![]() |
|
|
Vol. 287, Issue 1, 13-20, October 1998
Physiologisches Institut, Universität Würzburg, Würzburg, Germany
| |
Abstract |
|---|
|
|
|---|
Ochratoxin A (OTA) is a widespread mycotoxin, which is nephrotoxic and
carcinogenic. Because a decline in net-secretion of para-aminohippuric acid (PAH) was observed after chronic OTA
exposition in vivo, we investigated the effect of OTA on
proximal-tubule-derived opossum kidney (OK) cells. OTA up to
10
5 mol/liter had no acute effect on PAH transport when
bovine serum albumin (BSA) was present. By contrast, 72-hr incubation
of OK cells led to a decrease of PAH transport with half-maximal
inhibition at 6 · 10
7 mol/liter for
transepithelial secretion and 6 · 10
8 mol/liter
for basolateral uptake of PAH. Incubation of OK cells with
10
6 mol/liter OTA for 72 hr reduced the affinity of PAH
uptake, and decreased the maximum secretion rate to one-fifth of
control values. Apical uptake of amino acids and basolateral uptake of
glutarate were not affected. In addition, no signs of general toxic
action could be observed. Specific basolateral binding affinity of PAH was reduced to 50% of control. Furthermore, incubation with OTA led to
a decrease of PAH efflux across the apical membrane, although efflux
across the basolateral membrane and the amount remaining in the cells
increased as compared to control. By contrast to control cells, uptake
of PAH in OTA-treated cells was not stimulated after preloading with
glutarate. Our data show, that 1) long-term incubation with free OTA in
the nanomolar range reduces the activity of the organic anion
transporter, 2) without influencing general cell function. 3) OTA seems
to act preferentially on organic anion transport, by affecting the
exchange of organic anions and dicarboxylates. 4) Thereby, OTA
reduces its own secretion. 5) The excretion of other xenobiotics and
drugs may be also impaired, whereby OTA can exert an indirect toxic
action.
| |
Introduction |
|---|
|
|
|---|
OTA
is a mycotoxin produced as a secondary metabolite in different species
of Aspergillus and Penicillium (Harwig et al., 1983
). These
species often occur in improperly stored food and animal chow (Delacruz
and Bach, 1990
; Bauer and Gareis, 1987
). OTA is nephrotoxic,
carcinogenic (Bauer and Gareis, 1987
; Krogh et al., 1974
)
and has been unmasked as the agents responsible for the Danish porcine
nephropathy (Delacruz and Bach, 1990
; Krogh et al., 1974
).
Furthermore, there is epidemic evidence for an important role of OTA in
the development of the BEN (Radic et al., 1997
;
Petkova-Bocharova and Castegnaro, 1991
; Kuiper-Goodman and Scott, 1989
)
and for the increased incidence of urinary tract tumors in areas with
high occurrence of OTA (Nikolov et al., 1996
). Recent
studies in Tunisia indicate that OTA may also play a role in the
development of CIN (Maaroufi et al., 1995
), a disease
similar to BEN (Berndt et al., 1980
). Because it is becoming
more and more evident that the complete avoidance of OTA exposure to
humans is impossible, it is necessary to improve our knowledge of the toxodynamics and toxicokinetics of OTA. Millimolar concentrations of
OTA were found to be acutely toxic, leading to inhibition of mRNA
synthesis (Meisner and Polsinelli, 1986
), inhibition of
phenylalanyl-tRNA-synthetase (Creppy et al., 1983
; Roth
et al., 1989
), protein synthesis (Baudrimont et
al., 1997
) and DNA-damage (Kane et al., 1986
). OTA
concentrations detected in context with the above mentioned diseases,
however, were in the nano- to micromolar range (Kuiper-Goodman and
Scott, 1989
). Chronic treatment of rats with naturally occurring doses of OTA led to a reduced renal clearance and renal secretion of PAH
(Gekle and Silbernagl, 1993
; Gekle and Silbernagl, 1994
). These data
point to an inhibitory effect of OTA on the activity of the renal
organic anion transporter in the nano- to micromolar range, because PAH
is the classical substrate for this transporter.
The organic anion transport system of the proximal tubule of the kidney
plays a crucial role in the excretion of a variety of potentially toxic
compounds, such as endogenous metabolites or xenobiotics (Friis, 1991
).
This is also true for OTA, because it is also a substrate of the
organic anion transport system (Gekle et al., 1993
; Delacruz
and Bach, 1990
). The organic anion transport system consists of the
basolaterally located organic anion exchanger and a less well
characterized transport step across the apical membrane (Dantzler,
1996
). The basolateral organic anion exchanger is a tertiary active
transport system dependent on the maintenance of the inward-directed
Na+-gradient to drive uptake of
-KG. Subsequently,
-KG is exchanged for PAH, or any other competitive organic anion,
driving their uptake across the basolateral membrane (Pritchard and
Miller, 1992
; Dantzler, 1996
; Ullrich and Rumrich, 1988
; Friis, 1991
). Apical secretion of PAH is along its electrochemical gradient and is
carrier-mediated (Friis, 1991
). The above mentioned transport steps are
of major importance for the elimination of xenobiotics or metabolites
that are organic anions (Friis, 1991
).
To investigate the effect of OTA on the organic anion transporter in
more detail and without possible systemic interactions [e.g., renal
blood flow (Gekle and Silbernagl, 1993
)] we used a proximal
tubule-derived cell line (OK cells). The OK cell line is well
characterized and an accepted model system to investigate organic anion
secretion (Nagai et al., 1995
; Hori et al.,
1993
).
Our data show that incubation of OK cells with nano- to micromolar concentrations of OTA for 1 to 3 days leads to a dose-dependent decrease of basolateral uptake and transepithelial secretion of PAH. Cell viability and other energy-depending transport systems were not or only to a very minor extent affected in this concentration range. Thus, OTA can inhibit its own elimination and the elimination of other xenobiotics in a specific way and by a mechanism that is not disturbing cellular function in general.
| |
Materials and Methods |
|---|
|
|
|---|
Cell culture.
OK cells were obtained from Dr. Biber,
Department of Physiology, University of Zurich. Cells were maintained
in culture at 37°C in a humidified 5% CO2, 95% air
atmosphere. The growth medium was minimal essential medium, pH 7.4, supplemented with Earl's salts, nonessential amino acids, 10% (v/v)
fetal calf serum (Biochrom KG, 12213 Berlin, FRG) and 26 mmol/liter
NaHCO3. Cells were cultured on permeable supports (3-µm
pore diameter, Falcon, Becton Dickinson Labware, Franklin Lakes, NJ)
for transport measurements. The effective growth area on one permeable
support was 4.3 cm2/filter. All studies were performed
between passage 60 and 100. The seeding density was 0.4 · 106 cm
2. The medium was changed every third
day and the monolayers were used for experiments 4 to 7 days after
reaching confluence.
Transport measurements.
The volumes of the apical and
basolateral compartment were 1.3 ml and 2.5 ml to avoid hydrostatic
pressure differences. Before each experiment, the cells were washed
three times with PBS (138 mmol/liter NaCl, 1 mmol/liter
NaH2PO4, 4 mmol/liter
Na2HPO4, 4 mmol/liter KCl, 1 mmol/liter
MgCl2, 1 mmol/liter CaCl2, 5 mmol/liter glucose, pH 7.4). Unless otherwise stated, transport measurements were
performed in PBS at pH 7.4 and 37°C for 30 min. The concentrations of
the radio-labeled substrates were as follows: [14C]PAH:
1.5 · 10
6 mol/liter, [14C]TEA:
7.5 · 10
6 mol/liter, [14C]glutarate:
1.5 · 10
6 mol/liter,
[14C]cycloleucine: 1.5 · 10
6
mol/liter, [3H]-OTA: 10
6 mol/liter. The
corresponding concentrations of unlabeled substrates, if used, are
mentioned in the text. Correction of paracellular fluxes and
measurement of extracellular water space was performed with
[3H]mannitol (55 · 10
9 mol/liter) or
[14C]mannitol (6.2 · 10
9 mol/liter).
At the end of the experiment, the apical and basolateral solutions were
collected. Subsequently, the cells were washed twice with ice-cold PBS.
Radioactivity of the solutions and the cells was measured using a
liquid scintillation counter (Packard Instruments, Frankfurt, Germany).
3 mol/liter
glutarate for 10 min. After washing them twice with ice-cold PBS,
transport of [14C]PAH was measured for 5 min.
To investigate PAH efflux, the cells were incubated in PBS (37°C)
containing 1.5 · 10
6 mol/liter
[14C]PAH for 60 min. After washing the cells with
ice-cold PBS twice, the efflux was determined during the first 10 min.
Apical and basolateral solutions and the cellular compartment were
collected separately. Radioactivity in the solutions and the cells was
measured by liquid scintillation counting.
Specific binding.
To investigate binding of
[14C]PAH to the plasma membrane, cells were incubated
with 1.5 · 10
6 mol/liter [14C]PAH at
4°C for 60 min. Cells were washed twice with ice-cold PBS and apical
and basolateral solutions and cellular compartment were collected
separately afterward. Specific binding of [14C]PAH was
calculated as the difference between binding of 1.5 · 10
6 mol/liter [14C]PAH (alone or in
presence of a certain amount unlabeled PAH) and binding of 1.5 · 10
6 mol/liter [14C]PAH in presence of 15 mmol/liter PAH. Kinetic data were calculated as described for transport
kinetics.
Amino acid.
Protein biosynthesis was determined by the
incorporation of [14C]L-phenylalanine
according to Ling et al. (1996)
. Three days after reaching
confluence, cells were incubated with MEM containing 10
6
mol/liter OTA for 72 hr. 0.15 mBq
[14C]L-phenylalanine was present during the
last 12 hr.
Other experimental methods.
For determination of
K+-content (Montrose and Murer, 1996
), cells were seeded in
6-well culture dishes. The seeding density and performance of
incubation was as mentioned before. The epithelia were washed twice
with ice-cold washing buffer (130 · 10
3 mol/liter
TEA-Cl; 10
3 mol/liter MgCl2;
10
3 mol/liter EGTA; 10
2 mol/liter HEPES;
20 · 10
3 mol/liter BaCl2; pH 7.4).
After detaching the cells with perchloric acid (10%), the probes were
centrifuged. The supernatant was investigated using flame photometry
(Flammenphotometer Eppendorf, Hamburg, Germany). The protein
concentrations were determined using the method of Lowry et
al. (1951)
. LDH release was measured according to Roth et
al. (1989)
at room temperature in a photometer.
Analysis of kinetic data.
Kinetic data (affinity, transport
maximum) were obtained by fitting the values to the Michaelis-Menten
equation according to the least-square-method, using Sigma Plot
Software (Jandel Corte Madera, CA). IC50 values were
determined according to Delean et al. (1978)
by the
equation:
|
Data analysis. Data are presented as mean ± S.E.M., except for Vmax, Km and IC50 which are presented as ±S.D. n is given in the text or in the figures. n is the number of culture plates or filters used to perform the measurements. All data shown contain values from at least two different passages of cells. Statistical significance was determined by unpaired Student's t test. Results were considered statistically different at P < .05. The data were fitted using the least-square-method (Sigma Plot, Jandel Corte Madera, CA).
Materials. [14C]PAH (55 mCi/mmol), [14C]TEA (5 mCi/mmol), [14C]glutarate (55 mCi/mmol), [14C]cycloleucine (55 mCi/mmol), [14C]L-phenylalanine (475 mCi/mmol), [14C]mannitol (56 mCi/mmol), [3H]mannitol (15 mCi/mmol) and [3H]thymidine (6.7 mCi/mmol) were purchased from American Radiolabeled Chemicals Inc., St. Louis, MO. [3H]OTA (6 mCi/mmol) from Moravek Biochemicals Inc. Brea, CA and [14C]mannitol (51.5 mCi/mmol) from Du Pont De Nemours (Germany) GmbH. If not stated otherwise, all other chemicals were from Sigma.
| |
Results |
|---|
|
|
|---|
Kinetics of the organic anion transport system.
First we
determined the kinetic parameters of specific organic anion transport
in OK cell epithelia under control conditions. Calculated data were
Vmax = 578 ± 20 (pmol · cm
2
· 30 min
1), Km = 248 ± 21 (µmol/liter) for basolateral uptake (fig.
1A) and Vmax = 490 ± 82 (pmol · cm
2 · 30 min
1),
Km = 36 ± 17 (µmol/liter) for
transepithelial secretion (fig. 1B). These data are in good agreement
with data published previously (Hori et al., 1993
).
|
Effect of acute OTA exposure.
As 99% or more of OTA binds to
plasma albumin (Hagelberg et al., 1989
; Delacruz and Bach,
1990
), we investigated the effect of acute OTA exposure in the absence
and presence of BSA in the bath. We have chosen a concentration of 4 g/liter BSA, according to the amount of BSA in the growth medium used
in cell culture. Up to 10
6 mol/liter OTA were added
simultaneously with 1.5 · 10
6 mol/l
[14C]PAH to the bath on the basolateral side of OK cell
epithelia in the presence or absence of 4 g/liter BSA. As shown in
figure 2, 10
6 and
10
5 mol/liter OTA had no acute effect on transepithelial
secretion of [14C]PAH in the presence of BSA, whereas in
the absence of BSA, secretion was inhibited by 20 and 80%,
respectively. A total of 10
7 mol/liter OTA exerted no
acute effect. Uptake of PAH was affected in the same way as secretion.
To test whether this acute effect is due to specific competitive action
of free OTA on organic anion transport, we investigated the acute
effect of OTA on TEA transport. As shown in figure
3B, up to 10
5 mol/liter
free OTA did not alter basolateral uptake of organic cations in OK
cells. Transepithelial secretion of TEA was also not affected (fig.
3A).
|
|
Intracellular OTA concentration during acute exposure.
To
estimate the amount of OTA present in the cells during 30 min exposure,
uptake of [3H]OTA (10
6 mol/liter) was
determined. The resulting intracellular concentration of
[3H]OTA was 1.1 · 10
6 ± 10
7 mol/liter (n = 6).
Time course of chronic OTA exposure.
As OTA had no effect when
applied acutely, we incubated the cells with 10
6
mol/liter OTA for different time periods. As seen in figure
4, basolateral PAH uptake was already
decreased significantly after 24 hr. Maximum inhibition was reached
after 48 hr. All subsequent experiments were performed after 72 hr
incubation.
|
Kinetics and extent of inhibition.
Figure
5 shows uptake (fig. 5A) and secretion
(fig. 5B) of [14C]PAH after 72 hr incubation of OK cells
with OTA. Determined IC50 values were 6 · 10
7 ± 2 · 10
7 mol/liter for
transepithelial secretion and 6 · 10
8 ± 5 · 10
8 mol/liter for basolateral uptake of PAH. Maximum
inhibition was almost 100% for transepithelial secretion and 60% for
basolateral uptake. Because 10
6 mol/liter OTA leads to
almost maximum inhibition with virtually no reduction of cell viability
(see below), this concentration was used in all subsequent experiments.
A total of 10
5 mol/liter OTA was the highest
concentration tested. There, epithelia started to show a massive
decrease in tightness, as determined by mannitol fluxes (see below).
|
6 mol/liter OTA for 72 hr
altered the kinetic parameters of transepithelial secretion and
basolateral uptake of PAH. As shown in table
1, incubation led to a 2-fold increase of
Km for basolateral uptake, but only to a slight
decrease of Vmax. For secretion, Vmax dropped
to nearly one third of control, while the Km
value was not altered in cells incubated with OTA.
|
Specific basolateral binding of PAH.
We also investigated
specific binding of [14C]PAH to the basolateral membrane
of OK cells. As shown in table 1, 72 hr preincubation with OTA
(10
6 mol/liter) induced a 50% decrease in affinity of
specific basolateral binding of PAH. Similar to Vmax for
basolateral uptake, the maximal basolateral binding was not changed
after OTA incubation. Thus, although kinetic data for basolateral
uptake were gained in the saturation phase, we conclude that this
effect is the same in the initial phase. Secretion of PAH was still
linear after 30 min.
OTA concentrations after 72 hr incubation.
To determine the
amount of OTA remaining within the cells after 72 hr incubation
followed by the standard washing procedures, we incubated OK cells with
10
6 mol/liter [3H]OTA for 72 hr. After the
standard washing and equilibrating procedures, the amount of OTA left
in the intra- and extracellular compartment was determined.
Intracellular OTA concentration was 1.8 · 10
7 ± 0.2 · 10
7 mol/liter and the extracellular
concentration was 17.4 · 10
11 ± 1.4 · 10
11 mol/liter (n = 6 for both). No
metabolites of OTA were detectable after 72 hr, as determined by
high-performance liquid chromatography analysis (data not shown).
Specificity of the OTA effect.
To gain information about the
specificity of the effect of the 72 hr OTA incubation, we determined
the activity of three other transport systems expressed in proximal
tubular cells: the apically located transporter for neutral amino acids
(Schwegler et al., 1989
), the basolaterally located organic
cation transporter (Pritchard and Miller, 1992
) and the
Na+/dicarboxylate cotransporter (see below). As shown in
figure 6 neither basolateral uptake of
glutarate, nor apical uptake of cycloleucine was affected by incubation
with 10
6 mol/liter OTA for 72 hr. Intracellular
cycloleucine concentration exceeded the extracellular concentration
4-fold, indicating that cycloleucine accumulates. Accumulation is an
active transport process requiring metabolic energy. As intracellular
accumulation of cycloleucine did not change after treatment with
10
6 mol/liter OTA for 72 hr, a general disturbance of the
metabolic state of the cells seems to be unlikely. To our surprise,
TEA-uptake was reduced to 36 ± 9% of control (n = 7) after 72 hr OTA incubation, whereas transepithelial secretion of
TEA was not affected (fig. 7). At the
moment we can only speculate about possible reasons for this
discrepancy (see "Discussion").
|
|
3 mol/liter glutarate for 10 min
resulted in an increase of PAH uptake after 5 min of
[14C]-PAH present in the basolateral bath. After
treatment with 10
6 mol/liter OTA for 72 hr, the same
glutarate preload did not stimulate [14C]PAH uptake.
Uptake of [14C]glutarate after 10 min was not affected by
incubation with OTA (fig. 6B). As OK cells are glycolytic when kept in
culture (Gstraunthaler et al., 1993
-ketoglutarate, we consider these
results as further evidence that OTA induced reduction of PAH uptake is
not due to an impaired availability of substrates for countertransport.
One can assume that preloaded cells contain the same amount of
glutarate no matter if treated with OTA or not. We consider this as a
further evidence for the rather specific action of OTA on the exchange
step of dicarboxylates and organic anions.
|
Cell viability.
Furthermore, we investigated cell viability
and epithelial tightness by determination of protein content, LDH
release and mannitol flux. As shown in table
2, incubation with 10
6
mol/liter OTA for 3 days did not reduce protein content per filter or
LDH release. Paracellular permeability, as measured by mannitol fluxes,
was only slightly increased by incubation with 10
6
mol/liter OTA. Cellular K+-content was slightly increased.
Incorporation of [14C]L-phenylalanine was not
affected by OTA treatment. Incubation with 10
5 mol/liter
OTA for 72 hr led to a massive reduction of protein content and
epithelial tightness. These data indicate that treatment with
10
6 mol/liter OTA for 72 hr does not, or only to a very
minor extent, impair general viability and epithelial integrity of OK
cells.
|
Efflux of PAH.
Finally we determined whether treatment of OK
cells with 10
6 mol/liter OTA for 72 hr affects
[14C]PAH efflux. As shown in figure
9, OTA treatment led to a reduction of
PAH efflux into the apical compartment. Furthermore a greater fraction
of PAH remained within the OK cells and was extruded into the
basolateral compartment. Thus, as a functional consequence of OTA
incubation, transport mechanisms at the basolateral and at the apical
side seem to be altered in proximal-tubular cells.
|
| |
Discussion |
|---|
|
|
|---|
Many of the effects of OTA described previously, were studied in a
concentration range which exceeds the naturally occurring one
(Kuiper-Goodman and Scott, 1989
). The inhibition of
phenylalanyl-tRNA-synthetase is reported to occur at concentrations
above 10
4 mol/liter (Baudrimont et al., 1997
).
DNA-damage is induced by 10
4 mol OTA per kg body weight
(Kane et al., 1986
). Natural occurring concentrations of OTA
are in the range of 10
13 to 10
8 mol/liter
in human plasma in Germany (Deutsche Forschungsgemeinschaft, 1990
) or
up to 10
5 mol/liter in plasma samples from people in
Bulgaria and Yugoslavia (Delacruz and Bach, 1990
), countries with areas
of high incidence of BEN. The free OTA concentration is about
one-hundred times lower as compared to total OTA concentration. It has
been shown that the incidence of urinary tract tumors is seven to nine
times higher in BEN areas, than it is in nonendemic areas (Nikolov
et al., 1996
). Because OTA exposure seems to be unavoidable,
it is important to investigate effects of OTA in the nano- to
micromolar range, to gain more information about the nephrotoxic action
during natural exposures. Recent studies (Bruinink et al.,
1997
) showing toxic effects of OTA in the nanomolar concentration range
underline this importance. This is additionally underlined by a study
that indicates no relevant inhibition of phenylalanyl-tRNA-synthetase by naturally occurring OTA concentrations in vivo (Roth
et al., 1993
).
The polyspecific organic anion carrier of the kidney is of crucial
importance for the excretion of a variety of potentially toxic
compounds such as e.g., metabolites, xenobiotics and drugs (Friis, 1991
; Ullrich and Rumrich, 1988
; Pritchard and Miller, 1992
).
OTA itself is a substrate for the organic anion transport system (Sokol
et al., 1988
; Gekle et al., 1993
; Delacruz and
Bach, 1990
). In vivo studies in rats showed a reduced renal
secretion and clearance of PAH after subchronic (6 days) OTA exposure
(Gekle and Silbernagl, 1994
), indicating that the renal organic anion transport system may be a target of OTA toxicity. Impairment of organic
anion secretion by OTA affects kinetics of a variety of substances,
thereby possibly leading to indirect toxic effects.
Basolateral uptake and secretion of PAH are clearly saturable in OK
cells. The kinetic parameters for uptake and secretion are in the same
range as described previously (Hori et al., 1993
). Because
total estimated cell volume per filter was 2.5 · 10
6 liter, the intracellular concentration of PAH is
about 2.5 · 10
6 mol/liter. Thus, under our
conditions, PAH was accumulated 1.7-fold within the cells, indicating
(tertiary) active uptake.
In the absence of proteins, acute exposure to OTA reduced PAH
transport. This inhibition was totally abolished by adding 4 g/liter
BSA. We used this concentration of BSA, because it corresponds to the
concentration in media containing 10% FCS, which are used under
standard cell culture conditions as well as when the cells were
incubated for 72 hr with OTA. The fact that BSA was able to avoid acute
effects of OTA on PAH transport completely, is explained by binding of
OTA to BSA (Stojkovic et al., 1984
; Chu, 1971
). Similar
observations have been made for the action of OTA on growth of rat
proximal tubular cells (Gekle et al., 1995
). Our experiments
show, that in presence of BSA, OTA in concentrations up to
10
5 mol/liter did not acutely influence PAH transport. We
conclude that the inhibitory effect of acute OTA application in the
absence of BSA is just due to competitive inhibition as suggested by
Sokol et al. (1988)
, because both, OTA and PAH, are
substrates for the organic anion transporter (Gekle et al.,
1993
).
By contrast, the sensitivity of the organic anion transporter to
long-term exposure (72 hr) was much higher. The half-maximal inhibitory
concentration (IC50) for basolateral uptake was 6 · 10
8 mol/liter. During evaluation of the data obtained
after OTA incubation it is important to keep in mind, that BSA was
always present during the incubation period. Thus, the estimated
concentrations of free OTA (Stojkovic et al., 1984
; Chu,
1971
) inducing half-maximal inhibition of PAH transport are
~10
10 mol/liter. Thus, the sensitivity during long-term
exposure is at least three orders of magnitude higher as compared to
acute exposure in the presence of BSA. Furthermore, the effect of OTA was maximal only after 48 hr. These data are strong evidences that the
mechanisms acting during long-term exposure are different from those
acting during acute exposure (competitive inhibition). For competitive
inhibition of PAH transport, the crucial parameter is the OTA
concentration in the extracellular medium. At the beginning of the
transport experiments, after standard OTA incubation, the extracellular
concentration of OTA is about three orders of magnitude lower than
10
7 mol/liter. OTA at 10
7 mol/liter had no
effect during acute exposure. Thus, OTA was no longer present in
concentrations that can lead to competition with PAH when PAH transport
was determined after long-term incubation.
Incubation of OK cells with 10
6 mol/liter or
10
5 mol/liter PAH for 3 days did not affect organic anion
uptake (91 ± 11, respectively 93 ± 4, values in % of
control; n = 3). This indicates that the described
effect of OTA is not due to physiological down-regulation of organic
anion transport when OK cells are exposed to any substrate of the
organic anion carrier. However, the data do not exclude the possibility
that PAH at higher concentrations leads to down regulation of the
organic anion carrier. As the task of the organic anion transport
system of the kidney is to excrete organic anions constitutively, a
downregulation would make no physiological sense. Thus, the impairment
of organic anion transport observed after long term incubation is a
specific pathophysiological property of OTA.
As OTA affects the organic anion transport, it was of interest to see
whether OTA also affects other transport systems in the concentration
range tested. Because neither the apical uptake of the neutral amino
acid cycloleucine nor the basolateral uptake of glutarate was impaired,
OTA does not affect transport systems in general. The reduction of TEA
uptake is in agreement with data published before (Berndt et
al., 1980
). Additionally recent data (Wolff et al.,
1997
) show some identity (33% respectively 32% in amino acid
sequence) of the organic anion transporter (OAT1) and the organic
cation transporter (OCT1 resp. OCT2). As organic cation transport is
not acutely affected by OTA, one can speculate that the mechanism of
the long-term action of OTA is related to these sequence identities.
However, the organic cation transporter is specific enough to exclude a
direct competition of TEA and OTA. This hypothesis will be tested in
future investigations. Furthermore, the energy-dependent enrichment of
cycloleucine still occurs to the same extent as compared to controls,
indicating that OTA does not disturb cell metabolism in general. This
hypothesis is also supported by the results from our glutarate-preload
experiments. Glutarate is a nonmetabolizable analogue of
-ketoglutarate and acts as a counterion for the organic anion
transporter (Dantzler, 1996
). PAH uptake was stimulated by glutarate in
untreated OK-cells. If OTA incubation would lead to a decrease in
metabolic activity of the cells and thereby reduce the availability of
counterions, glutarate-preload should restore PAH uptake at least in
part. Yet, our data show that glutarate-preload had no effect. As
already mentioned above, uptake of glutarate was not changed after
incubation with OTA. These data indicate that OTA incubation affects
the PAH/dicarboxylate-exchanger directly and does not act via a change of driving forces. Otherwise, glutarate-preloading should have stimulated PAH uptake.
The K+-content of OK cells was not reduced by OTA, again
reinforcing the conclusion that OTA incubation does not act on cellular energy homeostasis. As described above, primary metabolism of the cells
seems not to be affected by incubation with 10
6 mol/liter
OTA for 72 hr. Furthermore, this treatment did not reduce the protein
content per filter (table 2) or protein synthesis. In fact a slight
increase in protein content was observed, which is in agreement with
published data showing a hypertrophic effect of OTA (Gekle et
al., 1995
). OTA incubation did not reduce cell membrane integrity
as shown by the lack of effect on LDH release. The slight increase of
mannitol flux points at a small decrease in epithelial tightness since
mannitol moves only via the paracellular space (Suki and Eknoyan,
1992
). By contrast, 72 hr exposure to 10
5 mol/liter OTA
led to 25% decrease in protein content and to a 28% decrease in
epithelial tightness. Hence, this concentration seems to mark the
transition to unspecific toxic effects as it was observed in rat
proximal tubular cells (Gekle et al., 1995
).
Affinity of basolateral uptake decreased after OTA incubation (table
1), whereas Vmax remained unchanged. This could be due to
reduced affinity of the organic anion transporter protein for PAH.
Another possible reason could be a reduced accessibility of the
transporter for the substrate. Furthermore, the translocation step
could be impaired or the dissociation of the substrate from the carrier
could be hindered. To gain further information about the mechanism and
the site of the OTA effect, we investigated specific binding of PAH to
the basolateral membrane of OK cells. Affinity of basolateral binding
was reduced to 50% after 72 hr of incubation with 10
6
mol/liter OTA, whereas maximal binding was not altered. These data are
in agreement with the kinetic data for basolateral uptake of PAH
mentioned above. Thus, the specific binding sites (i.e., carrier proteins) at the basolateral membrane seem to be affected by
OTA. OTA treatment could lead to a reduced synthesis of binding sites.
Furthermore, missorting of the protein, in a sense that it is not only
directed to the basolateral membrane but also to the apical membrane,
could also reduce the number of basolateral binding sites. Because
maximal binding and overall protein synthesis were not reduced, we
think that these possibilities are highly unlikely. Possible mechanisms
leading to reduced affinity include changes in the confirmation of the
carrier or the microenvironment surrounding the carrier. In addition
OTA could act on the regulation of the organic anion transporter,
e.g., by PKC (Takano et al., 1996
; Nagai et
al., 1997
). Yet, as PKC is a general regulatory protein, it seems
unlikely that the specific OTA effects described here, are mediated by
PKC alone. Future studies will have to unveil a possible involvement of
PKC in OTA-induced transport inhibition. Although the precise mechanism
of action still has to be unveiled, our data clearly show that OTA
affects directly organic anion/dicarboxylate exchange via a decrease of
substrate affinity.
OTA incubation reduces organic anion efflux across the apical membrane,
and increases the efflux across the basolateral membrane (fig. 9).
Thus, OTA seems to also act on transport processes at the apical
membrane. This dual effect of OTA could explain the fact that the
kinetic parameters of uptake and secretion are altered in a different
way by OTA. Additionally, the secretion data are in good agreement with
the reduction of organic anion secretion in vivo (Gekle and
Silbernagl, 1994
).
The renal organic anion transport system is responsible for the
blood-to-lumen transport of OTA (Gekle et al., 1993
;
Delacruz and Bach, 1990
). Thus, this mycotoxin delays its own
elimination by reducing the activity of this transport system. Our data
show that it is the exchange of dicarboxylates and organic anions that is affected by nanomolar concentrations of OTA and not dicarboxylate uptake or the sodium pump. Organic cation uptake, which is mediated by
a transporter with similarities in sequence to the organic anion
transporter, is also impaired by OTA incubation. Additionally, OTA
alters transport of organic anions at the apical membrane. The reduced
secretion may also contribute to the reported elimination half-lives of
OTA which are in the range of several hundred hours in mammals
(Hagelberg et al., 1989
). Thus, OTA has a self-enhancing effect. Furthermore, OTA delays the elimination of other substances and
thereby may cause indirect toxic action.
| |
Footnotes |
|---|
Accepted for publication May 15, 1998.
Received for publication December 19, 1997.
1 This work was supported by the Deutsche Forschungsgemeinschaft, DFG Grant Si 170/7-2 and Ge 905/3-3.
Send reprint requests to: Dr. Christoph Sauvant, Physiologisches Institut, Universität Würzburg, Röntgenring 9, 97070 Würzburg, Germany.
| |
Abbreviations |
|---|
-KG,
-ketoglutarate;
BEN, Balkan endemic
nephropathy;
BSA, bovine serum albumin;
CIN, chronic interstitial
nephropathy;
FCS, fetal calf serum;
OAT, organic anion transporter;
OCT, organic cation transporter;
OK cells, opossum kidney cells;
OTA, ochratoxin A;
PAH, para-aminohippuric acid;
PKC, protein
kinase C;
TEA, tetraethylammonium;
LDH, lactate dehydrogenase.
| |
References |
|---|
|
|
|---|
This article has been cited by other articles:
![]() |
C. Sauvant, H. Holzinger, and M. Gekle Prostaglandin E2 Inhibits Its Own Renal Transport by Downregulation of Organic Anion Transporters rOAT1 and rOAT3 J. Am. Soc. Nephrol., January 1, 2006; 17(1): 46 - 53. [Abstract] [Full Text] [PDF] |
||||
![]() |
C. Sauvant, H. Holzinger, and M. Gekle Proximal Tubular Toxicity of Ochratoxin A Is Amplified by Simultaneous Inhibition of the Extracellular Signal-Regulated Kinases 1/2 J. Pharmacol. Exp. Ther., April 1, 2005; 313(1): 234 - 241. [Abstract] [Full Text] [PDF] |
||||
![]() |
C. Sauvant, D. Hesse, H. Holzinger, K. K. Evans, W. H. Dantzler, and M. Gekle Action of EGF and PGE2 on basolateral organic anion uptake in rabbit proximal renal tubules and hOAT1 expressed in human kidney epithelial cells Am J Physiol Renal Physiol, April 1, 2004; 286(4): F774 - F783. [Abstract] [Full Text] [PDF] |
||||
![]() |
C. Sauvant, H. Holzinger, and M. Gekle Short-Term Regulation of Basolateral Organic Anion Uptake in Proximal Tubular OK cells: EGF Acts via MAPK, PLA2, and COX1 J. Am. Soc. Nephrol., August 1, 2002; 13(8): 1981 - 1991. [Abstract] [Full Text] [PDF] |
||||
![]() |
B. C. BURCKHARDT, N. A. WOLFF, and G. BURCKHARDT Electrophysiologic Characterization of an Organic Anion Transporter Cloned from Winter Flounder Kidney (fROAT) J. Am. Soc. Nephrol., January 1, 2000; 11(1): 9 - 17. [Abstract] [Full Text] |
||||
![]() |
C. Sauvant, H. Holzinger, and M. Gekle Modulation of the Basolateral and Apical Step of Transepithelial Organic Anion Secretion in Proximal Tubular Opossum Kidney Cells. ACUTE EFFECTS OF EPIDERMAL GROWTH FACTOR AND MITOGEN-ACTIVATED PROTEIN KINASE J. Biol. Chem., April 27, 2001; 276(18): 14695 - 14703. [Abstract] [Full Text] [PDF] |
||||
| |||||||||