|
|
|
|||
| Home Help Feedback Subscriptions Archive Search Table of Contents | ||||
First published online September 14, 2007
Journal of Experimental Biology 210, 3484-3493 (2007)
Published by The Company of Biologists 2007
doi: 10.1242/jeb.008300
Heavy metal detoxification in crustacean epithelial lysosomes: role of anions in the compartmentalization process
1 Department of Biology, University of North Florida, 4567 St Johns Bluff
Road, S., Jacksonville, FL 32224, USA
2 Department of Physiology, University of Florida, Gainesville, FL, 32610,
USA
* Author for correspondence (e-mail: gahearn{at}unf.edu)
| Summary |
|---|
|
|
|---|
Key words: zinc transport, lysosomes, detoxification, sulfate, oxalate, chloride, anion exchange, heavy metals, lobster, Homarus americanus, V-ATPase, electrogenic transport
| Introduction |
|---|
|
|
|---|
Previous studies with lobster (Homarus americanus)
heptaopancreatic lysosomes have shown that both copper
(Chavez-Crooker et al., 2003
)
and zinc (Mandal et al., 2006
)
are transported from hepatopancreatic epithelial cytoplasm into organelle
interior by ATP-dependent carrier-mediated transporters that are sensitive to
both vanadate and thapsigargin. In addition, both metals were cross-inhibited,
suggesting the presence of a metal transporter with a relatively broad
substrate specificity. Detoxification of heavy metals in organelles such as
lysosomes requires the presence of a mechanism that sequesters the cation in a
form that is relatively immobile and cannot be transferred back into the
cytoplasm. Electron microprobe analyses of a variety of invertebrate
epithelial cells indicate that metals are sequestered together with sulfate
and phosphate in solid concretions within membrane-bound organelles
(Al-Mohanna and Nott, 1985
).
While the composition of these concretions has been evaluated in a wide
variety of invertebrate species, the mechanisms whereby complexing anions are
transferred into these sites of detoxification are unknown. This study
examines the nature of anion transport by lobster hepatopancreatic lysosomal
membranes and suggests a mechanism by which metal cations and polyvalent
anions can be brought together to form detoxifying concretions in these
cells.
| Materials and methods |
|---|
|
|
|---|
Isolation of hepatopancreatic lysosomal membrane vesicles (LMV)
Hepatopancreatic lysosomal membrane vesicles (LMV) were prepared from fresh
organs of individual lobsters. Hepatopancreatic tissue was quickly placed in
chilled Buffer A (in mmol l–1: 250 sucrose, 20 Hepes, 1 EDTA,
0.1 PMSF, adjusted to pH 7.0 with Tris base). The tissue was homogenized with
a glass hand homogenizer and diluted tenfold in chilled Buffer A. The
homogenate was centrifuged at 800 g for 10 min and the
resulting supernatant was centrifuged at 20 000 g for 10 min.
The pellet was re-suspended in Buffer B (in mmol l–1: 250
mmol l–1 sucrose, 20 Hepes, adjusted to pH 7.0 with Tris
base). The suspension was mixed with isotonic PercollTM in the ratio of
9:11 (pellet suspended in Buffer B:isotonic PercollTM). The
PercollTM mixture was centrifuged at 40 000 g for 90 min.
The brownish dense lysosomal band near the bottom of the gradient was removed,
diluted with Buffer B and centrifuged at 20 000 g for 10 min.
The pellet was then incubated in freshly prepared Buffer B containing 5 mmol
l–1 methionine methyl ester, 2 mg ml–1
bovine serum albumin, and 2 mmol l–1 MgCl2 for 20
min at 18°C. An equal volume of ice-cold isotonic PercollTM was added
to the incubation mixture and centrifuged at 35 000 g for 30
min. The purified LMV (located on the top of the gradient as a brownish band)
was re-suspended in Preloading Buffer (varied experiment to experiment).
An enzyme characterization of lobster hepatopancreatic LMV produced by the
PercollTM centrifugation method described above has been previously
published (Mandal et al.,
2006
). In this study, the enrichments of three enzymes of known
disparate cellular localization were used to show the purification of the LMV
samples used in the present investigation. While the brush border enzyme
marker, alkaline phosphatase, and the ER marker enzyme, NADPH-cytochrome
c reductase, were not significantly enriched (P>0.05),
the lysosomal enzyme, acid phosphatase, was purified by more than a factor of
12 in the final vesicle suspension compared to the original tissue homogenate.
These data suggest that the LMV fractions used in this previous investigation,
and also in the present study, were relatively pure lysosomal membranes and
had minimal membrane contamination from other parts of the cell such as the
plasma membrane or the endoplasmic reticulum.
65Zn2+, 36Cl–, 35SO42– and 14C-oxalate2– transport measurements
Characteristics of 65Zn2+ transport by isolated
vesicles from hepatopancreatic lysosomal membranes were studied at room
temperature (23°C). Experiments were initiated by diluting a small volume
of vesicle suspension into a medium containing trace amounts of
65ZnCl2 (+ unlabelled zinc sulfate),
K36Cl– (+ unlabelled KCl),
K235SO42– (+ unlabelled
K2SO42–) or 14C-oxalic acid
(+ unlabelled oxalic acid). The composition of the final vesicle suspension
solutions (inside vesicles) and incubation media (outside vesicles) are
described separately for each experiment. Uptake of the radiolabelled
substrate was initiated by rapidly mixing 20 ml of membrane suspension (150 mg
of protein), preloaded with buffer (pH 7.0), with 180 ml of transport medium
(described separately for each experiment) and incubating for appropriate time
periods. Transport was terminated by addition of 2 ml (tenfold dilution)
ice-cold buffer (stop solution) and the suspension was immediately collected
under vacuum on a MilliporeTM filter (HAWP, Billerica, MA, USA; 45 mm
pore size), utilizing the MilliporeTM filtration technique developed by
Hopfer et al. (Hopfer et al.,
1973
). Filters were then dissolved in liquid scintillation
cocktail (EcolumeTM) and the radioactivity counted in a Beckman Coulter
LS 6500 multi-purpose scintillation counter. Isotope uptake was expressed as
pmol mg–1 protein s–1 or as nmol
mg–1 protein s–1. The protein content of the
vesicle suspension was determined according to the Bradford proceedure
(BioRad, Hercules, CA, USA), using bovine serum albumin as a standard.
Displayed zinc activities were achieved using appropriate concentrations of
zinc, NTA (nitriloacetic acid; N,N-bis[carboxymethyl]glycine), and
ATP (0.2 mmol l–1), using Winmax Chelator 2.0 software
(Bers et al., 1994
).
Isotope uptake into lysosomal vesicles was corrected for non-specific isotope binding (bound activity to exterior of vesicles and not transported to the vesicular interior) by injecting a sample of lysosomal vesicles and isotope directly into ice-cold stop solution without prior mixing. The resulting lysosomal vesicle suspension was then filtered, rinsed and counted as described previously. Resulting values for non-specific isotope binding were subtracted from total isotope uptake in each experiment, providing an index of transmembrane transport of the respective radiolabelled cation or anion. Time points are presented as means of 3–5 replicates and their associated standard errors (s.e.m.). Experiments were repeated at least twice with different animals. Statistical comparisons were made using Student's t-test where a value of P<0.05 was considered significant. Curve-fitting procedures were accomplished using Sigma Plot 9.0 software (Jandel, San Rafael, CA, USA), which provided an iterative best fit to experimental values.
Chemicals
65ZnCl2 was purchased from Oak Ridge National
Laboratory, Oak Ridge, TN, USA and 36Cl–,
35SO42– and 14C-oxalic acid
were obtained from DuPont New England Nuclear Corp., Boston, MA, USA.
Valinomycin, Zinc sulfate, Tris, D-mannitol, and other reagent
grade chemicals were purchased from Sigma Chemicals (St Louis, MO, USA),
Fisher (Pittsburgh, PA, USA), or Bio-Rad (Hercules, CA, USA).
| Results |
|---|
|
|
|---|
|
Because 25 µmol l–1 SO42– was one of the polyvalent inorganic anions that led to enhanced vesicle accumulation of 25 µmol l–1 65Zn2+, an experiment was conducted to see what effect a wide range of intravesicular SO42– concentrations would have on the metal uptake by these membrane preparations. Fig. 2 shows that increasing intravesicular SO42– from 25 to 1000 µmol l–1 resulted in a stepwise increase in uptake rate and equilibrium of 25 µmol l–1 65Zn2+ by hepatopancreatic lysosomal vesicles. Metal uptakes at 500 and 1000 µmol l–1 SO42– were not significantly different (P>0.05) from one another, but were significantly different (P<0.01) from those at lower SO42– concentrations, suggesting that the mechanism resulting in the enhancement of metal uptake reached a maximum around an intravesicular SO42– concentration of approximately 500 µmol l–1.
|
The influx of 65Zn2+ was stimulated by a decrease in intravesicular pH and by the presence of external ATP (Fig. 3). Furthermore, in the presence of ATP, metal transport was enhanced by an intravesicular positive electrical potential difference (e.g. K+i<K+o) compared to when the vesicles were either short-circuited (e.g. K+i=K+o) or contained an intravesicular negative electrical potential difference (e.g. K+i>K+o). These results suggest that because an electrically positive intravesicular potential difference increased the uptake of 65Zn2+, more positive charge must have been transferred out of the vesicle than into the vesicle during the exchange of zinc and protons. The minimum transport stoichiometry that could account for this exchange would be 1Zn2+/3H+ and this proposed ratio is consistent with the data displayed in Fig. 3.
|
Countertransport of anions by lysosomal vesicles
Because intravesicular polyvalent inorganic anions like
SO42– and PO43–
enhanced the equilibrium accumulation of 65Zn2+ within
hepatopancreatic lysosomal vesicles, the nature of the uptake process
facilitating the transfer of these anions from the cytoplasm was investigated.
Two groups of vesicles were prepared. One group was loaded with mannitol and
Hepes/Tris at pH 7.0 only and the other had mannitol and intravesicular
chloride at pH 7.0. These two vesicle groups were then incubated in media
containing 35SO42– or
14C-oxalate2– and the time course of isotope
uptake into both membrane groups was followed.
Fig. 4A shows that
35SO42– uptake was stimulated in
vesicles containing intravesicular Cl– compared to that shown
by mannitol-loaded vesicles. Fig.
4B shows a similar response to intravesicular Cl–
by 14C-oxalate2– uptake. These results suggest the
presence of an anion countertransport process in hepatopancreatic LMV, but do
not clarify any of its properties except that it exchanges anions.
|
Polyvalent anion exchange kinetics with intravesicular chloride
In order to more fully describe the features of LMV anion exchange,
additional experiments were conducted describing the characteristics of anion
influx kinetics into Cl–-loaded vesicles.
Fig. 5A shows
35SO42– influx kinetics into lysosomal
vesicles preloaded with 25 mmol l–1 Cl–. As
displayed in this figure, the influx of the divalent anion was a sigmoidal
function of its cytoplasmic concentration when 25 mmol l–1
intravesicular Cl– was present inside the preparation. Under
these conditions, 35SO42– influx
followed the Hill equation of multi-site cooperativity shown below:
![]() | (1) |
|
Fig. 5B displays a similar
exchange process between the organic divalent anion,
14C-oxalate2–, and intravesicular
Cl–. In contrast with the results disclosed for
sulfate2– (Fig.
5A), influx kinetics for oxalate2– followed the
hyperbolic Michaelis–Menten relationship described below:
![]() | (2) |
Lysosomal 36Cl– uptake occurs by exchange with OH–
Because Cl– ion acted as a `common currency' for exchange
with different divalent anions (e.g. Fig.
5), the question arose as to how this monovalent anion was taken
up by lysosomal vesicles. Fig.
6 displays the results of an experiment examining the nature of
36Cl– influx into lysosomal membrane vesicles that
were loaded at pH 7.0 or 9.0 (external pH 7.0 at both times), thereby
providing only hydroxyl ions as a potential anion substrate for exchange with
external 36Cl–. As indicated in this figure,
Cl– influx was a sigmoidal function of external chloride
concentration at each intravesicular pH condition and followed the Hill
equation for multisite cooperativity between binding ligands as described
previously for 35SO42– influx into
these vesicles:
![]() | (3) |
|
In order to clarify the transport exchange stoichiometry between
Cl– ions and OH– ions during
36Cl– influx into lysosomal membrane vesicles,
36Cl– influx was measured at four different
extravesicular [Cl–] (2.5, 5, 15 and 35 mmol
l–1 Cl–) over a range of different
intravesicular pH values and the 36Cl– influx
values are expressed as a function of intravesicular [OH–]
(nmol l–1). As the data presented in
Fig. 7 indicate,
36Cl– influx was a hyperbolic function of
intravesicular [OH–] at each extravesicular
[Cl–] from 2.5 to 35 mmol l–1
Cl–. These results suggest that
36Cl–/OH– exchange followed a
modified Michaelis–Menten equation for carrier-mediated transport as
shown below:
![]() | (4) |
|
Lysosomal 35SO42– uptake occurs by exchange with OH–
A series of experiments examining the nature of
35SO42– influx into lysosomal vesicles
was performed following the protocol outlined for the investigation of
36Cl– influx into these preparations as described
in Figs 6 and
7. In this instance vesicles
were loaded at pH 7.0, 8.0 and 9.0 and were incubated in media containing
35SO42– at concentrations from 2.5 to
50 mmol l–1. As in the previous series of experiments,
OH– ions were the only exchangeable anion substrate inside
the vesicles. Sigmoidal influx kinetics, as described in
Eqn 1, were obtained for
SO42– influx as a function of external
[SO42–] at each of the chosen internal pH
conditions (Fig. 8). Results
indicated that both sulfate2– influx
Kmn and Jmax
increased significantly (P<0.01) from pH 7.0 to 9.0, but a greater
change was observed in the Jmax parameters than in the
apparent affinity values. A small increase (P<0.02) was also
observed in the magnitude of the Hill coefficient n over the pH range
examined, but all values approximated 2.0, as was found for
Cl– influx under similar conditions
(Fig. 6).
|
|
| Discussion |
|---|
|
|
|---|
In addition to its macromolecular degradation role, lysosomal membranes
possess a number of ion transport proteins for transferring both cations and
anions between the intralysosomal compartment and the cytoplasm
(Pisoni and Thoene, 1991
;
Chou et al., 1992
;
Dell'Angelica et al., 2000
).
Both proton and calcium ATPases have been described for lysosomal membranes
(Pisoni and Thoene, 1991
;
Chou et al., 1992
). The
V-ATPase was considered responsible for lysosomal acidification, while the
Ca-ATPase may help regulate cytoplasmic calcium activity. Calcium transport by
human lysosomal membranes was inhibited by other divalent cations
(Cd2+>Hg2+>Zn2+>Mg2+>Ba2+>Sr2+),
but appeared insensitive to monovalent and trivalent cations
(Lemons and Thoene, 1991
).
Sulfate2–, phosphate3–,
molybdate4– and Cl– are transported across
vertebrate lysosomal membranes (Pisoni and
Thoene, 1991
; Chou et al.,
1992
). These transport systems are affected by pH and the presence
of other anions on the trans-side of a membrane preparation. Jonas and Jobe
(Jonas and Jobe, 1990
)
described sulfate2– transport across rat liver lysosomal
membrane in exchange for Cl– and suggest the presence of an
anion exchanger in this organelle that is regulated by pH or membrane
potential. Phosphate3– transport in human fibroblast
lysosomes is strongly affected by pH, but appears highly specific as certain
other anions (e.g. SO42–,
HCO3–, Cl– or DIDS) have no
effect on its transfer (Pisoni and Thoene,
1991
). However, arsenate3– was a strong
competitive inhibitor of phosphate3– transport in this system
with both substrate and inhibitor having similar binding constants
(phosphate2– Km=5 µmol
l–1; arsenate2– Ki=7
µmol l–1). None of the studies that characterized anion
transport by lysosomal membranes considered the interactions within the
organelle that may result from the simultaneous transport of divalent ions
from the cytosol.
Another function of lysosomes is the sequestration of heavy metals such as
zinc and copper. Vertebrate lysosomes are known to store zinc by transporting
the metal from cytosol to organelle interior by a Znt2 transport protein
(McMahon and Cousins, 1998
;
Liuzzi and Cousins, 2004
). In
the case of copper, this metal is accumulated in lysosomes as a result of the
activities of copper ATPases (ATP7A and ATP7B) or facilitated diffusion
systems of the Ctr2 or Ctr6 copper transporter isoforms
(Bellemare et al., 2002
).
In invertebrate cells, lysosomes are known to sequester a number of cations of both biological relevance (e.g. calcium, copper, zinc, iron) and non-relevance (e.g. cadmium, mercury, lead) in association with anions such as sulfate2– and phosphate3– in solid concretions that effectively remove them from cytoplasmic or plasma functionality. These concretions may serve as temporary storage facilities for cations involved in frequent physiological operations such as exoskeletal molting in crustaceans, where lysosomal calcium may be periodically mobilized or stored in cells of various tissues as needed to harden the newly synthesized, and still soft, exoskeletal components. Lysosomal storage of biologically important metals such as copper, zinc and iron may occur in similar endosomes side by side with calcium-containing organelles, but metal reclamation from the depots may occur at rates which are dictated by other physiological needs of the animal such as copper requirements in hemocyanin synthesis or zinc needs in efficient enzymatic activities. Lastly, some metals that have no known biological relevance, such as lead, cadmium and mercury, may be accumulated in certain lysosomes and retained there for the life of the cell, eventually being excreted from the animal through the gastrointestinal tract or some other evacuation site, effectively detoxifying the metals through long-term sequestration.
The experiments reported in this study extend those previously reported for
zinc and copper transport by lobster hepatopancreatic lysosomes
(Ahearn et al., 2004a
;
Ahearn et al., 2004b
;
Chavez-Crooker et al., 2003
;
Mandal et al., 2006
) and for
zinc transport by lobster hepatopancreatic endoplasmic reticulum (ER)
(Mandal et al., 2005
). In
these previous studies membranes of both organelles were reported to possess
ATP-dependent, thapsigargin- and vanadate-sensitive calcium and metal
transport systems that were suggested to play a role in regulating cytosolic
concentrations of these divalent cations. The suggestion was made that
apparently different isoforms of the ER SERCA (sarco-endoplasmic reticulum
calcium ATPase) may be localized at the membranes of both organelles and serve
similar regulatory properties in the two sites
(Ahearn et al., 2004b
).
However, the molecular identity of neither transporter was disclosed in these
studies and only their relative pharmacological responses were noted.
Data presented in Figs 1 and
2 suggest that the polyvalent
anions SO42– and PO43–
were more effective in metal accumulation within hepatopancreatic lysosomes
than were uncharged solutes (mannitol), monovalent anions
(Cl–), or divalent organic cations
(oxalate2–). In addition,
Fig. 3 provides, for the first
time, a proposed exchange stoichiometry of the zinc transporter in these
membranes. As a result of the action of an ATP-dependent V-ATPase
(Chavez-Crooker et al., 2003
)
on lysosomal membranes, the interior of these organelles is likely acidic and
the charge across the membrane would be oriented positive inside. The apparent
exchange stoichiometry for the zinc uptake process, as suggested by the
results in Fig. 3, and by the
proposed orientation of membrane potential, would be
3H+/1Zn2+ and could be powered by both ATP and the
membrane potential. Alternatively, it is possible that the asymmetric cation
exchanger is not directly activated by ATP, but is instead only indirectly
linked to the ATP-dependent, V-ATPase through the membrane potential it
generates.
|
Once inside the lysosomal acidic interior both metals and polyvalent anions are able to increase in concentration to values in excess of those in the cytosol. Because the intralysosomal binding sites for both the 3H+/1Zn2+ and 2SO42–/1OH– exchangers prefer monovalent ions, the transfer of either divalent metals or polyvalent anions back to the cytoplasm would be limited and would effectively trap the metals inside lysosomes in a soluble state at acidic pH. Reduction in V-ATPase activity with coincident elevation of lysosomal pH would likely precipitate metal–anion complexes and lead to the formation of a solid concretion that would detoxify the metal by lowering its availability for transfer from the lysosome. The nature of the control process(es) for variation in V-ATPase activity with resultant changes in intralysosomal pH and concretion formation is not known, but would be a fascinating extention of the present study.
The findings of this study are summarized in
Fig. 10, which suggests how
the hepatopancreatic lysosomal V-ATPase may power two electrogenic ion
exchangers through the use of ATP and the induced membrane potential and bring
about the accumulation of metals and polyvalent anions within these
organelles. As shown in the figure, the asymmetric exchange stoichiometries
for metal and SO42– uptake lead to the
accumulation of both ions within the organelle. It is likely that
PO43– may also enter lysosomes by the same
exchanger and be available for concretion formation under the appropriate
conditions (Fig. 1). Previously
published experiments have shown that zinc, copper and cadmium are competitive
inhibitors for transport into hepatopancreatic lysosomal vesicles
(Mandal et al., 2006
) and it
is likely that other divalent metals and calcium are transported out of the
cytosol by this mechanism. The model further suggests that high lysosomal
concentrations of metals and polyvalent anions may condense into a concretion
with a change in pH brought about by alterations in V-ATPase activity.
Several unanswered questions remain about the nature of concretion
formation and heavy metal detoxification by the processes shown in
Fig. 10. The three most
significant are: (1) what is the molecular nature of the ATP-dependent,
electrogenic, metal transporter that exchanges with intralysosomal protons? Is
it a lysosomal isoform of the ER thapsigargin- and vanadate-sensitive calcium
ATPase (e.g. SERCA) (Mandal et al.,
2005
)? Or is it a member of the metal transporting proteins
identified for vertebrate cells such as the Znt2 or ATP7A or ATP7B
(McMahon and Cousins, 1998
;
Liuzzi and Cousins, 2004
;
Vulpe and Packman, 1995
;
Suzuki and Gitlin, 1999
)? (2)
What is the physiological nature of the regulatory process(es) that control(s)
lysosomal pH and therefore regulate(s) whether enclosed metals are soluble or
insoluble? (3) Are there multiple populations of lysosomes within the
hepatopancreas that individually regulate the sequestration of different
cations that are needed for different physiological requirements, as electron
microscopic studies coupled with microprobe analysis of lysosomal contents
have previously suggested (Al-Mohanna and
Nott, 1985
; Al-Mohanna and
Nott, 1989
; Hopkin,
1989
; Nott, 1991
)?
Future experiments will be directed at elucidating some of the answers to
these critical aspects of heavy metal detoxification.
| Acknowledgments |
|---|
| References |
|---|
|
|
|---|
Ahearn, G. A., Mandal, P. K. and Mandal, A. (2004a). Mechanisms of heavy metal sequestration and detoxification in crustaceans: a review. J. Comp. Physiol. B 174,439 -452.[Medline]
Ahearn, G. A., Mandal, P. K. and Mandal, A. (2004b). Organelle-specific zinc ATPases in crustacean ER and lysosomal membranes. Int. Congr. Ser. 1275,114 -125.[CrossRef]
Al-Mohanna, S. Y. and Nott, J. A. (1985). The accumulation of metals in the hepatopancreas of the shrimp, Penaeus semisulcatus de Haan (Crustacea: Decapoda) during the molt cycle. In Marine Environment and Pollution (Proceedings of the First Arabian Conference on Environment and Pollution) (ed. R. Halwagy, D. Clayton and M. Behbehani), pp. 195-209. Kuwait: Kuwait University.
Al-Mohanna, S. Y. and Nott, J. A. (1989). Functional cytology of the hepatopancreas of Penaeus semisulcatus (Crustacea: Decapoda) during the molt cycle. Mar. Biol. 101,535 -544.[CrossRef]
Bellemare, D. R., Shaner, L., Morano, K. A., Deaudoin, J.,
Langlois, R. and Labbe, S. (2002). Ctr6, a vacuolar membrane
copper transporter in Schizosaccharomyces pombe. J. Biol.
Chem. 277,46676
-46686.
Bers, D. M., Patton, C. W. and Nuccitelli, R. (1994). A practical guide to the preparation of Ca2+ buffers. Methods Cell Biol. 40, 3-29.[Medline]
Brouwer, M., Winge, D. R. and Gray, W. R. (1989). Structural and functional diversity of copper-metallothioneins from the American lobster Homarus americanus.J. Inorg. Biochem. 35,289 -303.[CrossRef][Medline]
Brouwer, M., Schlenk, D., Ringwood, A. H. and Brouwer-Hoexum, T. (1992). Metal-specific induction of metallothionein isoforms in the blue crab Callinectes sapidus in response to single and mixed-metal exposure. Arch. Biochem. Physiol. 294,461 -468.[CrossRef]
Chavez-Crooker, P., Garrido, N. and Ahearn, G. A.
(2002). Copper transport by lobster (Homarus americanus)
hepatopancreatic mitochondria. J. Exp. Biol.
205,405
-413.
Chavez-Crooker, P., Garrido, N., Pozo, P. and Ahearn, G. A. (2003). Copper transport by lobster (Homarus americanus) hepatopancreatic lysosomes. Comp. Biochem. Physiol. 135C,107 -118.
Chou, H. F., Vadgama, J. and Jonas, A. J. (1992). Lysosomal transport of small molecules. Biochem. Med. Metab. Biol. 48,179 -193.[CrossRef][Medline]
Dell'Angelica, E. C., Mullins, C., Caplan, S. and Bonifacino, J.
S. (2000). Lysosome-related organelles. FASEB
J. 14,1265
-1278.
Gekle, M. (1998). Renal proximal tubular
albumin reabsorption: daily prevention of albuminuria. News
Physiol. Sci. 13,5
-11.
Hopfer, U., Nelson, K., Perrotto, J. and Isselbacher, K. J.
(1973). Glucose transport in isolated brush border membrane from
rat small intestine. J. Biol. Chem.
248, 25-32.
Hopkin, S. P. (1989). Ecophysiology of Metals in Terrestrial Invertebrates. London: Elsevier Applied Science.
Jonas, A. J. and Jobe, H. (1990). Sulfate
transport by rat liver lysosomes. J. Biol. Chem.
265,17545
-17549.
Kielland, J. (1937). Individual activity coefficients of ions in aqueous solutions. J. Am. Chem. Soc. 59,1657 -1678.[CrossRef]
Liuzzi, J. P. and Cousins, R. J. (2004). Mammalian zinc transporters. Annu. Rev. Nutr. 24,151 -172.[CrossRef][Medline]
Lemons, R. M. and Thoene, J. G. (1991).
Mediated calcium transport by isolated human fibroblast lysosomes.
J. Biol. Chem. 266,14378
-14382.
Mandal, P. K., Mandal, A. and Ahearn, G. A. (2005). Physiological characterization of 45Ca2+ and 65Zn2+ transport by lobster hepatopancreatic endoplasmic reticulum. J. Exp. Zoolog. Part A Comp. Exp. Biol. 303,515 -526.[Medline]
Mandal, P. K., Mandal, A. and Ahearn, G. A. (2006). 65Zn2+ transport by lobster hepatopancreatic lysosomal membrane vesicles. J. Exp. Zoolog. Part A Comp. Exp. Biol. 305,203 -214.[Medline]
McMahon, R. J. and Cousins, R. J. (1998).
Mammalian zinc transporters. J. Nutr.
128,667
-670.
Nott, J. A. (1991). Cytology of pollutant metals in marine invertebrates: a review of microanalytical applications. Scanning Microsc. 5,191 -204.[Medline]
Pisoni, R. L. and Thoene, J. G. (1991). The transport systems of mammalian lysosomes. Biochim. Biophys. Acta 1071,351 -373.[Medline]
Roesijadi, G. and Robinson, W. E. (1994). Metal regulation in aquatic animals: mechanisms of uptake, accumulation, and release. In Aquatic Toxicology (ed. D. C. Malins and G. K. Ostrander), pp. 387-420. Boca Raton: Lewis Publishers.
Suzuki, M. and Gitlin, J. D. (1999). Intracellular localization of the Menkes and Wilson's disease proteins and their role in intracellular copper transport. Pediatrics Int. 41,436 -442.[CrossRef]
Viarengo, A. (1989). Heavy metals ion marine invertebrates: mechanisms of regulation and toxicity at the cellular level. Rev. Aquatic Sci. 1,295 -317.
Vulpe, C. D. and Packman, S. (1995). Cellular copper transport. Annu. Rev. Nutr. 15,293 -322.[Medline]
Zhou, X., Thamaotharan, M., Gangopadhyay, A., Serdikoff, C. and Adibi, S. A. (2000). Characterization of an oligopeptide transporter in renal lysosomes. Biochim. Biophys. Acta 1466,372 -378.[Medline]
| |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||