0090-9556/03/3108-993-998$20.00
DMD 31:993-998, 2003
GLUCURONIDATION AND EXCRETION OF NONYLPHENOL IN PERFUSED RAT LIVER
Tomo Daidoji,
Hiroki Inoue,
Seiyu Kato, and
Hiroshi Yokota
Departments of Veterinary Biochemistry (T.D., H.Y.) and Veterinary
Physiology (H.I., S.K.), School of Veterinary Medicine, Rakuno Gakuen
University, Hokkaido, Japan
(Received February 4, 2003;
accepted May 9, 2003)
 |
Abstract
|
|---|
Nonylphenol, an environmental estrogenic chemical, is reported to have
adverse effects on the reproductive organs of animals. In this study, the
metabolism of nonylphenol and that of other alkylphenols in the rat liver was
investigated using liver perfusion. Alkylphenols (nonylphenol, hexylphenol,
butylphenol, and ethylphenol) were glucuronidated by rat liver microsomes.
Nonylphenol was found to be conjugated with glucuronic acid by an isoform of
UDP-glucuronosyltransferase, UGT2B1, expressed in yeast AH22 cells. However,
when nonylphenol was perfused into rat liver in situ, it was difficult for
free nonylphenol and conjugated metabolite to be excreted into the bile or
vein, and most of the perfused nonylphenol remained free and as a glucuronide
conjugate in the liver tissue, even after 1 h of perfusion. After 1 h of
perfusion of the other alkylphenols, most of them were excreted into the bile
as glucuronides. Ethylphenol, which has the shortest alkyl chain, was excreted
rapidly into both the bile and vein; however, the excretion rates of
alkylphenols having longer alkyl chains tended to be slow. MRP-2-deficient
Eisai hyperbilirubinemic rats could not secrete alkylphenol-glucuronides into
the bile, indicating that alkylphenol-glucuronides are transported by MRP-2 to
the bile in normal Sprague-Dawley rats. The results indicate that the kinetics
of excretion of alkylphenol-glucuronides into the bile or vein depends on the
length of alkyl chain and suggest that nonylphenol-glucuronide formed in the
liver cannot be transported by MRP-2.
Environmental estrogenic chemicals such as bisphenol A and nonylphenol,
which are contained in many industrial products, can be detected in foods, tap
water, and many environmental materials. Nonylphenol is used in a wide variety
of detergents and plastics and has been reported to be environmentally
persistent (White et al.,
1994
). The mean daily oral intake of nonylphenol by humans is
estimated to be 0.16 mg/day (Muller et
al., 1998
). Nonylphenol has been shown to be a possible endocrine
disrupter due to its estrogenic effects in MCF7 cell proliferation assays
(Soto et al., 1991
), binding
assays to the estrogen receptor (White et
al., 1994
) and uterotropic assays in mice
(Shelby et al., 1996
).
Exposure of male rainbow trout (Oncorhynchus mykiss) to four
different alkylphenolic chemicals, including nonylphenol, resulted in
synthesis of vitellogenin, a process normally dependent on endogenous
estrogens, and a concomitant inhibition of testicular growth
(Jobling et al., 1996
). Male
and female ratios of Japanese medaka (Oryzias latipes) in a control
group (2:1) and a 100 µg/l nonylphenol treatment group (1:2) were reported
to be significantly different (Gray and
Metcalfe, 1997
). Early neonatal exposure to nonylphenol has been
reported to cause dysfunction of postpubertal reproductive function in female
rats as well as disrupted development of gonads in male and female rats
(Nagao et al., 2000
). It has
also been reported that nonylphenol administered orally at a dose of 50 mg/kg
of body weight induced a significant increase in uterine weight of prepubertal
rats and advanced the age of vaginal opening
(Laws et al., 2000
).
Elucidation of the metabolism and fate of nonylphenol is important for
estimating the risks of the chemical for animals. Xenoestrogens such as
bisphenol A and diethylstilbestrol have been shown to be conjugated with
glucuronic acid by a UDP-glucuronosyltransferase isoform, UGT2B1, in the rat
liver (Yokota et al., 1999
).
Nonylphenol has also been reported to be glucuronidated extensively in the
liver of animals such as rainbow trout
(Lewis and Lech, 1996
;
Coldham et al., 1998
; Thibaut
et al.,
1998a
,b
)
and rats (Moffat et al., 2001
;
Yokota et al., 2002
). Since
the liver is the main barrier against drugs in the body, identifying or
tracing the metabolites of nonylphenol is important for elucidation of the
disruptive effects of the compound on the reproductive system.
In this study, we investigated the metabolism and kinetics of nonylphenol
and those of other alkylphenols by means of liver perfusion, and we found that
nonylphenol was delayed in excretion from the liver and that the length of the
alkyl chain is a critical factor for the excretion rate and route out of the
liver.
 |
Materials and Methods
|
|---|
Chemicals. 4-Nonylphenol and other alkylphenols were purchased from
Kanto Chemical Co. (Tokyo, Japan). High-performance liquid chromatography
(HPLC1)-grade
acetonitrile was obtained from Labscan Ltd. (Dublin, Ireland).
ß-Glucuronidase was obtained from Sigma-Aldrich (St. Louis, MO).
Animals. Male young adult Sprague-Dawley (SD) rats (813 weeks
old) and MRP-2-deficient Eisai hyperbilirubinemic rats (EHBR) were used in all
experiments. The rats were housed under standard conditions and given food and
water ad libitum before use. The rats were handled according to the Laboratory
Animal Control Guidelines of Rakuno Gakuen University based on the Guide for
the Care and Use of Laboratory Animals of the National Institutes of Health in
the United States.
Expression of UDP-Glucuronosyltransferase 2B1. cDNA of rat
UDP-glucuronosyltransferase isoform UGT2B1 was obtained by reverse
transcriptase-polymerase chain reaction and expressed in yeast AH22 cells as
previously described (Yokota et al.,
1999
). Nonylphenol glucuronidation was performed using yeast
microsome-expressed UGT2B1, and the resultant glucuronide conjugate was
analyzed by HPLC as described previously
(Yokota et al., 1999
).
Surgical Procedure. The rats were anesthetized by intraperitoneal
injection of 60% urethane (0.3 ml/100 g of body weight). Whole liver perfusion
was performed according to the method reported by Sugano et al.
(1978
) with slight
modifications (Inoue et al.,
2001
). Briefly, after anesthesia, the abdomen was opened and the
liver, portal vein, bile duct, and inferior vena cava were exposed. The common
bile duct and the portal vein were cannulated with PE-10 and PE-50
polyethylene tubes (BD Biosciences, San Jose, CA), respectively, and
oxygenated Krebs-Ringer buffer, described below, was pumped through the liver
via the portal vein. The abdominal vena cava was incised immediately after
perfusion, and a dripping polyethylene tube (2 mm i.d., 3 mm o.d.) was
inserted. The thorax was then opened and the thoracic vena cava was ligated.
The liver was not excised. All experiments were performed in situ. While the
animals were still under anesthesia, euthanasia was performed by
exsanguination.
Liver Perfusion. Krebs-Ringer buffer (115 mM NaCl, 5.9 mM KCl, 1.2
mM MgCl2, 1.2 mM NaH2PO4, 1.2 mM
Na2SO4, 2.5 mM CaCl2, 25 mM
NaHCO3, 10 mM glucose) was used in all experiments. The buffer
solution was aerated by 95% O2 + 5% CO2, and the pH was
adjusted to 7.4. Ethanol containing alkylphenol was dispersed into the buffer
solution, and final concentration of ethanol was 1%. The substrate buffer
solution contained alkylphenol in a final concentration of 0.025 or 0.05 mM.
These buffer solutions were maintained in a water bath at 37°C. The
perfusion system consisted of a peristaltic pump (MP-32N; EYELA, Tokyo
Rikakikai Co. Ltd., Tokyo, Japan) and silicone tubes, as described in our
previous paper (Inoue et al.,
2001
). The buffer solution was pumped at a constant rate of 30
ml/min, and the liver perfusion was carried out in a flow-through mode.
Preliminary perfusion was done for 15 min, and then the substrate buffer
solution was perfused for 5 min, followed by reperfusion of the Krebs-Ringer
solution. After perfusion of the substrate buffer, the excreted bile and
perfusate in the vein were collected at 5-min or 10-min intervals over a 1-h
period.
HPLC Analysis of Reaction Products. The bile was dissolved in
40-fold 50% acetonitrile, and perfusate was diluted with an equal volume of
acetonitrile; then, the perfusate mixtures were centrifuged for 10 min at
10,000g. The supernatant fractions were analyzed by HPLC (Shimadzu,
Tokyo, Japan) according to the method described previously
(Yokota et al., 1999
;
Inoue et al., 2001
).
Alkylphenols and its metabolites were eluted from HPLC by 75% acetonitorile
solution (acetonitrile/water/acetic acid, 75:25:0.1) for nonylphenol, 60%
solution for hexylphenol, 50% solution for butylphenol, and 35% solution for
ethylphenol. Recordings were made using a C-R8A integrator (Shimadzu, Tokyo,
Japan). Alkylphenols and its metabolites retained in the liver after the
perfusion were extracted with acetonitrile, the extractions were centrifuged
for 30 min at 25,000g, and the supernatants were analyzed by HPLC
with the same procedure described above. Alkylphenol-glucuronides were
quantitated by the amount of the deconjugated free alkylphenols after
ß-glucuronidase treatment of the reaction products as previously
described (Shibata et al., 2002).
 |
Results
|
|---|
The HPLC profiles of the metabolites of nonylphenol produced in the liver,
after the perfusion had been performed as described under Materials and
Methods, are shown in Fig.
1. The nonylphenol metabolite extracted from the perfused liver
was eluted at an early retention time as a single peak
[nonylphenol-ß-D-glucuronide (NP-G); 7 min] with slight
shoulder peaks (Fig. 1B). The
main peak produced by liver microsomes had the same retention time and was
reduced by treatment with ß-glucuronidase as was previously reported in
rainbow trout (Lewis and Lech,
1996
; Coldham et al.,
1998
; Thibaut et al.,
1998a
,b
)
(data not shown). A glucuronide conjugate of nonylphenol was produced by
UGT2B1 (Fig. 1D), indicating
that the main metabolite in the liver perfusion is NP-G. The peak of NP
glucuronide was confirmed to be not produced by AH22 yeast microsomes,
expressing no UGT2B1, and in the enzyme reactions where the substrate was
omitted. The Km value of the microsomal
UDP-glucuronosyltransferase was estimated to be 0.25 mM nonylphenol.
UDP-glucuronosyltransferase activities (Vmax) toward
nonylphenol and other alkylphenols in rat liver microsomes were assayed, and
the estimated enzymatic activities are shown in
Fig. 2.
UDP-glucuronosyltransferase activity toward nonylphenol showed about the same
value as that of ethylphenol. These alkylphenols were injected into the portal
veins of rats, and then the bile and perfusate in the veins were sampled and
analyzed by HPLC as previously described
(Inoue et al., 2001
). The
resultant metabolites of alkylphenols were mainly glucuronide conjugates (data
not shown), as was the case for nonylphenol. The concentrations of the
glucuronide conjugates of alkylphenols in the bile and vein during liver
perfusion are shown in Fig. 3.
After the liver perfusion, alkylphenol-glucuronides were excreted only into
the bile (Fig. 3, AD),
and only ethylphenol-glucuronide was excreted into both the bile and vein
within 60 min (Fig. 3E). When
0.05 mM butylphenol and hexylphenol were perfused, these alkylphenols were
also glucuronidated in the liver, but these glucuronides were not excreted
completely from the liver within 60 min of perfusion
(Fig. 3B). Trace amounts of
nonylphenol-glucuronide were detected only in the bile
(Fig. 3, C and D). The
alkylphenols remaining in the livers after 1 h of perfusion were extracted as
described under Materials and Methods. The amounts of alkylphenols in
the liver and that excreted into bile and vein during 1 h of perfusion are
shown in Fig. 4. Recovery of
alkylphenols after the perfusions were about 50 to 60%
(Fig. 4). One of the reasons
for this is that it was supposed that all other alkylphenol metabolites such
as hydroxylated alkylphenols and conjugated alkylphenols with sulfate or
glutathione remaining in the liver tissue were not extracted with acetonitrile
completely, and/or these metabolites were not detected in this HPLC system.
Unconjugated alkylphenols remained in the liver tissue, and small amounts of
free alkylphenols were detected in the bile
(Fig. 4). About 800 to 1000
nmol of injected nonylphenol could be conjugated as a glucuronide by the rat
liver within 1 h of perfusion, but most of the glucuronide and free
nonylphenol remained in the liver (Fig.
4). Other alkylphenols having shorter alkyl chains were excreted
smoothly into the bile as glucuronides
(Fig. 4). These results
indicated that alkylphenols with shorter (including C6) alkyl chains were
easily excreted into the bile as glucuronides and that only the glucuronide
conjugate of nonylphenol, which has a longer C9 alkyl chain, was not easily
excreted from the liver. The metabolites of butylphenol and hexylphenol in
liver perfusion of EHBR, which are deficient in xenobiotic conjugates
transporter MRP-2, are shown in Fig.
5. These alkylphenols were excreted into the vein as glucuronides,
and only slight amounts of the metabolites were observed in the bile
(Fig. 5A). Rapid excretion and
clearance of butylphenol-glucuronide from the liver were observed
(Fig. 5, A and B). The
cumulative biliary excretion of the alkylphenol-glucuronides, which were
produced in the liver, was severely impaired in EHBR compared with SD rats,
indicating that alkylphenol-glucuronides were transported to the bile by
MRP-2.

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FIG. 1. HPLC profiles of nonylphenol metabolites after liver perfusion and
glucuronide conjugate of nonylphenol produced by UDP-glucuronosyltransferase
UGT2B1.
The liver was perfused for 60 min with Krebs' solution as a control (A).
Nonylphenol perfusion was performed with the same buffer containing 0.050 mM
nonylphenol for 5 min and then perfused with Krebs buffer for 55 min (B).
Nonylphenol and its metabolites in the liver were extracted with acetonitrile
and then analyzed by HPLC after the perfusion as described under Materials
and Methods. The UDP-glucuronosyltransferase isoform UGT2B1 was expressed
in yeast AH22 cells, and nonylphenol was glucuronidated by microsomes prepared
from the yeast transformant as described under Materials and Methods.
The enzyme reactions were performed for 0 min (C) and 60 min (D), and the
resultant glucuronide produced by UGT2B1 was analyzed by HPLC. The arrows
indicate NP-G and unconjugated nonylphenol (NP).
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FIG. 2. UDP-glucuronosyltransferse activities in rat liver microsomes toward
various alkylphenols.
The alkylphenols, ethylphenol (C2), butylphenol (C4), hexylphenol (C6), and
nonylphenol (C9), were incubated with rat liver microsomes, which was
activated by sodium cholate in the presence of UDP-glucuronic acid.
UDP-glucuronosyltransferase activities were determined by HPLC analysis as
described under Materials and Methods. Parameters are shown as means
± S.E. (n = 3 animals).
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FIG. 4. Alkylphenol metabolites in the bile, liver tissue, and vein after 1 h
of perfusion in SD rats.
Total amounts of alkylphenols and glucuronide conjugates, which were
excreted into the bile and vein and remained in the liver during a 60-min
period of liver perfusion, are shown. Numerals in the columns indicate the
percentages of respective metabolites, free ( ) or glucuronide conjugate
( ). Data are represented in the upper box (A) when 0.025 mM alkylphneol
was injected, in the lower box (B) when 0.050 mM nonylphenol was injected.
About 30% of injected alkylphenols were absorbed to the inside of the silicon
tubes during the perfusions. Recovery was calculated with the tube absorption
of each alkylphenol. Parameters are shown as means ± S.E. (n =
4 animals or n = 3 animals in ethylphenol analysis).
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FIG. 5. Excretion of alkylphenol metabolites during liver perfusion in
EHBR.
A, excretion of metabolites of butylphenol and hexylphenol during a 1-h
period of liver perfusion in EHBR, which have a hereditary defect in MRP-2. B,
total amounts of the alkylphenols and glucuronide conjugates excreted into the
bile and vein, and the total amount of those that remained in the liver during
the 60-min period of liver perfusion. Numerals in the columns indicate the
percentages of the respective metabolites (free, ; or glucuronide
conjugate, ). Parameters are shown as means ± S.E. (n = 4
animals).
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 |
Discussion
|
|---|
The disposition of alkylphenols and their metabolites was investigated in
SD rats and EHBR by a liver perfusion method. To determine the effects of
nonylphenol on animals, it is essential to elucidate the metabolic fate of
this compound. Various data on the metabolism and disposition of nonylphenol
in fishes are available. The major metabolite (about half of the injected
nonylphenol) in rainbow trout (O. mykiss) was excreted as a
glucuronide conjugate of nonylphenol (Thibaut et al.,
1998a
,b
),
and other metabolites, including glucuronide conjugates of ring- or side
chain-hydroxylated nonylphenol (Coldham et
al., 1998
), were detected. It has been reported that nonylphenol
was extensively metabolized to the glucuronide conjugate in rats
(Moffat et al., 2001
;
Doerge et al., 2002
). Doerge et
al. (2002
) have reported that
two glucuronide metabolites (NP-glucuronide and p-nonyl-catechol
glucuronide) were detected in the rat liver and serum after oral
administration. We detected NP-glucuronide as a major peak with slight
shoulder peaks after the liver perfusion. Other metabolites may be contained
in the shoulder peaks. In this study, rat hepatocytes showed a significant
capability for glucuronidation of nonylphenol of about 800 to 1000 nmol/h by
liver perfusion, but the transport of the nonylphenol-glucuronide across the
canalicular membrane into the bile was delayed. These findings suggest that
nonylphenol glucuronidation is mediated by UDP-glucuronosyltransferase
isoform(s), such as UGT2B1, with high activity but that the resultant
glucuronide having a long (C9) alkyl chain could not be transported by
MRP-2.
The substrate specificity of MRP-2 has been studied by comparing the
transportation activity across the bile canalicular membrane in normal rats
with that in transport-deficient rats
(Paulusma et al., 1996
) or in
EHBR, which have a hereditary defect in MRP-2
(Fernandez-Checa et al., 1992
;
Takenaka et al., 1995
;
Yamazaki et al., 1996
). It has
been demonstrated that glutathione conjugates, glucuronides of xenobiotics,
sulfates of several bile acids, and some organic anions are substrates for
MRP-2, but the mechanism of the transport and the substrate specificity of the
transporter have not been clarified yet. In this study, it was found that
transportation activity of MRP-2 decreased with increase in the number of
alkyl chains of alkylphenols, suggesting that after MRP-2 recognizes or binds
to the glucuronic acid anion, the long alkyl chain of alkylphenol-glucuronide
disturbs the transportation across the membrane. The transporter, which
mediates the transportation of glucuronides into the vein from liver cells,
can transport only an ethylphenol-glucuronide having the shortest alkyl chain,
indicating that metabolic distribution and excretion of alkylphenol is caused
by the length of the alkyl chain. It has been shown that MRP-2 has
transportation activity of glucuronide conjugates of various xenobiotics
having large molecular mass (Yamazaki et
al., 1996
), suggesting that inability of MRP-2 to transport
nonylphenol-glucuronide is due to the shape or hydrophobicity of the long (C9)
alkyl chain.
Finally, nonylphenol has been shown to reduce the level of CYP1A1
expression in murine Hepa-1c1c7 cells
(Jeong et al., 2001
) and to
inhibit in vitro CYP1A1 activity in rat liver microsomes
(Lee et al., 1996
) and
activities of human cytochrome P450s, including steroidogeneic CYP17
activities (Niwa et al.,
2002
). Oral administration of nonylphenol decreased hepatic
testosterone hydroxylation and CYP2C expression level
(Laurenzana et al., 2002
).
Estradiol binding to the estradiol receptor (ER) was significantly inhibited
by nonylphenol (Danzo, 1997
).
These results suggest the possible inhibition of cytochrome P450s and ER
functions by nonylphenol, which delays excretion from the liver.
One of the toxicological implications for the delay of excretion of
nonylphenol and nonylphenol-glucuronide is estimated to the binding to and
inhibition of ER (Tabira et al.,
1999
); another is the inhibition of MRP-2 which excretes various
glucuronides such as estradiol glucuronide
(Ito et al., 2001
) and
bilirubin glucuronide (Kusuhara et al.,
1998
). The delay of nonylphenol excretion is possible because of
the adverse effects of nonylphenol on rat reproductive systems
(Laws et al., 2000
).
 |
Footnotes
|
|---|
1 Abbreviations used are: HPLC, high-performance liquid chromatography; SD,
Sprague-Dawley; EHBR, Eisai hyperbilirubinemic rats; MRP-2, multidrug
resistance-related protein-2; NP-G,
nonylphenol-ß-D-glucuronide; NP, nonylphenol; ER, estrogen
receptor. 
Address correspondence to: Hiroshi Yokota, Department of Veterinary
Biochemistry, School of Veterinary Medicine, Rakuno Gakuen University, Ebetsu,
Hokkaido, 069-8501 Japan. E-mail:
h-yokota{at}rakuno.ac.jp
 |
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