Subscriber access provided by UB + Fachbibliothek Chemie | (FU-Bibliothekssystem)
Article
Direct Conjugation of Emerging Contaminants in Arabidopsis: Indication for an Overlooked Risk in Plants? Qiuguo Fu, Jianbo Zhang, Dan Borchardt, Daniel Schlenk, and Jay J. Gan Environ. Sci. Technol., Just Accepted Manuscript • Publication Date (Web): 14 May 2017 Downloaded from http://pubs.acs.org on May 14, 2017
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 free 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 accessible to all readers and 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.
Environmental Science & Technology 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 42
Environmental Science & Technology
TOC Art
ACS Paragon Plus Environment
Environmental Science & Technology
1
Direct Conjugation of Emerging Contaminants in Arabidopsis: Indication for an
2
Overlooked Risk in Plants?
3
Qiuguo Fu,†,‡ Jianbo Zhang,§ Dan Borchardt,¶ Daniel Schlenk,† and Jay Gan†,*
4 5 6 7 8 9 10 11 12
†
Department of Environmental Sciences, University of California, Riverside, California 92521,
United States ‡
Eawag, Swiss Federal Institute of Aquatic Science and Technology Environmental Chemistry,
8600 Dübendorf, Switzerland §
Department of Health Sciences and Technology, Institute of Food, Nutrition and Health, ETH,
8092 Zürich, Switzerland ¶
Department of Chemistry, University of California, Riverside, California 92521, United States
13 14 15 16 17 18 19
Word count: Text (5452) + Figure (4×300) + Table (1×300) = 6952
20 21
1
ACS Paragon Plus Environment
Page 2 of 42
Page 3 of 42
Environmental Science & Technology
22
ABSTRACT
23
Agricultural use of treated wastewater, biosolids and animal wastes introduces a multitude of
24
contaminants of emerging concerns (CECs) into the soil-plant system. The potential for food
25
crops to accumulate CECs depends largely on their metabolism in plants, which at present is
26
poorly understood. Here we evaluated the metabolism of naproxen and ibuprofen, two of the
27
most used human drugs from the profen family, in Arabidopsis thaliana cells and Arabidopsis
28
plant. The complementary use of high-resolution mass spectrometry and 14C labeling allowed
29
characterization of both free and conjugated metabolites, as well as non-extractable residues.
30
Naproxen and ibuprofen, in their parent form, were conjugated quickly and directly with
31
glutamic acid and glutamine, and further with peptides, in A. thaliana cells. For example, after
32
120 h, the metabolites of naproxen accounted for >90% of the extractable chemical mass, while
33
the intact parent itself was negligible. The structures of glutamate and glutamine conjugates were
34
confirmed using synthesized standards, and further verified in whole plants. Amino acid
35
conjugates may easily deconjugate, releasing the parent molecule. This finding highlights the
36
possibility that the bioactivity of such CECs may be effectively preserved through direct
37
conjugation - a previously overlooked risk. Many other CECs are also carboxylic acids like the
38
profens. Therefore, direct conjugation may be a common route for plant metabolism of these
39
CECs, making it imperative to consider conjugates when assessing their risks.
40 41
Keywords: Contaminants of emerging concern; amino acid conjugation; water reuse;
42
pharmaceuticals; naproxen; ibuprofen
43
2
ACS Paragon Plus Environment
Environmental Science & Technology
44
INTRODUCTION
45
Many countries and regions are experiencing unprecedented water scarcity due to
46
population growth, urbanization, and climate change-induced disruptions in precipitation
47
patterns, prompting the search for alternative water sources.1 Reuse of municipal wastewater for
48
agricultural irrigation directly alleviates pressure on freshwater supplies, and indirectly
49
replenishes groundwater storage via percolation.2 However, treated wastewater is known to
50
contain many contaminants of emerging concern (CECs), including disinfection byproducts,
51
pharmaceuticals and personal care products, and endocrine disrupting compounds. Additionally,
52
large amounts of biosolids and animal wastes, which also contain numerous CECs, are
53
increasingly recycled back into agricultural fields as fertilizers.3 These practices inevitably
54
introduce CECs into the soil-plant system, posing the possibility for some CECs to enter the
55
terrestrial food chains, including the human diet.4–6
56
Studies over the last decade show that plants are capable of accumulating CECs from
57
soil, but the levels in edible tissues are relatively low under realistic conditions.1,7,8 However, in
58
these studies, researchers almost always targeted only the parent compound for analysis, while
59
neglecting metabolites, particularly conjugates that may have biological activity.8,9 Previous
60
research on xenobiotics such as pesticides shows that plants can transform man-made chemicals
61
through Phase I, II and III metabolism.9–11 Phase II metabolism is characterized with conjugation
62
of parent or metabolites with sugars, sulfates, and amino acids.12–14 Moreover, such conjugates
63
may readily undergo cleavage through enzymatic hydrolysis (e.g., in human gut), releasing
64
xenobiotics in the free form that may subsequently elicit biological responses.15 Therefore, a
65
comprehensive risk assessment of CECs in the soil-plant system should consider metabolic
66
transformations, especially conjugation, in plants.
3
ACS Paragon Plus Environment
Page 4 of 42
Page 5 of 42
Environmental Science & Technology
67
The goal of this study was to elucidate the biotransformation of CECs in plants to better
68
understand their risks in the waste reuse-food safety nexus. We used naproxen and ibuprofen as
69
model CECs to explore their metabolic fate in Arabidopsis. Naproxen and ibuprofen belong to
70
the profen family of the non-steroidal anti-inflammatory drugs, and are among the most
71
consumed human medicines.16 Like many other CECs, naproxen and ibuprofen are not
72
completely removed at wastewater treatment plants (WWTPs),17 resulting in their ubiquitous
73
occurrence in aquatic environments.18–20 For example, naproxen and ibuprofen were detected in
74
WWTP and hospital effluents at levels up to 11 µg L-1 and 151 µg L-1, respectively.21,22
75
In a recent study, low levels of naproxen and ibuprofen were detected in several
76
vegetables grown with treated wastewater irrigation under field conditions.1 When cultivated
77
hydroponically, naproxen and ibuprofen disappeared quickly from the nutrient media, but only
78
trace amounts of the parent were found in plant tissues,23 implying that they were converted to
79
other forms in the plant. Staswick et al. discovered that Arabidopsis was capable of conjugating
80
endogenous carboxylic acids with a number of amino acids.24 Here we hypothesized that in
81
plants, CECs with a carboxyl group, which encompass a large number of compounds, may form
82
conjugates with plant biomolecules. If this pathway is prevalent, the biological activity of these
83
contaminants may be effectively preserved, highlighting the importance to consider conjugates
84
when predicting adverse risks of CECs.
85 86 87
MATERIALS AND METHODS Chemicals. [Methoxy-14C]-Naproxen ((S)-6-methoxy-α-methyl-2-naphthaleneacetic
88
acid, radiochemical and chemical purity >99%, specific activity 55 mCi/mmol) was purchased
89
from American Radiolabeled Chemicals (Saint Louis, MO). Non-labeled naproxen and ibuprofen
4
ACS Paragon Plus Environment
Environmental Science & Technology
90
were obtained from Alfa Aesar (Ward Hill, MA). d3-Naproxen and d3-ibuprofen were obtained
91
from C/D/N Isotopes (Pointe-Claire, Quebec, Canada). Standard of 6-O-desmethylnaproxen was
92
acquired from Toronto Research Chemicals (Toronto, Ontario, Canada). Standards of glutamic
93
acid and glutamine conjugates of naproxen and ibuprofen were obtained through custom
94
synthesis (Biosynthesis, Lewisville, TX). All other chemicals were purchased from Fisher (Fair
95
Lawn, NJ). Ultrapure water was prepared using a Barnstead E-Pure water purification system
96
(Thermo Scientific, Dubuque, IA).
97
Arabidopsis thaliana Cell Line. The A. thaliana cell line PSB-D was provided by the
98
Arabidopsis Biological Resource Center at Ohio State University (Columbus, OH). Cells were
99
cultured in suspension at 25 °C and 130 rpm in the dark based on the supplier’s instructions.
100
Details on the medium composition and preparation are given in Text S1 in Supporting
101
Information (SI).
102
Incubation Experiments and Treatments. Active cells of A. thaliana were inoculated
103
into fresh culture medium (10%, v/v), followed by incubation in the dark at 25 °C and 130 rpm
104
for 4 d. An aliquot of 20 µl stock solution of 14C-naproxen (3.8 × 106 dpm) was spiked to the cell
105
culture to yield an initial chemical concentration of 2.0 ± 0.05 µg mL-1. The use of such a
106
relatively high concentration was to facilitate the identification of metabolites.21,22 For ibuprofen,
107
only non-labeled standard was used. Several control treatments were included for quality control,
108
including a blank cell culture control with A. thaliana cells only, a carrier solvent control with A.
109
thaliana cells spiked with 20 µl methanol (i.e., without chemical), a medium control with
110
naproxen (or ibuprofen) but without cells, and a medium control with non-viable cells
111
(autoclaved at 121 °C for 45 min) similarly spiked with 14C-naproxen.
112
Sample Preparation and Analysis. At 0, 6, 12, 24, 48, 96, and 120 h into the incubation,
5
ACS Paragon Plus Environment
Page 6 of 42
Page 7 of 42
Environmental Science & Technology
113
cells were immediately separated from the medium by centrifugation at 3000 rpm for 30 min. A
114
0.5 mL aliquot of supernatant was mixed with 4 mL UltimaGold cocktail to measure 14C
115
radioactivity on a PerkinElmer TriCarb liquid scintillation counter (LSC). The remaining
116
supernatant was added with 50 µL of 10 mg L-1 d3-naproxen (or d3-ibuprofen) as surrogate, and
117
the mixture was passed through a 150-mg HLB cartridge (Waters, Milford, MA) pre-conditioned
118
with 7-mL methanol and 7-mL ultrapure water. The analytes were eluted with 20 mL methanol
119
and reconstituted in 1.5 mL methanol after drying under N2.
120
The cell matter after centrifugation was collected and freeze-dried, followed by
121
sequential extractions and cleanup. Briefly, 0.10 g of the freeze-dried cells was spiked with 50
122
µL of 10 mg L-1 d3-naproxen (or d3-ibuprofen), followed by extraction with 20 mL of methanol
123
(twice) and acetonitrile (twice) in a sonication water bath. The extracts were pooled after
124
centrifugation (30 min at 3000 rpm) and reconstituted in 1.0 mL methanol after drying under N2.
125
A 20-µL aliquot of the final extract was measured for 14C radioactivity by LSC and defined as
126
the extractable residue (ER). The remaining extract was diluted with 20 mL ultrapure water and
127
passed through a 150-mg HLB cartridge (Waters, Milford, MA) for cleanup, as described above.
128
The final samples were centrifuged at 12,000 rpm for 10 min (Eppendorf 5840R, Wesseling-
129
Berzdorf, Germany) and filtered through a 0.22-µm polytetrafluoroethylene (PTFE) membrane
130
(Millipore, Carrigtwohill, Cork, Ireland) to remove solids. The final samples were stored at -
131
20 °C before analysis. The recoveries of naproxen and ibuprofen, as determined using the
132
deuterated surrogate, ranged from 76% to 94%, suggesting the overall effectiveness of the above
133
extraction procedure. More details on the recovery determination is provided as Text S2 in the
134
Supporting Information (SI).
135
To quantify the non-extractable residue, the cell matter after the sequential extractions
6
ACS Paragon Plus Environment
Environmental Science & Technology
136
was dried in the fume hood and then combusted on a Biological Oxidizer OX500 (R. J. Harvey
137
Instruments, Hillsdale, NJ). The released 14CO2 was trapped in 15 mL Harvey Carbon-14
138
Cocktail (R. J. Harvey) and the radioactivity was determined on LSC. The catalyst temperature
139
was 680 °C, the combustion temperature 900 °C and the combustion cycle was 4 min. The
140
recovery of the combustion procedure for 14C was determined to be 92.7 ± 2.6% (n= 3) using
141
standards.
142
UPLC-QqQ-MS/MS and LC-TOF-HRMS. The samples after SPE cleanup were
143
analyzed first on LC-TOF-HRMS to obtain the overall metabolic profile and identify metabolite
144
candidates after cross-comparison between the treatment and controls. The metabolite
145
candidates, together with the parent compound, were further analyzed on UPLC-QqQ-MS/MS in
146
different scan modes, including product ion scan, neutral loss scan, and multiple reactions
147
monitoring (MRM).
148
For the LC-TOF-HRMS analysis, an Agilent 1200 LC system coupled to Agilent 1200
149
series UV detector and an Agilent 6210 time-of-flight (TOF) mass spectrometer was used, and
150
the separation was achieved on an ACQUITY UPLC BEH C18 column (2.1 mm x 100 mm, 1.7
151
µm particle size, Waters) at 40 °C. Water (containing 5% methanol and 0.001% formic acid) and
152
methanol were used as the mobile phases A and B, respectively, which was programmed as
153
below (with respect to e B): 0-1 min, 5% to 50%; 1-17 min, 50 to 100%; 17-27 min, 100%; 28-
154
30 min, 100 to 5%; and 30-32 min, 5%. The flow rate was 0.17 mL/min and the injection volume
155
was 5 µL. The UV absorbance was recorded at 232 nm. The instrument control and data
156
acquisition were carried out with the MassHunter workstation software (Version B.01.03,
157
Agilent). The instrumental settings for TOF-HRMS were as follow: capillary voltage 2.5
158
kV, nebulizer 60 psig, drying gas 6 L/min, gas temperature 200 °C, fragmentor 115
7
ACS Paragon Plus Environment
Page 8 of 42
Page 9 of 42
Environmental Science & Technology
159
V, skimmer 60 V, Oct dc1 37.5 V, and Oct rf V 250 V. The mass axis was calibrated using the
160
mixture provided by the manufacturer over the m/z 100 – 3200 range. Spectra were acquired in
161
the electrospray ionization (ESI) negative mode over m/z 100−1700 Da, a scan rate of 1 scan/s
162
and resolution of 10,000.
163
For UPLC-QqQ-MS/MS analysis, samples were injected into a Waters ACQUITY ultra-
164
performance liquid chromatography (UPLC) combined with a Waters Micromass Triple
165
Quadrupole mass spectrometer (QqQ-MS) equipped with an electron spray ionization (ESI)
166
interface (Waters, Milford, MA). Separation was achieved on the same column and with mobile
167
phases as described above. The injection volume was 5 µL and flow rate was 0.2 mL min-1. The
168
MRM transitions of authentic standards of naproxen, d3-naproxen, desmethyl-naproxen,
169
ibuprofen and d3-ibuprofen were optimized and are summarized in Table S1. The specific
170
instrument settings were: capillary voltage 3.2 kV, cone voltage 30 V, collision gas (Argon,
171
99.99%) 0.2 ml/min, dwell time 0.02 s, source temperature 120 °C, desolvation temperature
172
350 °C, desolvation gas 600 L h-1 and cone gas 50 L h-1. The cone voltage (V) and collision
173
energy (eV) for each target analyte were optimized and are described in Supporting Information.
174
Candidate Identification. Raw data files were converted to mzXML files with
175
msConvert by PreoteoWizard25 and subsequently analyzed using the MZmine 2 software.26 The
176
presence, peak areas, retention times, and exact m/z in the different treatments were analyzed and
177
compared via MZmine according to the manual. Candidate metabolites were proposed in
178
accordance with their unique presence in the treatment and absence in all controls. At identical
179
retention times, characteristic natural isotopes were considered in structural elucidation. The
180
possible chemical formula for metabolite candidates and the error of mass accuracy in part per
181
million (ppm) were obtained using the Agilent Mass Hunter. After preliminary identification of
8
ACS Paragon Plus Environment
Environmental Science & Technology
182
candidate metabolites, the data were further confirmed by LC-QqQ-MS in the product ion scan,
183
neutral loss scan, and MRM scan mode. The main fragmentation patterns were acquired to
184
ascertain the structures of candidate metabolites by comparing with the database. Authentic
185
standards were used to confirm the proposed structures, when available. In addition to the parent
186
compound, custom synthesized standards of glutamic acid and glutamate conjugates of naproxen
187
or ibuprofen were used in this study to confirm the structure of the proposed conjugates by cross
188
comparison. Retention times, accurate masses, and fragmentation patterns were cross-compared
189
for unambiguous identification. Validation in Whole Plants. The metabolites were further validated in the whole plants
190 191
of two wild-type A. thaliana, i.e., Col-0 and Ler-0, grown in a hydroponic system. In brief, wild-
192
type A. thaliana seedlings were exposed to naproxen at 1.0 mg L-1 in the nutrient solution. After
193
4 d of exposure, the whole plants and nutrient medium were separately harvested. The
194
preparation of plant and growth medium samples was the same as described above for cell
195
cultures. LC-QqQ-MS/MS was used to target screen the proposed metabolites in the MRM
196
mode.
197
Statistical Analysis. Data are presented as mean ± standard deviation (SD). One-way
198
analysis of variance (ANOVA) and Student’s t-test were carried out with GraphPad 6 to evaluate
199
systematic differences among treatments and between two groups, respectively (α = 0.05).
200 201 202
RESULTS Dissipation of Parent Compound in Cell Culture. Both naproxen and ibuprofen were
203
considered in similar experiments and subjected to similar analyses. To streamline discussion,
204
here we focus on naproxen results in the main text, and present the findings on ibuprofen in SI.
9
ACS Paragon Plus Environment
Page 10 of 42
Page 11 of 42
205
Environmental Science & Technology
To affirm biotransformations of naproxen in A. thaliana cells, negative and positive
206
controls underwent the same handling and analytical procedures. In the control with non-viable
207
cells and cell-free medium, no apparent disappearance of naproxen occurred after the 120-h
208
incubation, indicating absence of abiotic transformation or adsorption onto the non-viable cells
209
(Figure 1A). However, in the presence of viable A. thaliana cells, naproxen quickly dissipated in
210
the medium. For example, naproxen concentration in the medium decreased from 2058 ± 290 ng
211
mL-1 initially to 61.5 ± 19.2 ng mL-1 at 6 h, to 0.6 ± 0.2 ng mL-1 at 24 h, and remained at a
212
negligible level until the end of 120-h incubation (Figure 1A). Fitting naproxen concentrations in
213
the medium to a first-order decay model resulted in a half-life of only 1.6 h. As abiotic
214
transformation or adsorption was negligible, naproxen disappearance in the medium containing
215
viable cells may be attributed to uptake and subsequent biotransformation by A. thaliana cells.
216
Figure 1B shows that naproxen appeared in the cells and that the level was the highest
217
after 6 h of incubation (the first sampling interval), providing direct evidence for its uptake into
218
A. thaliana cells. The concentration of naproxen in the cells, however, rapidly decreased as the
219
incubation time further increased and became negligible after 48 h (Figure 1B). Moreover, even
220
at 6 h, the amount of naproxen in the A. thaliana cells, in the parent form, accounted for only 1.0
221
± 0.1% of the spiked amount. This large discrepancy in mass balance implied that naproxen was
222
quickly and nearly completely converted to other forms from its parent form in the culture.
223
Formation of Metabolites of Naproxen. Eleven metabolites of naproxen in A. thaliana
224
cells were identified using LC-TOF-HRMS and UPLC-QqQ-MS/MS (Table 1 and Figure S1,
225
Figure S2). The identification was based on the following criteria commonly used for metabolite
226
identification27–31: a) error of measurement accuracy is < 5 ppm for [M-H] and [M+1-H]; b)
227
difference of observed and calculated isotopic abundance is < 1.5%; c) the calculated empirical
10
ACS Paragon Plus Environment
Environmental Science & Technology
228
formula obeys the nitrogen rule;32 d) fragmentation pattern matches reported data in literature or
229
database, or could be adequately explained; and e) retention time (tR) is identical to that of a
230
standard, if available.
231
The naproxen parent molecule was confirmed against its standard in LC-TOF-HRMS,
232
giving an accurate mass to charge ratio (m/z) of 229.0837 and a predicted [M-H] formula of
233
C10H9ON6. Further fragmentation gave fragments at m/z 185, 170, and 169, and the pattern was
234
consistent with those in the database (MassBank record KO001524). The demethylated product,
235
i.e., 6-O-desmethyl-naproxen, was observed and further confirmed with an authentic standard
236
(Table S1, Figure S2). Therefore, according to the scheme proposed by Schymanski et al.,33
237
naproxen and 6-O-desmethyl-naproxen achieved Level 1 unambiguous confirmation and they
238
may be considered as “confirmed” structures.
239
The metabolites N357 and N358 were identified via HRMS, fragmentation patterns,
240
literature and database searching, and directly confirmed with custom-synthesized standards
241
(Table 1, Text S2, Table S2-3, Figure S3-5). The accurate measurement of m/z of N357 (m/z
242
357.1455, tR = 9.3 min) gave the predicted [M-H] formula of C19H21N2O5 with an error of 0.15
243
ppm (Table 1), and the isotopic abundance difference (∆abundance) of [M+1-H] was 0.69%
244
(Table S2). In addition, N357 was found to produce fragments at m/z 185, 170, 145, 128, 127,
245
109, 84, and 74. The fragments of m/z 185 and 170 were the same as naproxen and suggested the
246
presence of naproxen analog in the metabolite (Table 1). Meanwhile, the fragments at m/z 145,
247
128, 127, 109, 84, and 74 were consistent with those of glutamine (Gln) as in the MassBank
248
database (Figure S3, Table S3). Therefore, N357 was identified as (2S)-2-(6-methoxy-2-
249
naphthyl) propanoyl-L-glutamine (Gln-naproxen). Similarly, the accurate m/z of N358 (m/z
250
358.2609, tR = 10.0 min) allowed the prediction of a chemical formula C19H21NO6 at 4.46 ppm,
11
ACS Paragon Plus Environment
Page 12 of 42
Page 13 of 42
Environmental Science & Technology
251
with ∆abundance of [M+1-H] at 0.39%. The metabolite N358 produced fragments at m/z 185,
252
170, 146, 128, 102, and 84, which were in agreement with the characteristic fragmentation
253
pattern of naproxen and glutamic acid in the present study and in the database (Table 1, Table S3,
254
and Figure S4). Consequently, N358 was identified as (2S)-2-(6-methoxy-2-naphthyl)
255
propanoyl-L-glutamic acid (Glu-naproxen). The structures of Gln-naproxen and Glu-naproxen
256
were further confirmed by comparing retention times and mass spectra against the authentic
257
standards (Text S2 and Figure S5). Thus, Gln-naproxen and Glu-naproxen also achieved Level 1
258
unambiguous confirmation as “confirmed” structures.33
259
The identification of the other 8 metabolites achieved Level 2a confirmation as
260
“probable” structures by applying the above criteria and analysis of fragmentation patterns.33 In
261
brief, N486 was identified as (2S)-2-(6-methoxy-2-naphthyl) propanoyl-L-α-glutamyl-L-
262
glutamine (GluGln-naproxen) (Table 1, Text S2), N401 as (2S)-2-(6-methoxy-2-naphthyl)
263
propanoyl-L-α-anlanyl-L-threonine (ThrAla-naproxen), N429 as (2S)-2-(6-methoxy-2-naphthyl)
264
propanoyl-L-α-anlanyl-L-glutamic acid (GluAla-naproxen) (Figure S4), and N457 as (2S)-2-(6-
265
methoxy-2-naphthyl) propanoyl-L-α-glutamyl-L-valine (ValGlu-naproxen) (Table 1). The
266
metabolites N471-a and N471-b were identified as (2S)-2-(6-methoxy-2-naphthyl) propanoyl-L-
267
α-glutamyl-L-isoleucine (IleGlu-naproxen) and (2S)-2-(6-methoxy-2-naphthyl) propanoyl-L-α-
268
glutamyl-L-leucine (LeuGlu-naproxen), respectively. The metabolite N505 was identified as
269
(2S)-2-(6-methoxy-2-naphthyl) propanoyl-L-α-glutamyl-L-phenylalanine (PheGlu-naproxen),
270
and N563 as (2S)-2-(6-hydroxy-2-naphthyl) propanoyl-L-α-glutaminylglycyl-L-tyrosine
271
(TyrGlyGln-DMnaproxen) (Table 1, Text S2, Table S1, Figure S6).
272 273
Finally, N477 (m/z 477.0562, tR =7.2min) showed a predicted formula C19H17N4O7S2 with a mass error of 3.84 ppm. However, the fragments were not adequately explained and
12
ACS Paragon Plus Environment
Environmental Science & Technology
274 275
therefore it remained as an “unknown” structure in this study (Table 1). Phase I and II Transformations of Naproxen. Analysis of primary metabolites clearly
276
showed that direct conjugation of naproxen with amino acids or peptides was a major route for
277
naproxen biotransformation in A. thaliana cells, accounting for >90% of the metabolites detected
278
after 120 h of cultivation (Figures 2 and 3). In view of the confirmed and probable
279
transformation intermediates, their abundance over time, and known plant auxin amino acid
280
pathways,34 three tentative transformation pathways depicting Phase I and II metabolism are
281
proposed (Figure 2). Briefly, naproxen parent undergoes direct conjugation with Glu to form
282
Glu-naproxen (N358) and further conjugation with an additional amino acid to form dipeptide
283
conjugates, i.e., ValGlu-naproxen (N457), IleGlu-naproxen (471-a), LeuGlu-naproxen (N471-b),
284
GluGln-naproxen (N486), or PheGlu-naproxen (N505). In addition, naproxen may also
285
conjugate directly with Gln, forming Gln-naproxen (N357) or undergo demethylation to form
286
DMnaproxen. These two metabolites may then undergo multi-step reactions, e.g., demethylation
287
and amino acid conjugation, to form the tripeptide conjugates, i.e., TyrGlyGln-DMnaproxen
288
(N563) (Figure 2). Interestingly, Gln-naproxen (N357) disappeared quickly from the cells, while
289
Glu-naproxen (N358) increased concurrently (Figures 3 and S6), suggesting that Gln-naproxen
290
may have been oxidized to Glu-naproxen. Additionally, naproxen may also conjugate with
291
peptides L-α-alanyl-L-threonine and L-α-alanyl-L-glutamic acid to form ThrAla-naproxen
292
(N401) and GluAla-naproxen (N429), respectively. The amounts of all metabolites tended to
293
decrease over time, except for Glu-naproxen (N358) or ThrAla-naproxen (N401) (Figures S7 and
294
S8), suggesting that some conjugates were further converted or incorporated into cell matter.
295 296
Throughout the incubation, the relative fraction of Glu-naproxen (N358) increased, and that of Gln-naproxen (N357) decreased, while naproxen and the other metabolites remained at
13
ACS Paragon Plus Environment
Page 14 of 42
Page 15 of 42
Environmental Science & Technology
297
similar levels over time (Figure 3). As reference standards were not available for all metabolites,
298
it was impossible to accurately evaluate the abundance of the conjugates in the cell extracts.
299
However, given their generally similar core structures and the use of identical analytical
300
conditions, the kinetics of formation and accumulation of these metabolites may be regarded as
301
semi-quantitative.30 These metabolites were also observed in the whole plant of Arabidopsis (Col-0 and Ler-
302 303
0). The concentrations of naproxen, Glu-naproxen and Gln-naproxen in Arabidopsis seedlings
304
after 4 d of cultivation were 3.5 ± 0.9, 3.2±1.0, and 1.5 ± 0.4 mg kg-1, respectively, for
305
Arabidopsis Col-0 and 1.8 ± 0.0, 4.6 ± 0.6, and 4.4 ± 1.3 mg kg-1, respectively, for Arabidopsis
306
Ler-0.
307
To the best of our knowledge, this is the first observation that conjugation of the parent
308
molecule with amino acids, instead of demethylation, glucuronidation, or sulfation, contributed
309
largely to the metabolic fate of naproxen in plants. The amino acid conjugates of naproxen and
310
its metabolite demethyl-naproxen were previously observed only in animals and microorganisms,
311
where the glycine conjugate was the most frequently observed, while the glucuronide conjugate
312
was the most dominant.35–40
313
Mass Balance and Phase III Compartmentation of Naproxen. To elucidate the full
314
metabolic fate of naproxen in plant cells, 14C labeled naproxen was used to quantitatively track
315
the incorporation of naproxen and its metabolites into cell matter. Figure 4 shows the dissipation
316
of extractable residues, formation of non-extractable residue and the overall mass balance of 14C
317
radioactivity. The overall mass balance ranged from 89±2 to 100±5% throughout the incubation,
318
suggesting good recoveries using the sample preparation protocol (Figure 4). The total
319
radioactivity in system did not change appreciably over time, implying that there was negligible
14
ACS Paragon Plus Environment
Environmental Science & Technology
320
loss due to volatilization of naproxen or its metabolites (e.g., 14CO2), or adsorption to container
321
surfaces. At the end of incubation, the extractable residues were 74.2 ± 0.6% of the initial spiked
322
14
C activity. The non-extractable residue quickly increased to 11.1 ± 1.7% at 6 h and further to
323
21.7 ± 3.4% at 24 h, and then gradually decreased to 11.0 ± 0.7% at 120 h. Therefore, non-
324
extractable residue was a relatively small fraction of the total radioactivity. This finding was
325
similar to that for the herbicide 2,4-D (also a carboxylic acid as naproxen) in soybean (Glycine
326
max L.) and wheat (Triticum aestivum L.) cells.41,42
327
Direct Conjugation of Ibuprofen. To test whether other profens undergo similar
328
transformation pathways in Arabidopsis, we exposed Arabidopsis cells to ibuprofen and
329
identified metabolites in a similar manner as for naproxen. The results showed that ibuprofen
330
underwent very similar transformation reactions to naproxen. For example, ibuprofen parent
331
conjugated directly with Gln or Glu to form Gln-IBP (IBP333, confirmed structure) or Glu-IBP
332
(IBP334, confirmed structure) (Figure S9, Text S2). In addition, ibuprofen was hydroxylated to
333
OH-IBP, which subsequently conjugated with Glu, Gln, and Ser to form 2-OH-Glu-IBP
334
(IBP350a), 3-OH-Glu-IBP (IBP350b), OH-Gln-IBP (IBP349), and OH-Ser-IBP (IBP308)
335
(Figure S9, Table S4). These results, together with findings for naproxen, clearly show that
336
conjugation with amino acids, especially Glu and Gln, was a major route of biotransformation of
337
profens in Arabidopsis.
338
It must be noted that to facilitate the identification of metabolites,21,22 relatively high
339
concentrations of naproxen and ibuprofen were used in both the cell cultivation and whole plant
340
hydroponic experiments. For instance, the concentration of naproxen or ibuprofen in wastewater
341
effluents usually does not exceed the low µg/L level. However, when treated wastewater is used
342
to irrigate a field, it is likely that water evaporates or leaches below the root zone, rendering the
15
ACS Paragon Plus Environment
Page 16 of 42
Page 17 of 42
Environmental Science & Technology
343
actual concentration of chemicals in the soil porewater higher than that in the irrigation water.
344
The root zone enrichment may further increase with repeated water applications. On the other
345
hand, studies show that plant transformation of xenobiotics (e.g., 2-mercaptobenzothiazole in
346
Arabidopsis) followed a similar kinetics at different concentrations. The dependence of
347
naproxen or ibuprofen biotransformation kinetics on the treatment concentrations was
348
unfortunately not evaluated in this study. Future research should consider field relevant
349
concentrations to obtain realistic plant accumulation data and refine potential dietary exposure
350
assessment.
351 352 353
DISCUSSION This study represents the first attempt to explore the metabolic fate of commonly used
354
profen drugs in plants by considering especially the formation of conjugates. The results clearly
355
showed that plant metabolites of naproxen or ibuprofen differed from that in other biota such as
356
microorganisms,43 fish,39 rodents,44 and humans.35,45 Demethylation, and conjugation with
357
glucuronic acid, sulfate, or glycine accounted for the major biotransformation routes of naproxen
358
in animals and microorganisms.38,39,44,46 Surprisingly, even though they were targeted for
359
analysis, there was no glucuronide conjugate of naproxen or ibuprofen detected in this study. In
360
contrast, a series of amino acid and peptide conjugates of the parent compound were identified in
361
the present study as the primary phase II metabolites of naproxen or ibuprofen in Arabidopsis
362
(Figure 2 and 5, Table S4 and Table S5). This observation was consistent with LeFevre et al. who
363
found several amino acid conjugates of 2-mercaptobenzothiazole27 and benzotriazole47 in
364
Arabidopsis, while no glucuronide conjugate was detected. In addition, glutamine and glutamate
365
also conjugated with hydroxyl-ibuprofen. These findings together suggest that conjugation with
16
ACS Paragon Plus Environment
Environmental Science & Technology
366 367
glutamic acid and glutamine is a common pathway for profens in Arabidopsis. Amino acid and dipeptide conjugates of other carboxylic acids have been previously
368
observed in insects, rodents, birds, mammals, and human, but this transformation route is
369
considered an “unusual” pathway in plants.48–50 For example, conjugates of carboxylic acids with
370
alanine, aspartic acid, arginine, serine, histidine, glutamic acid, glycine, glutamine, aspartic acid,
371
tryptophan, and taurine, as well as several dipeptides (i.e. glycyltaurin, glycylglycin,
372
aspartylserine, glycylvaline) have been reported in different animal species such as spiders,
373
houseflies, millipede, peripatus, rat, mouse, hamster, pigeon, hen, mallard, duck, bat, cow, horse,
374
cat, dog, and humans (Table S5 and Figure S10).48,51–53 In comparison, only sporadic studies
375
have shown amino acid conjugates of carboxylic acids in plants. Staswick et al.24 characterized
376
the conjugates of a plant auxin, indole-3-acetic acid (IAA), with Ala, Asp, Phe, and Trp in A.
377
thaliana seedlings. Feung et al.41 and Witham et al.42 studied the metabolism of the carboxylic
378
acid herbicide 2, 4-D in soybean callus tissue cultures. Seven amino acid conjugates were found,
379
with 2,4-D-Glu and 2,4-D-Asp as the major conjugates.41,42 In addition, the metabolic fate of 2,4-
380
D in plant cell cultures was found to be similar to that in whole plants, suggesting that
381
biotransformation in cells closely reflects the biotransformation pathways in intact plants.54
382
Findings from the previous studies and the current study together suggest that amino acid
383
conjugation is likely a common transformation pathway of carboxylic acids in plants.
384
Amino acid conjugation differs from glucuronidation or sulfation, as it involves one of
385
the various adenosine triphosphate (ATP)-dependent acid: CoA synthetases and acyl-CoA: amino
386
acid N-acyltransferases. The initial step in both xenobiotic and bile acid conjugation involves
387
activation of the carboxyl group to the reactive intermediate acyl-CoA, which is then transferred
388
to an amino acid residue.48,49 The most obvious physicochemical parameter potentially useful in
17
ACS Paragon Plus Environment
Page 18 of 42
Page 19 of 42
Environmental Science & Technology
389
determining conjugation is probably the pKa value of the carboxylic acid. The data for three
390
monochlorobenzoic acid derivatives indicated that the extent of glycine conjugation increased
391
with pKa and a change of ca. 1 pKa unit resulted in a 10- to 12-fold increase in glycine
392
conjugation.48 However, for compounds with a narrower range of pKa values, the position of
393
substitution is of greater importance.48,55 In addition to the substitution position, steric hindrance
394
may also be a determining factor in amino acid conjugation. For example, examination of the
395
ortho-substituted benzoic acids showed that chlorine, nitro, and methyl groups may have
396
stronger steric hindrance than the other moieties such as hydrogen and amino group.48
397
Furthermore, the conjugation pattern differed between isomers 1- and 2-naphthylacetic acids,
398
where 1-naphthylacetic acid conjugated preferentially with glucuronic acid and glycine, whereas
399
2-naphthylacetic acid conjugated favorably with glutamine, taurine, and glycine (Table S5).56
400
Indeed, naproxen and ibuprofen, analogous to 2-naphthylacetic acid, were found to be
401
preferentially conjugated with glutamine in Arabidopsis at the beginning of incubation. The
402
decrease of glutamine conjugate of naproxen (Figure S7) after 6 h may be due to further
403
conversions, e.g., to glutamate conjugate via oxidation (Figure 2). It must be noted that naproxen
404
(pKa = 4.2) and ibuprofen (pKa = 4.6) have very similar pKa values, and differences in their
405
conjugate formation may be attributable more to differences in their substitutions.57 Such
406
structural effects should be considered in future research to establish quantitative structure-
407
activity (QSAR) relationships, such as for the profens that all contain a propionic acid group with
408
different substitutions.
409
The predominance of certain amino acid conjugates observed in this and previous studies
410
may be due to the abundance and substrate specificity of enzymes in Arabidopsis that catalyze
411
these reactions.24,58 Staswick et al.,24 Westfall et al.,59 and Peat et al.60 systematically identified
18
ACS Paragon Plus Environment
Environmental Science & Technology
412
and characterized an Arabidopsis enzyme family, i.e., indole-3-acetic acid (IAA).
413
amidosynthetase (GH3), for conjugating IAA with various amino acids. Among the 19 GH3
414
proteins from Arabidopsis, GH3.5, GH3.2, GH3.12 and GH3.17 appeared to favor Glu over
415
other amino acids under in vitro reaction conditions.24,59 In addition, benzoate and 1-
416
naphthaleneacetic acid (NAA), structurally similar to naproxen, were found to have affinity for
417
the active site of GH3 proteins.24,60,61 These mechanistic studies, together with our results, show
418
that the GH3 enzyme family in plants may have a significant role in catalyzing the conjugation
419
of carboxylic acid compounds such as profens in plants. It is likely that differences in enzyme
420
types or their abundance may contribute to variations among plant species for their ability to
421
carry out these conjugation reactions.
422
Phase II reactions, i.e., glucuronidation, sulfation, and amino acid conjugation, are
423
generally considered detoxification pathways in animals, since the conjugates may be excreted
424
via urine and bile. However, conjugates in plant tissues may lead to underestimation of human
425
exposure, if such conjugates are deconjugated in plants or after human intake. Although it is
426
unclear how amino acid conjugates of naproxen or ibuprofen are regulated in plants, there is
427
evidence showing that glutamate conjugate of indole acetic acid (IAA-Glu) is not appreciably
428
hydrolyzed compared to other amino acid (e.g., leucine, alanine) conjugates of IAA in
429
Arabidopsis seedlings.34 In addition, human gut microbiota, enterocytes, and hepatocytes are
430
known to express enzymes such as aminoacylases, dipeptidases and glucuronidases that may
431
cleave conjugates.15,62–68 For instance, amino acid conjugates of salicylic acid were stable in the
432
upper gastrointestinal tract, but were hydrolyzed in the colon to release the active parent salicylic
433
acid.68 Glycine conjugate of naproxen was found to exhibit 78.5% reversion to naproxen by fecal
434
content in vitro.69 In general, the deconjugation rate of amino acid conjugates varied from 52.6%
19
ACS Paragon Plus Environment
Page 20 of 42
Page 21 of 42
Environmental Science & Technology
435
to 96.5%.64,66,68–70 Indeed, the daily intake of naproxen, if estimated by considering the
436
conjugation fraction in Arabidopsis seedlings and deconjugation rates, would be 752 ng/kg body
437
weight/day, using the same input values as in Prosser and Sibley.71 The calculated adult hazard
438
quotient would become 0.11, which is 11 times larger than that derived solely from the parent
439
compound (Text S3).71
440
The metabolite-parent back transformation was also found for other biologically active
441
compounds such as steroidal growth promoters72 and anticancer drugs.63 In some cases,
442
hydrolysis of conjugates and the following release of the active compound may be even fatal.63
443
Irinotecan, a potent antineoplastic prodrug in clinical use, was metabolized to an active
444
metabolite, SN-38, which conjugates with glucuronic acid by the liver to form SN-38-
445
glucuronide and then excreted into the colon via bile. The SN-38-gluruconide then served as a
446
substrate for gut microbial glucuronidase, producing active metabolite SN-38, which caused
447
severe diarrhea.63
448
While the release of parent or metabolites in the free form may be a source of
449
exposure,64,73 the amino acid conjugates themselves may also confer toxicological effects.69,74
450
For example, a variety of amino acid conjugates of naproxen and ibuprofen were found to have
451
similar biological activity to the parent in vivo in rats.74 The glycine/glutamine conjugates of
452
several other carboxylic acids also showed acute toxicity to mice or rat that was comparable to
453
that of the parent on a molar basis.48,75 This preservation and/or enhancement of reactivity or
454
toxicity has also been observed for various conjugates arising from acetylation, glucuronidation,
455
and glutathione conjugation.48 However, little is known about the biological activity of amino
456
acid conjugates of plant origin. Given the dominance of amino acid conjugates as observed for
457
naproxen and ibuprofen, it is possible that the other profens or carboxylic acids may undergo a
20
ACS Paragon Plus Environment
Environmental Science & Technology
458
similar transformation process. Thus, it is imperative to conduct further research to understand
459
the toxicological consequence of amino acid conjugates of such CECs from plant matrices.
460
Findings from this study showed that naproxen and ibuprofen were quickly metabolized
461
to produce a range of metabolites in Arabidopsis cells. The parent form of naproxen or ibuprofen
462
was only a negligible fraction of the chemical mass in Arabidopsis cells after 48 h. As many as
463
10 monoamino acid or peptide conjugates were confirmed or tentatively identified for naproxen,
464
of which the primary conjugates were Gln-naproxen (N357) and Glu-naproxen (N358). A similar
465
pattern was also observed for ibuprofen. The conjugates of amino acids and the parent compound
466
were also detected in whole plants of Arabidopsis. Given the importance of amino acid
467
conjugation in the plant metabolism of naproxen and ibuprofen, and that such conjugates are
468
potentially biologically active either before or after cleavage, risk assessment based on the
469
monitoring of the parent compound alone may lead to underestimations. Therefore, improved
470
risk assessment of human exposure to these compounds through practices such as wastewater
471
irrigation and solid waste reuse in agriculture should take plant biotransformation and conjugates
472
into consideration.
473
As many CECs similarly carry a carboxylic group, conjugation with amino acids may be
474
a common pathway for plant metabolism of a wide range of man-made chemicals. Further
475
research is needed to evaluate the biological activity of conjugates of CECs of plant origin and to
476
characterize the dependence of such conjugation on chemical structures as well as plant species.
477
Field and clinical observations targeting such conjugates in food produce may offer information,
478
enabling realistic risk predictions for practices, such as the use of treated wastewater, biosolids
479
and animal wastes in agriculture.
480
21
ACS Paragon Plus Environment
Page 22 of 42
Page 23 of 42
Environmental Science & Technology
481
Supporting Information
482
Additional details on descriptions of cell culture medium, metabolite identification, human
483
health risk calculation, and mass spectral information of naproxen and ibuprofen metabolites.
484
This material is available free of charge via the Internet at http://pubs.acs.org.
485 486
Corresponding Author:
487
*Phone: 951-827-2712; fax: 951-827-3993; e-mail:
[email protected].
488 489
ACKNOWLEDGMENTS. We appreciate Mr. Ron New for assistance in instrumental analysis.
490
This research was supported by the U.S. Environmental Protection Agency (Grant No.
491
83582901).
492 493
REFERENCES
494
(1)
Wu, X.; Conkle, J. L.; Ernst, F.; Gan, J. Treated wastewater irrigation: uptake of
495
pharmaceutical and personal care products by common vegetables under field conditions.
496
Environ. Sci. Technol. 2014, 48 (19), 11286–11293.
497
(2)
2012; Vol. 26.
498 499
(3)
United States Environmental Protection Agency. Biosolids generation, use, and disposal in the United States; Washington DC, 1999.
500 501
US Environmental Protection Agency. Guidelines for Water Reuse; Washington, D.C.,
(4)
Boxall, A.; Rudd, M. A.; Brooks, B. W.; Caldwell, D. J.; Choi, K.; Hickmann, S.; Innes,
502
E.; Ostapyk, K.; Staveley, J. P.; Verslycke, T.; et al. Pharmaceuticals and personal care
503
products in the environment: what are the big questions? Environ. Heal. Perspect. 2012,
22
ACS Paragon Plus Environment
Environmental Science & Technology
120 (9), 1221–1229.
504 505
(5)
Carter, L. J.; Harris, E.; Williams, M.; Ryan, J. J. .; Kookana, R. S. .; Boxall, A. B. A. Fate
506
and uptake of pharmaceuticals in soil-plant systems. J. Agric. Food Chem. 2014, 62 (4),
507
816–825.
508
(6)
of triclosan and triclocarban. Water Res. 2016, 102, 117–124.
509 510
Fu, Q.; Wu, X.; Ye, Q.; Ernst, F.; Gan, J. Biosolids inhibit bioavailability and plant uptake
(7)
Malchi, T.; Maor, Y.; Tadmor, G.; Shenker, M.; Chefetz, B. Irrigation of root vegetables
511
with treated wastewater: evaluating uptake of pharmaceuticals and the associated human
512
health risks. Environ. Sci. Technol. 2014, 48 (16), 9325–9333.
513
(8)
Wu, C.; Spongberg, A. L.; Witter, J. D.; Fang, M.; Czajkowski, K. P. Uptake of
514
pharmaceutical and personal care products by soybean plants from soils applied with
515
biosolids and irrigated with contaminated water. Environ. Sci. Technol. 2010, 44 (16),
516
6157–6161.
517
(9)
Schwitzguebel, J. P.; Vanek, T. Some fundamental advances for xenobiotic chemicals. In
518
Phytoremediation: transformation and control of contaminants; McCutcheon, S. C.,
519
Schnoor, J. L., Eds.; John Wiley & Sons: New Jersey, 2004; Vol. 121, pp 123–124.
520
(10)
Liu, J.; Hu, D.; Jiang, G.; Schnoor, J. L. In vivo biotransformation of 3,3′,4,4′-
521
tetrachlorobiphenyl by whole plants-poplars and switchgrass. Environ. Sci. Technol. 2009,
522
43 (19), 7503–7509.
523
(11)
carrot cell cultures. Environ. Pollut. 2016, 211, 141–147.
524 525 526
Wu, X.; Fu, Q.; Gan, J. Metabolism of pharmaceutical and personal care products by
(12)
Bartha, B.; Huber, C.; Schröder, P. Uptake and metabolism of diclofenac in Typha latifolia – how plants cope with human pharmaceutical pollution. Plant Sci. 2014, 227,
23
ACS Paragon Plus Environment
Page 24 of 42
Page 25 of 42
Environmental Science & Technology
12–20.
527 528
(13)
followed by glucose conjugation. J. Hazard. Mater. 2012, 243, 250–256.
529 530
Huber, C.; Bartha, B.; Schröder, P. Metabolism of diclofenac in plants – Hydroxylation is
(14)
Wang, S.; Cao, S.; Wang, Y.; Jiang, B.; Wang, L.; Sun, F.; Ji, R. Fate and metabolism of
531
the brominated flame retardant tetrabromobisphenol A (TBBPA) in rice cell suspension
532
culture. Environ. Pollut. 2016, 214, 299–306.
533
(15)
Weinheim, Germany, 2003.
534 535
(16)
Cleuvers, M. Mixture toxicity of the anti-inflammatory drugs diclofenac, ibuprofen, naproxen, and acetylsalicylic acid. Ecotoxicol. Environ. Saf. 2004, 59 (3), 309–315.
536 537
Testa, B.; Mayer, J. M. Hydrolysis in drug and prodrug metabolism; Wiley-VCH
(17)
Jelic, A.; Gros, M.; Ginebreda, A.; Cespedes-Sánchez, R.; Ventura, F.; Petrovic, M.;
538
Barcelo, D. Occurrence, partition and removal of pharmaceuticals in sewage water and
539
sludge during wastewater treatment. Water Res. 2011, 45 (3), 1165–1176.
540
(18)
Blair, B. D.; Crago, J. P.; Hedman, C. J.; Klaper, R. D. Pharmaceuticals and personal care
541
products found in the Great Lakes above concentrations of environmental concern.
542
Chemosphere 2013, 93 (9), 2116–2123.
543
(19)
Tixier, C.; Singer, H. P.; Oellers, S.; Muller, S. R. Occurrence and fate of carbamazepine,
544
clofibric acid, diclofenac, ibuprofen, ketoprofen, and naproxen in surface waters. Environ.
545
Sci. Technol. 2003, 37 (6), 1061–1068.
546
(20)
Eslami, A.; Amini, M.; Yazdanbakhsh, A.; Rastkari, N.; Mohseni-Bandpei, A.; Nasseri,
547
S.; Piroti, E.; Asadi, A. Occurrence of non-steroidal anti-inflammatory drugs in Tehran
548
source water, municipal and hospital wastewaters, and their ecotoxicological risk
549
assessment. Environ. Monit. Assess. 2015, 187 (12), 1–15.
24
ACS Paragon Plus Environment
Environmental Science & Technology
550
(21)
Verlicchi, P.; Al Aukidy, M.; Galletti, A.; Petrovic, M.; Barceló, D. Hospital effluent:
551
Investigation of the concentrations and distribution of pharmaceuticals and environmental
552
risk assessment. Sci. Total Environ. 2012, 430, 109–118.
553
(22)
Gómez, M. J.; Petrović, M.; Fernández-Alba, A. R.; Barceló, D. Determination of
554
pharmaceuticals of various therapeutic classes by solid-phase extraction and liquid
555
chromatography–tandem mass spectrometry analysis in hospital effluent wastewaters. J.
556
Chromatogr. A 2006, 1114 (2), 224–233.
557
(23)
Wu, X.; Ernst, F.; Conkle, J. L.; Gan, J. Comparative uptake and translocation of
558
pharmaceutical and personal care products (PPCPs) by common vegetables. Environ. Int.
559
2013, 60, 15–22.
560
(24)
Staswick, P. E.; Serban, B.; Rowe, M.; Tiryaki, I. Characterization of an Arabidopsis
561
enzyme family that conjugates amino acids to indole-3-acetic acid. Plant Cell 2005, 17
562
(2), 616–627.
563
(25)
Kessner, D.; Chambers, M.; Burke, R.; Agus, D.; Mallick, P. ProteoWizard: open source
564
software for rapid proteomics tools development. Bioinformatics 2008, 24 (21), 2534–
565
2536.
566
(26)
Pluskal, T.; Castillo, S.; Villar-Briones, A.; Oresic, M. MZmine 2: modular framework for
567
processing, visualizing, and analyzing mass spectrometry-based molecular profile data.
568
BMC Bioinformatics 2010, 11 (1), 395.
569
(27)
Lefevre, G. H.; Portmann, A. C.; Mu, C. E.; Sattely, E. S.; Luthy, R. G. Plant assimilation
570
kinetics and metabolism of 2- mercaptobenzothiazole tire rubber vulcanizers by
571
Arabidopsis. Environ. Sci. Technol. 2016, 50 (13), 6762–6771.
572
(28)
Rösch, A.; Anliker, S.; Hollender, J. How Biotransformation Influences Toxicokinetics of
25
ACS Paragon Plus Environment
Page 26 of 42
Page 27 of 42
Environmental Science & Technology
573
Azole Fungicides in the Aquatic Invertebrate Gammarus pulex. Environ. Sci. Technol.
574
2016, 50 (13), 7175–7188.
575
(29)
Storck, V.; Lucini, L.; Mamy, L.; Ferrari, F.; Papadopoulou, E. S.; Nikolaki, S.; Karas, P.
576
A.; Servien, R.; Karpouzas, D. G.; Trevisan, M.; et al. Identification and characterization
577
of tebuconazole transformation products in soil by combining suspect screening and
578
molecular typology. Environ. Pollut. 2016, 208, Part, 537–545.
579
(30)
Macherius, A.; Eggen, T.; Lorenz, W.; Moeder, M.; Ondruschka, J.; Reemtsma, T.
580
Metabolization of the bacteriostatic agent triclosan in edible plants and its consequences
581
for plant uptake assessment. Environ. Sci. Technol. 2012, 46 (19), 10797–10804.
582
(31)
cells: Rapid formation of conjugates. Environ. Pollut. 2017, 222, 383–392.
583 584
(32)
Silverstein, R. M.; Webster, F. X.; Kiemle, D. J.; Bryce, D. L. Spectrometric identification of organic compounds; John Wiley & Sons, 2014.
585 586
Fu, Q.; Ye, Q.; Zhang, J.; Richards, J.; Borchardt, D.; Gan, J. Diclofenac in Arabidopsis
(33)
Schymanski, E. L.; Jeon, J.; Gulde, R.; Fenner, K.; Ruff, M.; Singer, H. P.; Hollender, J.
587
Identifying small molecules via high resolution mass spectrometry: communicating
588
confidence. Environ. Sci. Technol. 2014, 48, 2097−2098.
589
(34)
95 (5), 707–735.
590 591
Woodward, A. W.; Bartel, B. Auxin: regulation, action, and interaction. Ann. Bot. 2005,
(35)
Sidelmann, U. G.; Bjornsdottir, I.; Shockcor, J. P.; Hansen, S. H.; Lindon, J. C.;
592
Nicholson, J. K.; Grove, U.; Bjørnsdottir, I.; Shockcor, J. P.; Honore, S.; et al. Directly
593
coupled HPLC-NMR and HPLC-MS approaches for the rapid characterisation of drug
594
metabolites in urine: Application to the human metabolism of naproxen. J. Pharm.
595
Biomed. Anal. 2001, 24 (4), 569–579.
26
ACS Paragon Plus Environment
Environmental Science & Technology
596
(36)
chronic toxicity studies: Application to naproxen. J. Pharm. Sci. 1973, 62 (6), 937–941.
597 598
Thompson, G. F.; Collins, J. M. Urinary metabolic profiles for choosing test animals for
(37)
Vree, T. B.; van den Biggelaar-Martea, M.; Verwey-van Wissen, C. P. Determination of
599
naproxen and its metabolite O-desmethylnaproxen with their acyl glucuronides in human
600
plasma and urine by means of direct gradient high-performance liquid chromatography. J.
601
Chromatogr. 1992, 578 (2), 239–249.
602
(38)
Andersen, J. V.; Hansen, S. H. Simultaneous quantitative determination of naproxen, its
603
metabolite 6-O-desmethylnaproxen and their five conjugates in plasma and urine samples
604
by high-performance liquid chromatography on dynamically modified silica. J.
605
Chromatogr. B Biomed. Sci. Appl. 1992, 577 (2), 325–333.
606
(39)
Brozinski, J.-M.; Lahti, M.; Oikari, A.; Kronberg, L. Detection of naproxen and its
607
metabolites in fish bile following intraperitoneal and aqueous exposure. Environ. Sci.
608
Pollut. Res. Int. 2011, 18 (5), 811–818.
609
(40)
Lahti, M.; Brozinski, J. M.; Jylhä, A.; Kronberg, L.; Oikari, A. Uptake from water,
610
biotransformation, and biliary excretion of pharmaceuticals by rainbow trout. Environ.
611
Toxicol. Chem. 2011, 30 (6), 1403–1411.
612
(41)
Feung, C.-S.; Hamilton, R. H.; Mumma, R. O. Metabolism of 2,4-dichlorophenoxyacetic
613
acid. V. Identification of metabolites in soybean callus tissue cultures. J. Agric. Food
614
Chem. 1973, 21 (4), 637–640.
615
(42)
Witham, F. H.; Feung, C.-S.; Hamilton, R. H. Metabolism of 2,4-dichlorophenoxyacetic
616
acid by soybean cotyledon callus tissue cultures. J. Agric. Food Chem. 1971, 19 (3), 475–
617
479.
618
(43)
Zhong, D.-F.; Sun, L.; Liu, L.; Huang, H.-H. Microbial transformation of naproxen by
27
ACS Paragon Plus Environment
Page 28 of 42
Page 29 of 42
Environmental Science & Technology
Cunninghamella species. Acta Pharmacol. Sin. 2003, 24, 442–447.
619 620
(44)
Sanoh, S.; Horiguchi, A.; Sugihara, K.; Kotake, Y.; Tayama, Y.; Uramaru, N.; Ohshita,
621
H.; Tateno, C.; Horie, T.; Kitamura, S.; et al. Predictability of metabolism of ibuprofen
622
and naproxen using chimeric mice with human hepatocytes. Drug Metab. Dispos. 2012,
623
40 (12), 2267–2272.
624
(45)
Aresta, A.; Palmisano, F.; Zambonin, C. G. Determination of naproxen in human urine by
625
solid-phase microextraction coupled to liquid chromatography. J. Pharm. Biomed. Anal.
626
2005, 39, 643–647.
627
(46)
Quintana, J. B.; Weiss, S.; Reemtsma, T. Pathways and metabolites of microbial
628
degradation of selected acidic pharmaceutical and their occurrence in municipal
629
wastewater treated by a membrane bioreactor. Water Res. 2005, 39 (12), 2654–2664.
630
(47)
LeFevre, G. H.; Müller, C. E.; Li, R. J.; Luthy, R. G.; Sattely, E. S. Rapid
631
phytotransformation of benzotriazole generates synthetic tryptophan and auxin analogs in
632
Arabidopsis. Environ. Sci. Technol. 2015, 49 (18), 10959–10968.
633
(48)
Hutt, A. J.; Caldwell, J. Amino acid conjugation. In Conjugation reactions in drug
634
metabolism: an integrated approach; Mulder, G. J., Ed.; CRC Press: London, 2003; pp
635
278–299.
636
(49)
Knights, K. M.; Sykes, M. J.; Miners, J. O. Amino acid conjugation: contribution to the
637
metabolism and toxicity of xenobiotic carboxylic acids. Expert Opin. Drug Metab.
638
Toxicol. 2007, 3 (2), 159–168.
639
(50)
Schröder, P. Exploiting Plant Metabolism for the Phytoremediation of Organic
640
Xenobiotics. In Phytoremediation; Willey, N., Ed.; Methods in Biotechnology; Humana
641
Press: New Jersey, 2007; pp 251–263.
28
ACS Paragon Plus Environment
Environmental Science & Technology
642
(51)
Knights, K. M.; Miners, J. O. Amino Acid Conjugation: A Novel Route of Xenobiotic
643
Carboxylic Acid Metabolism in Man. In Encyclopedia of Drug Metabolism and
644
Interactions; Lyubimov, A. V., Ed.; John Wiley & Sons, Inc.: Lancaster, 2011; pp 1–3.
645
(52)
Dixon, P. A. F.; Caldwell, J.; Smith, R. L. Metabolism of Arylacetic Acids: 2. The Fate of
646
[14C] Hydratropic Acid and its Variation with Species. Xenobiotica 1977, 7 (11), 707–
647
715.
648
(53)
Tanaka, Y.; Shimomura, Y.; Hirota, T.; Nozaki, A.; Ebata, M.; Takasaki, W.; Shigehara,
649
E.; Hayashi, R.; Caldwell, J. Formation of glycine conjugate and (–)-(R)-enantiomer from
650
(+)-(S)-2-phenylpropionic acid suggesting the formation of the coa thioester intermediate
651
of (+)-(S)-enantiomer in dogs. Chirality 1992, 4 (6), 342–348.
652
(54)
Feung, C. S.; Loerch, S. L.; Hamilton, R. H.; Mumma, R. O. Comparative metabolic fate
653
of 2,4-dichlorophenoxyacetic acid in plants and plant tissue culture. J. Agric. Food Chem.
654
1978, 26 (5), 1064–1067.
655
(55)
Dixon, P. A. F.; Caldwell, J.; Woods, C. J.; Smith, R. L. Influence of Chemical Structure
656
on the Pattern of Conjugation in vivo and in vitro of Some Arylacetic Acids in the Rat.
657
Biochem. Soc. Trans. 1976, 4 (1), 143–145.
658
(56)
Emudianughe, T. S.; Caldwell, J.; Smith, R. L. Studies on the metabolism of arylacetic
659
acids. 6. Comparative metabolic conjugation of 1-and 2-naphthylacetic acids in the guinea
660
pig, mouse, hamster and gerbil. Xenobiotica 1987, 17 (7), 815–821.
661
(57)
Chiarini, A.; Tartarini, A.; Fini, A. pH-Solubility Relationship and Partition Coefficients
662
for some Anti-Inflammatory Arylaliphatic Acids. Arch. Pharm. (Weinheim). 1984, 317
663
(3), 268–273.
664
(58)
Staswick, P. E.; Tiryaki, I.; Rowe, M. L. Jasmonate Response Locus JAR1 and Several
29
ACS Paragon Plus Environment
Page 30 of 42
Page 31 of 42
Environmental Science & Technology
665
Related Arabidopsis Genes Encode Enzymes of the Firefly Luciferase Superfamily That
666
Show Activity on Jasmonic, Salicylic, and Indole-3-Acetic Acids in an Assay for
667
Adenylation. Plant Cell 2002, 14 (6), 1405–1415.
668
(59)
Westfall, C. S.; Zubieta, C.; Herrmann, J.; Kapp, U.; Nanao, M. H.; Jez, J. M. Structural
669
basis for prereceptor modulation of plant hormones by GH3 proteins. Science (80-. ).
670
2012, 336, 1708–1711.
671
(60)
Peat, T. S.; Böttcher, C.; Newman, J.; Lucent, D.; Cowieson, N.; Davies, C. Crystal
672
structure of an indole-3-acetic acid amido synthetase from grapevine involved in auxin
673
homeostasis. Plant Cell 2012, 24 (11), 4525–4538.
674
(61)
Okrent, R. A.; Brooks, M. D.; Wildermuth, M. C. Arabidopsis GH3.12 (PBS3) conjugates
675
amino acids to 4-substituted benzoates and is inhibited by salicylate. J. Biol. Chem. 2009,
676
284 (15), 9742–9754.
677
(62)
August, J. T.; Murad, F.; Anders, M. W.; Dekant, W. Conjugation-dependent
678
carcinogenicity and toxicity of foreign compounds, 1st Edition. In Advances in
679
Pharmacology; Anders, M. W., Dekant, W., Eds.; Academic Press: San Diego, 1994; pp
680
431–448.
681
(63)
Wallace, B. D.; Wang, H.; Lane, K. T.; Scott, J. E.; Orans, J.; Koo, J. S.; Venkatesh, M.;
682
Jobin, C.; Yeh, L.-A.; Mani, S.; et al. Alleviating cancer drug toxicity by inhibiting a
683
bacterial enzyme. Science (80-. ). 2010, 330 (6005), 831–835.
684
(64)
acid in rabbit intestinal microorganisms. J. Pharmacobiodyn. 1985, 8 (12), 989–995.
685 686 687
Shibasaki, J.; Inoue, Y.; Kadosaki, K.; Sasaki, H.; Nakamura, J. Hydrolysis of salicyluric
(65)
Vomvukas, S.; Anders’r, M. W. Bioconversion of prodrugs by conjugate-processing enzymes. Conjug. Carcinog. Toxic. Foreign Compd. 1994, 27, 479–499.
30
ACS Paragon Plus Environment
Environmental Science & Technology
688
(66)
Environ. Microbiol. 1977, 33 (1), 15–18.
689 690
(67)
Sinha, V. R.; Kumria, R. Microbially triggered drug delivery to the colon. Eur. J. Pharm. Sci. 2003, 18 (1), 3–18.
691 692
Gilliland, S. E.; Speck, M. L. Deconjugation of bile acids by intestinal lactobacilli. Appl.
(68)
Nakamura, J.; Asai, K.; Nishida, K.; Sasaki, H. A novel prodrug of salicylic acid, salicylic
693
acid-glutamic acid conjugate utilizing hydrolysis in rabbit intestinal microorganisms.
694
Chem. Pharm. Bull. 1992, 40 (8), 2164–2168.
695
(69)
Mishra, A.; Agrawal, S.; Pathak, K. Naproxen glycine conjugate-synthesis,
696
pharmaceutical preformulation and pharmacodynamic evaluation. Drug Deliv. 2012, 19
697
(2), 102–111.
698
(70)
using a targeted prodrug approach. J. Pharm. Pharmacol. 2008, 60 (5), 607–613.
699 700
Philip, A. K.; Dubey, R. K.; Pathak, K. Optimizing delivery of flurbiprofen to the colon
(71)
Prosser, R. S.; Sibley, P. K. Human health risk assessment of pharmaceuticals and
701
personal care products in plant tissue due to biosolids and manure amendments, and
702
wastewater irrigation. Environ. Int. 2015, 75, 223–233.
703
(72)
Qu, S.; Kolodziej, E. P.; Long, S. A.; Gloer, J. B.; Patterson, E. V; Baltrusaitis, J.; Jones,
704
G. D.; Benchetler, P. V; Cole, E. A.; Kimbrough, K. C.; et al. Product-to-Parent Reversion
705
of Trenbolone: Unrecognized Risks for Endocrine Disruption. Science (80-. ). 2013, 342
706
(6156), 347–351.
707
(73)
products. Environ. Sci. Technol. 2003, 37 (20), 4617–4625.
708 709 710
Sinclair, C. J.; Boxall, A. B. A. Assessing the ecotoxicity of pesticide transformation
(74)
Shanbhag, V. R.; Crider, A. M.; Gokhale, R.; Harpalani, A.; Dick, R. M. Ester and amide prodrugs of ibuprofen and naproxen: Synthesis, anti-inflammatory activity, and
31
ACS Paragon Plus Environment
Page 32 of 42
Page 33 of 42
Environmental Science & Technology
gastrointestinal toxicity. J. Pharm. Sci. 1992, 81 (2), 149–154.
711 712
(75)
Buly, R. L.; Mumma, R. O. Excretion and metabolism of [(2,4-
713
dichlorophenoxy)acetyl]aspartic acid and [(2,4-dichlorophenoxy)acetyl]valine in the rat. J.
714
Agric. Food Chem. 1984, 32 (3), 571–577.
715
32
ACS Paragon Plus Environment
Environmental Science & Technology
716
Figure captions:
717 718
Figure 1. Levels of naproxen in the medium and Arabidopsis thaliana cells. (A) Concentrations
719
of naproxen in the medium cultured with nonviable cells (filled square, ■), no cells (filled
720
triangle, ▲), and viable cells (open circle, ○); and (B) Concentrations of naproxen in viable cells
721
(open diamond, ◊) and nonviable cells (open square, □).
722 723
Figure 2. Proposed formation pathways of naproxen metabolites observed in Arabidopsis
724
thaliana cells based on literature pathways of auxin storage and reactivation. Full chemical
725
names are given in Table 1 for naproxen and its metabolites. Solid line means that phase II
726
metabolites were formed, and dash line indicates that phase I metabolites were formed. Two
727
solid arrow suggests multi-step reactions.
728 729
Figure 3. Kinetics of realtive fractions (%, based on LC-MS/MS peak areas) of naproxen and its
730
metabolites in Arabidopsis thaliana cells during 120-h incubation. Full chemical names are
731
given in Table 1.
732 733
Figure 4. Extractable residue (filled triangle, ▼), bound residue (open triangle, △), and mass
734
balances (open square, □) of 14C-naproxen in Arabidopsis thaliana cell cultures. Error bars
735
represent standard deviation of triplicates. Invisible error bars are in the symbols.
736 737 738 739
33
ACS Paragon Plus Environment
Page 34 of 42
Page 35 of 42
Environmental Science & Technology
740
Table 1. Identities of naproxen and its transformation products, and information of high-resolution mass spectra, fragments, retention
741
times, and identification confidence.
742
IDa
tR (min) TOF
m/z measured
Predicted formula [M-H]
m/z calculate d
NPX
11.5
229.0874
C14H13O3
229.0870
N357
9.3
357.1455
C19H21N2O5
357.1456
N358
10.0
358.1312
C19H20NO6
358.1296
N401
9.1
401.1721
C21H25N2O6
401.1718
Error (ppm)
Fragments (m/z)
*185 (naproxen-CO2), 1.7 170 (185-CH3), 169 185 (-Gln-CO), 170 (185-CH3), *145 (Gln), a 128 (Gln-NH2), 0.15 127 (Gln-OH), 109 (145-H2O-NH3), 84 (128-CO2), 74 185 (-Glu-CO), 170 (185-CH3), 146 (Glu), b 4.46 128 (Glu-H2O), *102 (Glu-CO2), 84 (128-CO2) 383 ( 401-H2O), 185 (-AlaThr-CO), 170 (185-CH3), 189 (AlaThr), 0.61 *171 (189-OH), 153 (171-H2O), 141 (171-CH2O), 128 (AlaThr-CO2-OH), 34
ACS Paragon Plus Environment
Structure proposed
Confidenceb Level 1 (Confirmed)
Level 1 (Confirmed)
Level 1 (Confirmed)
Level 2a (Probable)
Environmental Science & Technology
N429
9.5
429.1675
C22H25N2O6
N457
10.2
457.1988
C24H29N2O7
N471a
10.8
471.2125
C25H31N2O7
D471b
11.2
471.2141
C25H31N2O7
110 (128-NH3), 86 (Thr-OH-CH3), 84 (128-C2H6N), 185 (-GluAla-CO), 170 (185-CH3), 155 (170-CH3), 429.1667 1.79 300 (+H2O-Glu) 199 (GluAla), *128 (Glu- H2O), *88 (Ala), c 185 (-GluVal-CO), 170 (185-CH3), 395 (-CO2-OH), 341 (-Val), d 297 (341-CO2), 457.1980 1.71 245 (ValGlu), e 228 (245-OH), 201 (228-OH), 184 (228-CO2), *128 (Glu- H2O), 116 (Val) 185 (-GluIle-CO), 128 (Glu-H2O), 457.2137 0.8 241 (GluIle-OH) 130 (Ile), f 185 (-GluLeu-CO), 170 (185-CH3), 128 (Glu-H2O), 457.2137 0.9 241 (GluLeu-OH) 130 (Leu), g
35
ACS Paragon Plus Environment
Page 36 of 42
Level 2a (Probable)
Level 2a (Probable)
Level 2a (Probable)
Level 2a (Probable)
Page 37 of 42
Environmental Science & Technology
N486
8.9
486.1885
C24H28N3O8
N505
11.0
505.2003
C28H29N2O7
N563
8.5
563.2145
C29H31N4O8
185 (-GluGln-CO), 170 (185-CH3), *145 (Gln), 128 (Gln-OH/Glu-H2O), 127 (Gln-OH), 109 (145-H2O-NH3), 486.1882 0.63 146 (Glu), 102 (Glu-CO2), 86 (102-O), 274 (GluGln) 257 (274-OH), 239 (257-H2O), 213 (257-CO2), 185 (-PheGlu-CO), 170 (185-CH3), 325 (-Phe-O), 275 (PheGlu-OH), 252 (275-OH), 505.1980 4.5 *164 (Phe), h 147, (Phe-OH) 72 (Phe-Bn), i 128 (Glu-H2O), 109 (128-NH4), 171 (-TyrGlyGln-CO), *351 (TyrGlyGln-NH2), 333 (351-H2O), 383 (-Tyr), 162 (Tyr-OH), 563.2147 0.47 149 (Tyr-OH-NH), 119 (Tyr-CO2-OH), 128 (Gln-NH2), 101 (Gln-CO-NH2), 89, 85, 72,
36
ACS Paragon Plus Environment
Level 2a (Probable)
Level 2a (Probable)
Level 2a (Probable)
Environmental Science & Technology
N477
743 744 745 746 747 748 749 750 751 752
7.2
477.0562
C19H17N4O7S2
477.0544
405, 360, 129, 195, 284, 119, 110, 101, 99, *97, 3.84 96, 85, 75,145, 139, 165, 203, 436, 74, 128, 175, 236
a
Page 38 of 42
Unknown structure
Level 3 (Unknown)
List of abbreviations: NPX (naproxen): (2S)-2-(6-methoxy-2-naphthyl)propanoic acid; N357, (2S)-2-(6-methoxy-2naphthyl)propanoyl-L-glutamine; N358, (2S)-2-(6-methoxy-2-naphthyl)propanoyl-L-glutamic acid; N401, (2S)-2-(6-methoxy-2naphthyl)propanoyl-L-α-anlanyl-L-threonine; N429, (2S)-2-(6-methoxy-2-naphthyl)propanoyl-L-α-anlanyl-L-glutamic acid; N457, (2S)-2-(6-methoxy-2-naphthyl)propanoyl-L-α-glutamyl-L-valine; N471-a, (2S)-2-(6-methoxy-2-naphthyl)propanoyl-L-α-glutamyl-Lisoleucine; D471-b, (2S)-2-(6-methoxy-2-naphthyl)propanoyl-L-α-glutamyl-L-leucine; N486, (2S)-2-(6-methoxy-2naphthyl)propanoyl-L-α-glutamyl-L-glutamine; N505, (2S)-2-(6-methoxy-2-naphthyl)propanoyl-L-α-glutamyl-L-phenylalanine; and N563, (2S)-2-(6-hydroxy-2-naphthyl)propanoyl-L-α-glutaminylglycyl-L-tyrosine. b Structure identification confidence was calculated according to Schymanski et al.33 ppm: part per million.
37
ACS Paragon Plus Environment
Page 39 of 42
Environmental Science & Technology
753 754
755 756 757
Figure 1.
758 759 760 761 762 763 764
38
ACS Paragon Plus Environment
Environmental Science & Technology
765 766 767
Figure 2.
768
39
ACS Paragon Plus Environment
Page 40 of 42
Page 41 of 42
Environmental Science & Technology
769
770 771 772
Figure 3.
773 774
40
ACS Paragon Plus Environment
Environmental Science & Technology
775
776 777 778
Figure 4.
41
ACS Paragon Plus Environment
Page 42 of 42