Product. Biochemistry
543
1994, 33, 3625–3631.
544
(41)
Graham, D. E.; Xu, H.; White, R. H. Identification of the 7,8-Didemethyl-8-Hydroxy-5-
545
Deazariboflavin Synthase Required for Coenzyme F420 Biosynthesis. Arch. Microbiol. 2003,
546
180 (6), 455–464.
547
(42)
Urban, O. F.; Morris, T. W.; Reed, K. E.; Al, M. E. T. Lipoic Acid Metabolism in Escherichia
548
Coli: The LplA and LipB Genes Define Redundant Pathways for Ligation of Lipoyl Groups to
549
Apoprotein. J. Bacteriol. 1995, 177 (1), 1–10.
550
(43)
Perche-Letuvée, P.; Kathirvelu, V.; Berggren, G.; Clemancey, M.; Latour, J. M.; Maurel, V.;
551
Douki, T.; Armengaud, J.; Mulliez, E.; Fontecave, M.; Garcia-Serres, R.; Gambarelli, S.; Atta,
552
M.. 4-Demethylwyosine Synthase from Pyrococcus Abyssi Is a Radical-S-Adenosyl- L-
553
Methionine Enzyme with an Additional [4FE-4S]+2 Cluster That Interacts with the Pyruvate Co-
554
substrate. J. Biol. Chem. 2012, 287 (49), 41174–41185.
555 556 557 558 559 560 561 562 563 564 565 566 567 568 569 570 571 572 573 574 575 576 577 578 579 580 23
ACS Paragon Plus Environment
Environmental Science & Technology
Page 24 of 33
581 582 583
The TOC was created by Dr Xi-Mei Xue
584
TOC artwork
585 586 587 588 589 590 591 592 593 594 595 596 597 598 599 600 601 602 603 604 605 606 607 608 609 610 611 612 613 614 615 616 617 24
ACS Paragon Plus Environment
Page 25 of 33
Environmental Science & Technology
618 619
Legends
620 621
Table 1 Arsenic species in E. coli cells expressing SsarsM and SsarsS and medium were
622
determined by HPLC-ICP-MS/HR-ES-MS analysis using PRP-X100 when E. coli cells
623
expressing SsarsM and SsarsS were induced with 0.5 mM IPTG and 3 μΜ As(III) or
624
As(V).
625
A
m/z
Formula
Delta m [ppm]
138.97346
C2H8O2As
0.02
Molecular structure C H3 O
As
OH
C H3
210.99459
C5H12O4As
OH
-0.41
C H3
B
O
O
As OH
C H3 C H3
C
239.02589
C7H16O4As
-0.99
O
O
As OH
C H3 OH
241.00514
C6H14O5As
OH
-1.00
D
O
OH
As C H3
271.0157
C7H16O6As
-0.87
E
O
C H3
OH
C H3 O
OH
O
As OH
C H3 OH
OH
626 627 628 629 25
ACS Paragon Plus Environment
Environmental Science & Technology
Page 26 of 33
630 631
Figure 1. Cyanobacterial ars operons. Shown are the putative operons of Synechocystis
632
sp. PCC 6803 and Nostoc sp. PCC 7120. The arsM (slr0303, alr3095) genes encode
633
As(III) S-adenosylmethionine methyltransferases. Slr0305 from Synechocystis sp. PCC
634
6803 belongs to SNARE-associated superfamily, alr3096 of Nostoc sp. PCC 7120
635
encodes PitA (the low affinity inorganic phosphate transporter), arsS (slr0304, alr3097)
636
encodes a radical SAM superfamily enzyme shown in this report to be involved in
637
arsenosugar biosynthesis.
638
Figure 2. Anion-exchange HPLC-ICP-MS chromatograms of arsenic species from (a)
639
wild type Synechocystis and (b) Synechocystis ΔarsS after exposure to 1 µM As(III) for
640
two weeks, (c) wild type Synechocystis and (d) Synechocystis ΔarsS incubated with 10
641
µM MAs(V) for two weeks, (e) wild type Synechocystis and (f) Synechocystis ΔarsS
642
treated with 100 µM DMAs(V) for one week.
643
Figure 3 A. Western blot analysis of SsArsM and/or SsArsS expression in E. coli strain
644
Rosetta bearing the indicated expression plasmid constructs. MSR, MR, SR, or CK
645
containing pETDuet-SsarsS and pET-28a-SsarsM, pET-28a-SsarsM, pETDuet-SsarsS,
646
or pETDuet and pET-28a, respectively, induced by IPTG. B. Typical chromatograms
647
of arsenic species in E. coli strain Rosetta medium incubated with 3 μM As(III) by ion-
648
pairing
649
dimethylarsinoyl-hydroxycarboxylic acids.
650
Figure 4. Arsenic species transformed by different combination of ArsS orthologs and
651
SsArsM. A. Western blot analysis of SsArsM and different ArsS orthologs expression
652
in Rosetta bearing the indicated expression plasmid constructs. MNsS, MSeS, MPmS,
reverse-phase
column
HPLC-ICP-MS.
DMA-HA
indicates
the
26
ACS Paragon Plus Environment
Page 27 of 33
Environmental Science & Technology
653
MApS, MCvS indicate E. coli strain Rosetta cells containing pET-28a-SsarsM and
654
pETDuet-NsarsS, pETDuet-SearsS, pETDuet-PmarsS, pETDuet-AparsS, or pETDuet-
655
CvarsS induced by IPTG respectively. B. Typical chromatograms of arsenic analysis in
656
E. coli strain Rosetta medium treated with As(III) by ion-pairing reversed-phase
657
column HPLC-ICP-MS of SsArsM and different ArsS orthologs expressed in E. coli
658
strain Rosetta. DMA-HA indicates the dimethylarsinoyl-hydroxycarboxylic acids. The
659
mix consists of As(III), MAs(V), DMAs(V), As(V), and TMAO.
660 661 662 663 664 665 666 667 668 669 670 671 672 673 674 675 676 677 678 679 680 681 682 683 684 685 686 687 688 689 27
ACS Paragon Plus Environment
Environmental Science & Technology
Page 28 of 33
690
Associated content
691
Supporting Information: Supporting methods, Reagents and solutions (pS5),
692
Confirmation of arsMarsS operon (pS5), Phylogenetic analyses of SsArsS (pS6),
693
Comparative growth curves for WT, disruption strains and complementary strains
694
(pS6), Cloning arsM and arsS from cyanobacteria (pS7), Resistance assays (pS8),
695
Nucleotide sequence synthesis of ArsS orthologs from other sequenced organisms
696
(pS8), Construction of SsarsS cysteine mutants (pS9), Immunological detection of ArsS
697
and ArsM (pS10), The structures of several common arsenic compounds found in
698
nature (Figure S1), bacterial strains and plasmids (Table S1), Primer sequences used
699
for PCR amplification in the disruption, complementation, gene expression, site-mutant,
700
and ars operon identification strategies (Table S2), ICP-MS and chromatographic
701
conditions used for arsenic species analysis (Table S3), Confirmation of arsMarsS
702
operon (Figure S2), Gene deletion and complementation (Figure S3), Phylogram of
703
SsArsS and representative enzymes of the radical SAM superfamily with different
704
functions (Figure S4), The UV/visible spectroscopy of SsArsS shows a shoulder
705
centered at 410 nm for the [4Fe-4S]2+ protein (Figure S5), SDS-PAGE analysis (12%,
706
Coomassie blue-stained) of SsArsM and/or ArsS expression in Rosetta bearing the
707
indicated plasmid (Figure S6), SsArsS or /and SsArsM confers resistance to As(III) in
708
E. coli (Figure S7), Arsenic concentrations of different E. coli Rosetta cells or Rosetta
709
cells expressing SsarsM and SsarsS (Figure S8), ICP-MS and HR-ESMS measurements
710
of unknown arsenic species in E. coli medium (Figure S9), HPLC-ICP-MS (A) and HR-
711
ESMS measurements (B) of unknown arsenic species in E. coli cells (Figure S10),
712
Arsenic species transformed by different combination of SsarsS mutants and SsarsM 28
ACS Paragon Plus Environment
Page 29 of 33
Environmental Science & Technology
713
(Figure S11), The information of ArsS orthologs studied in this study (Table S4),
714
Multiple alignment of SsArsS and other five ArsS orthologs (Figure S12).
715 716 717 718 719 720 721 722
29
ACS Paragon Plus Environment
Environmental Science & Technology
Cyanobacterial ars operons. Shown are the putative operons of Synechocystis sp. PCC 6803 and Nostoc sp. PCC 7120. The arsM (slr0303, alr3095) genes encode As(III) S-adenosylmethionine methyltransferases. Slr0305 from Synechocystis sp. PCC 6803 belongs to SNARE-associated superfamily, alr3096 of Nostoc sp. PCC 7120 encodes PitA (the low affinity inorganic phosphate transporter), arsS (slr0304, alr3097) encodes a radical SAM superfamily enzyme shown in this report to be involved in arsenosugar biosynthesis. 283x122mm (96 x 96 DPI)
ACS Paragon Plus Environment
Page 30 of 33
Page 31 of 33
Environmental Science & Technology
Anion-exchange HPLC-ICP-MS chromatograms of arsenic species from (a) wild type Synechocystis and (b) Synechocystis ΔarsS after exposure to 1 µM As(III) for two weeks, (c) wild type Synechocystis and (d) Synechocystis ΔarsS incubated with 10 µM MAs(V) for two weeks, (e) wild type Synechocystis and (f) Synechocystis ΔarsS treated with 100 µM DMAs(V) for one week. 330x322mm (96 x 96 DPI)
ACS Paragon Plus Environment
Environmental Science & Technology
A. Western blot analysis of SsArsM and/or SsArsS expression in E. coli strain Rosetta bearing the indicated expression plasmid constructs. MSR, MR, SR, or CK containing pETDuet-SsarsS and pET-28a-SsarsM, pET28a-SsarsM, pETDuet-SsarsS, or pETDuet and pET-28a, respectively, induced by IPTG. B. Typical chromatograms of arsenic species in E. coli strain Rosetta medium incubated with 3 μM As(III) by ionpairing reverse-phase column HPLC-ICP-MS. DMA-HA indicates the dimethylarsinoyl-hydroxycarboxylic acids. 407x197mm (96 x 96 DPI)
ACS Paragon Plus Environment
Page 32 of 33
Page 33 of 33
Environmental Science & Technology
Arsenic species transformed by different combination of ArsS orthologs and SsArsM. A. Western blot analysis of SsArsM and different ArsS orthologs expression in Rosetta bearing the indicated expression plasmid constructs. MNsS, MSeS, MPmS, MApS, MCvS indicate E. coli strain Rosetta cells containing pET-28a-SsarsM and pETDuet-NsarsS, pETDuet-SearsS, pETDuet-PmarsS, pETDuet-AparsS, or pETDuet-CvarsS induced by IPTG respectively. B. Typical chromatograms of arsenic analysis in E. coli strain Rosetta medium treated with As(III) by ion-pairing reversed-phase column HPLC-ICP-MS of SsArsM and different ArsS orthologs expressed in E. coli strain Rosetta. DMA-HA indicates the dimethylarsinoyl-hydroxycarboxylic acids. The mix consists of As(III), MAs(V), DMAs(V), As(V), and TMAO. 333x157mm (96 x 96 DPI)
ACS Paragon Plus Environment