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J. Biol. Chem., Vol. 277, Issue 41, 38111-38120, October 11, 2002
From the
Received for publication, June 5, 2002
The carboxylic acid ionophore monensin, known as
an electroneutral Na+ ionophore, an anticoccidial
agent, and a growth-promoting feed additive in agriculture, is shown to
be highly efficient as an ionophore for Pb2+ and to be
highly selective for Pb2+ compared with other divalent
cations. Monensin transports Pb2+ by an electroneutral
mechanism in which the complex PbMonOH is the transporting species.
Electrogenic transport via the species PbMon+ may also be
possible. Monensin catalyzed Pb2+ transport is little
affected by Ca2+, Mg2+, or K+
concentrations that are encountered in living systems. Na+
is inhibitory, but its effectiveness at 100 mM does not
exceed ~50%. The poor activity of monensin as an ionophore for
divalent cations other than Pb2+ is consistent with the
pattern of complex formation constants observed in the mixed solvent
80% methanol/water. This pattern also explains why Ca2+,
Mg2+, and K+ are ineffective as inhibitors of
Pb2+ transport, but it does not fully explain the actions
of Na+, where kinetic features of the transport mechanism
may also be important. When given to rats at 100 ppm in feed together
with Pb2+ at 100 ppm in drinking water, monensin reduces Pb
accumulation in several organs and tissues. It also accelerates the
excretion of Pb that was accumulated previously and produces this
effect without depleting the organs of zinc or copper. Monensin, used alone or in combination with other agents, may be useful for the treatment of Pb intoxication.
Ionophores are lipophilic chelating agents that transport cations
across phospholipid bilayer membranes, such as the plasma and
subcellular membranes of cells. The naturally occurring compounds (about 100) are antibiotics produced primarily by soil bacteria of the
Streptomyces genus (1). They are distinguished from pore-forming antibiotics such as gramicidin by the involvement of a
discrete complex in the transport mechanism. Thus, true ionophores can
be highly selective for particular cations (2, 3). The known compounds
are generally divided into two groups: the so-called electrogenic and
the electroneutral ionophores (4, 5). Electrogenic ionophores are
typified by the well known compound valinomycin (6). They
are neutral molecules that form cation complexes that carry a net
positive charge, such that transbilayer charge movements accompany
transport catalyzed by this class. Accordingly, the rate of transport
is influenced by membrane electrical potential, which also determines
the transmembrane distribution of the transported cation at
equilibrium. Compounds such as monensin, nigericin, and A23187 (Fig.
1) typify electroneutral ionophores, also called carboxylic acid or polyether ionophores. The anionic forms of
these compounds complex the cation, which is exchanged for H+, or another cation, without net charge movement.
Transport catalyzed by this class is therefore influenced by
transmembrane pH gradients, as is the equilibrium distribution of
cations.
Among the carboxylic acid ionophores, it has been common to consider
individual compounds as able to complex/transport a small group of
cations having the same charge, with transport occurring through a
single species by a mechanism that is purely electrogenic or
electroneutral. Thus, monensin and nigericin were known as ionophores
for Na+ and K+, respectively, with transport
occurring via a 1:1 complex and electroneutral mechanism; A23187 was
known as a Ca2+ ionophore transporting via a 1:2 complex
and an electroneutral mechanism, and so forth. In work conducted over a
period of time, we showed that the model depicted in Fig.
2 is a more accurate representation of
the factors that establish the transport properties of a carboxylic
acid ionophore (7-16). The equilibrium shown at the top of
Fig. 2 represents formation of 1:1 complexes and emphasizes that
carboxylic acid ionophores react with a broad range of cations (n = 1-3), not just those with a particular charge as
often assumed. The 1:1 complexes then react to form higher order
species by competing equilibria I-III, which involve free ionophore
(A In considering the above model, the characteristics of the donor atoms in typical ionophores, and the metal ion complexation properties of analogous synthetic polyethers (17), we realized that some of the antibiotic compounds might be efficient ionophores for Pb2+ and for other cations with biological toxicity. Subsequently, we showed that ionomycin transports Pb2+ rapidly and with selectivity over Ca2+ near 103 when both cations are present simultaneously. Ionomycin was also found to affect an efficient transport of Pb2+ into cultured cells as well as to facilitate the depletion of Pb2+ when the cells had been previously loaded. We indicated that ionomycin should be considered primarily as an ionophore for Pb2+, rather than Ca2+, and suggested that its Pb2+-transporting activity might be adapted to improve existing treatments for Pb2+ intoxication (15). In the present report, we extend the investigation of
ionophore-mediated Pb2+ transport by demonstrating that
monensin is also effective as a Pb2+ ionophore and is more
selective in that regard than is ionomycin. We also show that monensin
promotes the excretion of Pb2+ from rats when the cation
has been previously provided in drinking water and the ionophore is
administered in feed. Aspects of these data have been presented in
abstract form (18).
Reagents and Solvents-- High purity nitric acid (trace metal; Fisher) and perchloric acid (double-distilled; GFS Chemicals) were obtained from commercial sources. Synthetic 1-palmitoyl-2-oleoyl-sn-glycerophosphatidylcholine (POPC)1 was obtained from Avanti Polar Lipids, Inc. Purity was confirmed by thin layer chromatography before use. For the transport studies, monensin and ionomycin were obtained from Calbiochem and used without further purification. Ionomycin stock solutions were prepared in ethanol and standardized spectrophotometrically using an extinction coefficient of 13,560 at 278 nm. In the case of monensin, standardization was gravimetric or by titration with Me4NOH. Quin-2 (K+ salt) from Sigma was purified by passage over Chelex 100 resin (100-200-mesh) in the Cs+ form as described previously (19), or in the Na+ form when Na+-loaded vesicles were employed. The nitrate and chloride salts of divalent cations were the ultrapure grade from Alfa Products. Stock solutions were standardized by titration with a primary standard EDTA solution (20) or by atomic absorption spectroscopy using certified solutions (Fisher). For solution chemical studies, a mixed solvent of 80% (w/w) methanol in water was prepared gravimetrically, using distilled deionized water and reagent grade methanol (Fisher) that had been freshly distilled. The Et4NClO4 that was used to maintain ionic strength in this solvent was prepared by reaction of Et4NOH (Aldrich) with 70% perchloric acid (distilled; GSH Chemicals). The salt obtained was recrystallized four times from water. Solvent containing Et4NClO4 and H+ buffering compounds was further deionized by passage over Chelex 100. For this purpose, the resin was in the Et4N+ form, which was prepared as previously described (8). Preparation of Phospholipid Vesicles-- The preparation of freeze-thaw-extruded POPC vesicles loaded with Quin-2 has also been described previously (21, 22). Briefly, 300 mg of POPC in chloroform was dried by rotation under a nitrogen stream to produce a film on the wall of a 25 × 150-mm culture tube. Residual solvent was removed under high vacuum (4 h), and the film was subsequently hydrated in 6 ml of a solution containing 6.6 mM purified Quin-2 and 10.0 mM Hepes buffer adjusted to pH 7.00 with Chelex-treated CsOH or NaOH (19), depending on the internal composition required. The mixture was vortexed, and the resulting multilamellar vesicles were frozen in a dry ice-acetone bath, thawed in lukewarm water, and vortexed again. The freeze-thaw and vortexing procedures were repeated two additional times, after which the vesicles were extruded three times through two stacked 100-nm polycarbonate membrane filters. This step was followed by six additional freeze-thaw cycles coupled with additional extrusions. The resulting preparations were applied to Sephadex G-50 minicolumns (23) to remove extravesicular Quin-2. These columns were eluted by low speed centrifugation and had previously been equilibrated with a solution containing 10 mM Hepes buffer, pH 7.00. A single pass over such columns effectively removes the external Quin-2 (19, 21, 22). The nominal concentration of POPC in the final preparations was determined by measurement of lipid phosphorus (24) and was near 80 mM. The average diameter of these vesicles is 71 nm as determined by freeze-fracture electron microscopy (21), and they contain entrapped solutes at the following concentrations: Quin-2, 10.5 ± 0.8 mM; Hepes, 34 ± 8 mM (pH ~7.4); and Cs+/Na+, 60 ± 5 mM. Specific values for Quin-2 and Cs+/Na+ were determined for each preparation by the methods described previously (19, 25). Briefly, entrapped Quin-2 is determined by spectrophotometric titration with standard CaCl2 following dispersion of the vesicles in deoxycholate. The entrapped monovalent cation is determined by atomic absorption spectroscopy, following replacement of the external medium with one containing a different cation, and dispersion of the vesicles in 0.1 N HCl. When of interest, buffer entrapment is determined from the other values by calculation, using the Henderson-Hasselbach equation, the buffer pKa, and the internal pH. When buffer entrapment is to be determined, the vesicles also contain the fluorescent pH indicator 2',7'-bis(2-carboxyethyl)-5(6)-carboxyfluorescein, so that the internal pH can be ascertained. The internal pH and solute concentrations differ from those of the vesicle formation medium because of a freeze-thaw-driven solute-concentrating effect that operates during preparation of the vesicles (21, 22). Pb2+ Buffers and the Determination of
Transport--
A buffer system was used to control the concentration
of Pb2+ available for transport into the vesicles. 15 or 5 mM citrate was employed to buffer the concentration of this
cation, whereas 10 mM each of Hepes and Mes were present to
buffer H+. Seventeen equilibria involving
citrate3 The transport of Pb2+ and other divalent cations into Quin-2-loaded vesicles was determined by monitoring formation of the Quin-2-cation complexes spectroscopically. Unless otherwise indicated, vesicles containing Quin-2 were present at a nominal POPC concentration of 1.0 mM in a medium that also contained 50 mM CsCl and 10 mM each of Hepes and Mes. The medium pH ranged from 6.00 to 9.50 and was adjusted with CsOH that had been passed over Chelex 100 columns to remove contaminating divalent cations (19). In some cases, valinomycin (0.5 µM) and carbonyl cyanide m-chlorophenylhydrazone (CCCP) (5 µM) were also present to maintain internal pH at the external value and to dissipate any transmembrane electrical potential that might otherwise arise (25). Specific concentrations of ionophores, divalent cations, and pH values are given in the figure legends. Reactions were started by the addition of the ionophore, following an initial 2-min preincubation to allow equilibration of transmembrane pH. The formation of Quin-2-cation complexes was followed continuously by difference absorbance spectroscopy, using an Aminco DW2a spectrophotometer operated in the dual wavelength mode. An Oriel 59800 band pass filter was used between the cuvette and the beam scambler-photomultiplier assembly to prevent detection of the fluorescent light emitted by Quin-2. The sample wavelength used for all cations was 264 nm. The reference wavelengths were at an isosbestic point in the Quin-2/Quin-2-cation complex difference spectrum of interest. These wavelengths vary slightly from cation to cation, as previously described (13). Data were collected on disk using Unkel Scope software (Unkel Software, Inc., Lexington, MA).
To determine initial transport rates, an early portion of the progress
curves was fit to Equation 1 using standard nonlinear least-squares
methods.
Potentiometric Titrations and the Determination of pH in Aqueous Methanol-- The protonation constants and complex formation constants of monensin were measured by potentiometric methods in the mixed solvent 80% (w/w) methanol/water. For these studies, Na+ monensin was purified by column chromatography on silica gel, using ethyl acetate as the eluent. The Na+ salt was converted to the acid form by repeated back-extraction of a CHCl3 solution with 1.0 M HCl. The CHCl3 solution was then washed three times with distilled water, the solvent was removed, and the product was dried under vacuum. Analysis by flame atomic emission showed that less than 0.05% Na+ (w/w) remained. Pb(ClO4)2 and Zn(ClO4)2 were prepared by reaction of the metal oxide (lead, 99.9995%; zinc, 99.99%; Aesar) with 70% HClO4 (distilled; GFS Chemicals). CaCl2·xH2O (99.999%) and MgCl2·6H2O (99.995%; Aldrich) were used as received. Stock solutions of Pb2+, Zn2+, Ca2+, and Mg2+ salts were standardized by titration using EDTA (20). NaCl (99.999%; Aldrich) and KCl (99.997%; Aesar) were dried at 110 °C, and stock solutions of these salts were prepared gravimetrically. Test solutions for potentiometric titration typically contained 0.5-1.0 mM monensic acid (HL) and, where appropriate, the metal ion (M) at concentration ratios ([HL]/[M]) in the range of 1.0-3.0. In the case of Mg2+ and K+, [HL]/[M] ratios of 0.2-0.25 were also used. Ionic strength was maintained at 0.050 using Et4NClO4, except in the case of K+, where Et4NCl (>99%; Fluka) was used. The titrations were carried out using a digital burette, (Metrohm, model 665) and pH meter (Fisher, model 825MP) that was interfaced to a computer (11). pH* measurements were made using double junction combination electrodes (Sensorex S1021CD, Orion Ross 8175BN, Thomas 4080-B49), where the external filling solution was replaced with 0.1 M Et4NClO4 or 0.1 M Me4NCl in 20% methanol/water.
The pH meter-electrode system was calibrated in aqueous solution using
standard buffers (Gram-Pac; Fisher); then the electrodes were
equilibrated in 80% methanol/water for at least 2 h prior to
measurement. The operational pH* scales developed by de Ligny et
al. (30, 31) and Gelsema et al. (32, 33) were utilized to determine the value of pH*. The term pH* is defined as All titrations were carried out at 25.0 °C using a thermostatted cell and 20 mM Me4NOH as the titrant. A nitrogen or argon atmosphere was maintained to minimize contamination by CO2. The Me4NOH was standardized using KH2PO4 and checked for carbonate content (35). Typical titrations consisted of 50-100 pairs of pH* versus ml Me4NOH readings. The titration data were analyzed using the computer programs PKAS for the protonation constants (36) and BEST for the metal ion complexation constants (37). Treatment of Experimental Animals-- Male rats were utilized when investigating the effects of monensin on the pathophysiology of Pb2+. They were housed in AALAC-approved animal facilities at the College of Medicine, Ohio State University. A 12-h light-dark cycle, single housing in plastic cages, or in metabolic cages, and conditions of constant temperature and humidity were employed. One week was allowed for acclimation before an experimental protocol began. During this period, a standard laboratory chow was employed, whereas the AIN-93 M diet containing 0.5% calcium was employed thereafter. During the administration of Pb2+ and/or monensin, water and feed were provided ad libitum, and records of consumption were maintained, together with periodic measurements of body weight. At the beginning of an experimental protocol, the rats weighed 245-255 g. They were divided randomly into groups of six or eight, and the administration of Pb2+ was begun. It was provided at 100 ppm in the drinking water and was in the form of Pb(acetate)2. The water was rendered slightly acidic with acetic acid to prevent the precipitation of PbCO2 (38). When utilized, monensin was provided in the feed, also at 100 ppm. Determination of Pb in Biological Samples-- Blood samples were taken periodically from the tail artery, and blood Pb levels were determined by electrothermal atomic absorption spectroscopy against certified standards (39). For the determination of Pb in urine and feces, total outputs were collected over 2-day periods from each rat individually. The urine samples were neutralized by the careful addition of nitric acid while the samples were stirred, and the pH was monitored with an electrode. Samples were then extracted with methyl isobutyl ketone in the presence of excess ammonium pyrrolidine dithiocarbamate, which quantitatively extracts Pb2+ into the organic layer and concentrates it compared with the original concentration in urine (40). The Pb content was thereafter determined by flame atomic absorption spectroscopy. For the determination of Pb in feces, weighed samples comprising ~1.0 g were dispersed in 10 ml of concentrated nitric acid and allowed to stand at room temperature overnight. They were then concentrated to ~1.5 ml by heating on a hot plate and diluted to a total volume of 10.0 ml with water, and Pb was determined by flame atomic absorption spectroscopy (41).
At the completion of experimental protocols, the rats were
sacrificed by the injection of excess Nembutal and perfused briefly with Hepes-buffered 0.9% NaCl, via the left ventricle, to remove blood
from the organs. Organs and tissues of interest were then removed and
stored at
Monensin-mediated Pb2+ Transport--
Fig.
3 compares the efficiency of ionomycin
and monensin as ionophores for Pb2+ and contrasts their
selectivity for Pb2+ compared with other divalent cations.
Under the conditions employed, the two compounds are similarly
effective from the perspective of rate, whereas monensin is much more
selective. Selectivity for Pb2+ over Ca2+, for
example, as defined by Equation 2, is ~100 for ionomycin and ~3400
for monensin.2
The stoichiometry of the complex between ionomycin and Pb2+
that is responsible for transport is 1:1, cation/ionophore, based upon
plots of log rate versus log ionomycin or log
Pb2+ concentration, which both display slopes of 1.0 (15).
By the same criteria, monensin-mediated Pb2+ transport also
occurs through formation of a 1:1 complex (Fig. 4), although the plot of log
rate versus log Pb2+ concentration progressively
deviates from a slope of 1 as the free Pb2+ concentration
rises above 1 µM. This negative deviation suggests that
the steady state fraction of monensin that is located at the external
membrane interface approaches saturation with Pb2+ at
concentrations above that value.
Ionomycin is dibasic, because both the carboxylic acid function and the
enolized
Fig. 5A shows
examples of the primary data obtained, whereas Fig. 5B
reports the complex stability constants. It is seen that the complex
PbMon+ is relatively stable, displaying a log K
value of 7.25. The uncharged complex PbMonOH that is formed upon
reaction of PbMon+ with OH
To further examine these possibilities, the effect of external pH on
the rate of Pb2+ transport was examined, using
Na+-containing vesicles with valinomycin and CCCP
excluded. These conditions limit transport to the fraction occurring by
neutral mechanisms, because no provision is made to collapse the
membrane potential arising from electrogenic transport, which is very
effective at limiting the process (e.g. Refs. 14 and 16). In
addition, the use of Na+ rather than
Cs+-containing vesicles allows the ionophore to exchange
Pb2+ for Na+, ensuring that the rate of
Pb2+ transport does not become limited by the protonation
of monensin at the internal membrane interface. As seen in Fig.
6A, monensin remains active as
an ionophore for Pb2+ under these conditions, demonstrating
that the electroneutral mode is indeed active.
Regarding the species PbMonOH, the data in Fig. 6B show that increasing external pH enhances the rate of transport, consistent with a model involving dissociation of a single proton from hydrated PbMon+ to form PbMonOH. This finding and a comparison of the transport data with the pH dependence for PbMonOH formation shown in Fig. 5C indicate that PbMonOH is indeed the major transporting species. In Fig. 6, the half-maximal rate was seen at pH 7.8 (pOH 6.2) or at pPbOH 6.9 if it is considered that that species is the one which is actually transported. Competitive Relationships between Pb2+ and Other
Cations--
Given the potential use of ionophores to manipulate
Pb2+ in living systems, we considered the possibility that
the relatively high concentrations of other cations found in blood and
intracellular compartments might substantially prevent monensin from
transporting Pb2+ in vivo. Specifically, the
rates of Pb2+ transport were compared when the free
Pb2+ concentration was buffered at 1.0 µM
alone and when 1.0 mM free Ca2+ or
Mg2+ was also present. Only negligible differences were
seen (Fig. 7, A and
B), as might be expected based upon the complex stability constants shown in Fig. 5B. Potential interference by
K+ and Na+ was also examined. The actions of
K+ were again negligible when it was present at 5.0 or 100 mM, approximately the levels of this cation in blood and
cytoplasm, respectively (data not shown). The same concentrations of
Na+ did have modest inhibitory effects (Fig.
7C); however, these were smaller than expected based on the
KML values listed in Fig. 5B. In
other words, the ratio
KPb/KNa is ~300,
whereas at a ratio of free Na+/Pb2+ of
105 (i.e. when Na+ was present at
100 mM and Pb2+ at 1.0 µM), the
rate of Pb2+ transport is reduced by only a factor of
<2.
To further examine the effectiveness of Na+ as an inhibitor
of monensin-mediated Pb2+ transport, the Na+
concentration was varied from 0 to 100 mM while another
solute was varied in the opposite direction, so as to maintain the
external ionic strength and/or the osmotic pressure at constant values. As seen in Fig. 8, Na+ is
more effective when used to replace Cs+, compared with
K+ or tetraethylammonium cation, and it is ineffective when
used to replace mannitol. These data presumably reflect modest
differences in the stability of complexes between monensin and
monovalent cations (47-49) together with effects of ionic strength on
complex stability. However, of greater importance, they further
indicate that concentrations of Na+ found in living systems
have little effect on the efficiency of monensin as a Pb2+
ionophore.
Monensin Promotes the Excretion of Pb2+ in Rats-- Given that the above data are consistent with the notion that monensin might alter the dynamics of Pb2+ in whole organisms, we determined the effect of monensin on the accumulation and disposition of Pb in rats. In one experiment, the ionophore and Pb2+ were administered simultaneously, at 100 ppm in feed and 100 ppm in drinking water, respectively, or Pb2+ was administered without the ionophore. Blood samples were taken at weekly intervals over a 28-day period, and thereafter the rats were sacrificed to allow the determination of Pb in organs and tissues. Throughout the entire experimental period, the average concentration of Pb in blood was lower by ~25% in the rats that had received monensin, and this difference was significant at p = 0.05 (Table I and data not shown). Monensin also reduced the accumulation of Pb in several organs, with a particularly large effect seen in heart, where it was reduced by 66% (Table I). The reduced values seen in brain, muscle, and bone were also significant.
In a second experiment, the rats were loaded with Pb2+ over a 21-day period and in the absence of monensin. Thereafter, they were divided into groups and given drinking water that did not contain Pb2+. One group was given monensin at 100 ppm in feed, whereas another was given the same feed without monensin. After an additional 21 days, the rats were sacrificed, and lead in organs and tissues was determined. This time there was no difference in blood lead, either at the time of sacrifice (Table II) or at earlier sampling times (data not shown). However, the rats given monensin had lower levels of lead in brain, kidney, liver, and bone. The greatest effect was seen in kidney (a 55% reduction), with the effect on liver being of similar magnitude. Consistent with the transport data shown in Fig. 3 and the complex stability constants shown in Fig. 5B, the reduced levels of Pb in organs were obtained without reducing the levels of zinc or copper (Table III). Thus, the actions of monensin on lead are not accompanied by perturbation of these trace elements having biological roles.
During this second experiment, the rats were housed in metabolic cages
so that urine and feces could be collected to determine the fate of Pb
released from the organs. Amounts excreted in urine were low and were
unaffected by the presence or absence of monensin (Fig.
9). Determining excretion via the feces
is more problematic, because the gastrointestinal tract in rats rejects
most Pb that is ingested, resulting in high levels of Pb in feces
during the loading period (Refs. 50 and 51 and data not shown). When Pb2+ is withdrawn, feces Pb remains high for several days
while the contents of the gastrointestinal tract turn over. These large values of excreted Pb obscure smaller differences between groups, such
as differences that might be produced by monensin. Nevertheless, at
later times, a statistically significant effect of monensin on Pb in
feces was observed. In other words, during the second and third week of
monensin administration, the treated rats lost lead at a rate of ~120
nmol/day, whereas without monensin the rate was about half that value.
As further considered below, these data suggest that the lead mobilized
from organs by monensin is ultimately excreted via the feces.
Monensin was among the first group of carboxylic acid ionophores to be discovered, a group that also includes dianemycin, nigericin, compound X-206, and lasalocid A (reviewed in Ref. 5). Soon after these compounds were reported to be potent anticoccidial agents (52) and to derive this activity through a direct interaction with monovalent cations, leading to altered cation transport (53). Among the monovalent alkali metal cations, monensin was subsequently shown to be most effective as an ionophore for Na+, and it has long been utilized as a research tool in that regard (reviewed in Refs. 2 and 54). It has also been used as a feed additive in agriculture, because of the anticoccidial activity and because it promotes the growth of several animal species that are used in that industry (55, 56). Relatively recent studies have shown that monensin also forms complexes with several divalent cations and that they are generally more stable than those formed with monovalent cations when compared in nonaqueous solvents such as methanol or diethylformamide (47, 48, 57-59). More limited data have furthermore shown that monensin displays some capacity to extract divalent cations from a bulk aqueous to a bulk organic phase (57) and to convey these cations through three phase bulk solvent systems (60) and polyvinyl chloride membranes in ion-selective electrodes (61, 62). Thus, previous studies have suggested that monensin might not be strictly an ionophore for monovalent cations, but they did not reveal that it is actually a highly selective and efficient ionophore for Pb2+ when phospholipid membranes are employed. That activity is newly discovered and is shown in the present report (Figs. 3 and 4). The stoichiometry of the complex that transports Pb2+ is
clearly 1:1, ionophore/cation, based upon the relationships between log
rate and log monensin or log Pb2+ concentration, which are
both linear over a wide range and display slopes of 1.0 (Fig. 4). As
illustrated in Fig. 10, the 1:1 complex PbMon+ may then be active as a transporting species and
would function by an electrogenic mechanism. This type of mechanism may
have contributed to the transport seen in Figs. 3 and 4, because
valinomycin and CCCP were present during those experiments. Valinomycin
and CCCP, acting together, are fully effective at collapsing an induced membrane potential in the present vesicle system (14, 16), which is
required for sustained electrogenic transport.
No provision was made to collapse membrane potential during
the experiments reported in Figs. 6-8, so only electroneutral
transport was contributing. The transporting species under those
conditions is PbMonOH, as shown by the relationship between rate and
external pH (Fig. 6) and by comparing that relationship to the
distribution of Pb/monensin species that arises when the pH is varied
(Fig. 5C). PbMonOH can form by the pathways shown by
Reaction 1 or 2, as further illustrated in Fig. 10, and both of these
pathways can be considered to involve the acid ionization of a
hydrating water molecule associated with Pb2+.
The present data do not provide insight into which of the pathways may be the most significant, but that may not be a point of central interest, assuming that all equilibria shown in Fig. 10 remain at or near equilibrium during monensin-catalyzed Pb2+ transport. Apart from the pathway forming PbMonOH, the extent of equilibration between reactants forming the transporting species is of interest when the origin of high selectivity for Pb2+ transport is considered, compared with the transport of other divalent cations. If near equilibrium conditions are maintained, selectivity is expected to arise from differing complex stabilities, together with variation in the transmembrane diffusion constants of the various metal cation-monensin complexes. Several alkaline earth and first transition series divalent cations are poorly shielded when complexed by monensin (57), a factor that reduces transmembrane diffusion constants. However, the role of differential shielding in establishing the selectivity of monensin as an ionophore for Pb2+ is uncertain, because shielding in Pb2+-monensin complexes has not been investigated. Regarding complex stabilities, the CaMon+ and the
MgMon+ complexes are less stable than the
PbMon+ complex by ~4 orders of magnitude (Fig.
5B; Refs. 57 and 59), and in addition, no interaction of
these complexes with OH On the other hand, Na+ is much less effective as an
inhibitor of monensin-mediated Pb2+ transport than would be
expected on the basis of complex stability constants alone, were near
equilibrium maintained between monensin, OH The current data obtained in model systems suggest that, like ionomycin (15), monensin might be useful in the treatment of lead intoxication; however, there are no studies that have tested that possibility in animals. Accordingly, we determined whether monensin alters the accumulation or distribution of lead when the two agents are given simultaneously and whether monensin affects the disposition of lead that was accumulated previously. The level of Pb2+ employed and the method of administration are typical of those used when investigating Pb toxicity in rats (64-67). The level of monensin is the same as that usually given to chickens as an agricultural practice (56) and is below the toxic threshold for monensin in rats (68, 69).3 Monensin was administered as a component of feed, because that is the practice in agriculture and because activity upon oral administration is considered to be advantageous for agents used to treat lead intoxication. The data show that in both types of experiment monensin reduced the level of lead in several organs and tissues (Tables I and II). The design of studies that investigate the efficiency of agents used to treat lead intoxication varies widely, so it is difficult to compare the effectiveness of monensin with that of the traditional agents (e.g. EDTA and dimercaptosuccinate) in a succinct manner. Nevertheless, monensin appears to be similarly effective to these better investigated compounds (e.g. compare with Refs. 70-72), although the dose employed here, the treatment interval, etc. have not been optimized. In addition, monensin reduces Pb in bone and brain, which is not true for the traditional compounds under some circumstances (64, 73), and does not deplete the tissues of zinc and copper, which can occur as an unwanted side effect with some of the traditional compounds (74-76). Thus, monensin may indeed be useful for promoting the elimination of lead from animals. At this early stage, it is appropriate to consider the possibility than
monensin acts differently than the traditional compounds as regards the
mechanism by which lead excretion occurs. The traditional compounds are
hydrophilic cation chelators that circulate in blood and form
Pb2+ complexes having stability constants of
~1015 and higher. They are not membrane-permeant and are
excreted together with Pb2+, typically via the kidney. The
lead-monensin complex is much less stable (K = 107.25 in 80% methanol/water) and has little solubility in
an aqueous environment. Moreover, the complex easily crosses a
phospholipid membrane, whereas Pb excretion occurs primarily via the
colon. Thus, monensin may act primarily by transporting Pb out of
cells, where it eventually returns to the lumen of the gastrointestinal tract and is excreted by a normal mechanism, possibly involving the
enterohepatic circulation. Since monensin is highly active as an
ionophore for Na+ as well as for Pb2+, its
presence will couple the gradients of these two cations across cell
membranes, providing a driving force for Pb transport out of the cell.
Overall, this potential mechanism suggests that the application of
monensin, together with a hydrophilic chelator, might be particularly
effective at promoting the excretion of Pb from animals. That
possibility is currently under investigation.
* This research was supported by the Wallace Research Foundation, by American Heart Association Grant 0255017B, by National Institutes of Health Grant GM66206, and Oklahoma Center for the Advancement of Science and Technology Grant HR00-030.The costs of publication of this article were defrayed in part by the payment of page charges. The article must therefore be hereby marked "advertisement" in accordance with 18 U.S.C. Section 1734 solely to indicate this fact.
Published, JBC Papers in Press, June 21, 2002, DOI 10.1074/jbc.M205590200
2 When both cations are present simultaneously, the selectivity of ionomycin for Pb2+ compared with Ca2+ is similar to the value for monensin derived from Fig. 3B (15).
3 Consistent with the reports cited, we did not find a significant effect of monensin at 100 ppm on growth (weight gain) or on the consumption of feed and water.
The abbreviations used are: POPC, 1-palmitoyl-2-oleoyl-sn-glycerophosphatidylcholine; CCCP, carbonyl cyanide m-chlorophenylhydrazone; Ches, 2-(cyclohexylamino)ethanesulfonic acid; Mes, 2-(N-morpholino)ethanesulfonic acid.
Copyright © 2002 by The American Society for Biochemistry and Molecular Biology, Inc. This article has been cited by other articles:
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