|
|
|
|||
| Home Help Feedback Subscriptions Archive Search Table of Contents | ||||
First published online March 14, 2008
Journal of Experimental Biology 211, 1063-1074 (2008)
Published by The Company of Biologists 2008
doi: 10.1242/jeb.010181
The effect of hypoxia on gill morphology and ionoregulatory status in the Lake Qinghai scaleless carp, Gymnocypris przewalskii

1 Department of Biology, San Diego State University, San Diego, CA, USA
2 Department of Zoology, University of British Columbia, Vancouver, BC, V6T 1Z4,
Canada
3 Department of Biology, Queen's University, Kingston, Ontario, KZP 3N6,
Canada
4 Department of Biology, McMaster University, Hamilton, Ontario, L8S 4K1,
Canada
5 Ecosystem Science and Management Program, University of Northern British
Columbia, Prince George, BC, V2N 4Z9, Canada
6 Department of Biotechnology, Life Science College, Zhejiang University,
Hangzhou, Zhejiang 310027, People's Republic of China
*Author for correspondence in Chinese (e-mail:
dujz{at}zju.edu.cn)
Author for correspondence (e-mail:
brauner{at}zoology.ubc.ca)
Accepted 30 January 2008
| Summary |
|---|
|
|
|---|
Key words: gill morphology, hypoxia, ionoregulation, mitochondria rich cell, osmorespiratory compromise
| INTRODUCTION |
|---|
|
|
|---|
The presence of such a large interlamellar mass in normoxia has been
proposed as a mechanism for reducing water and/or ion fluxes across the gills,
while still providing a sufficient surface for gas exchange. The reduced
diffusion capacity of the gills in normoxia is partially compensated for by a
very high blood oxygen affinity in the crucian carp
(Sollid et al., 2005
). The
goldfish at low temperature also exhibits a large interlamellar mass in
normoxia that is greatly reduced in hypoxia. Both crucian carp and goldfish
(Carassius carassius) are renowned for their hypoxia tolerance, which
is at least in part related to their high blood–oxygen affinity
(Sollid et al., 2005
) and the
latter may be a prerequisite for the possession of a low gill surface area in
normoxia.
Although gross morphological changes in the gills of carp and goldfish
during exposure to hypoxia have been relatively well documented, changes to
specialized cells in the gill epithelium during exposure to hypoxia and
associated gill remodeling have been largely unexplored but are likely of
great significance during acclimation. The complex epithelium of the gill
consists primarily of mitochondria-rich cells (MRC), pavement cells (PVC) and
mucous cells (MC). Current morphological classification of ion transporting
MRCs is based on their surface topography, internal ultrastructure, and
location in the filament epithelium
(Perry, 1997
;
Wilson and Laurent, 2002
;
Evans et al., 2005
). Based upon
surface structure, there appear to be three types of MRCs in the gill and
operculum epithelia (Lee et al.,
1996
; Chang et al.,
2001
; Chang et al.,
2002
; Shieh et al.,
2003
). These are the `deep-hole' MRCs with a distinctive apical
crypt, formed by a deeply invaginated apical membrane recessed below
neighboring cells; the `shallow-basin' MRCs with a slightly recessed or flat
apical surface; and the `wavy-convex' MRCs which possess a convex apical
membrane with wavy microvilli extending above neighboring cells. Based upon
their ultrastructure, association with different parts of gill circulatory
system, and cytoplasm density, MRCs have been classified as
and β
forms, respectively (Pisam et al.,
1987
).
-MRCs are concentrated predominantly at the base of
the lamella in contact with arterio-arterial circulation whereas β-MRCs
are located in the interlamellar regions in contact with arterio-venous
circulation. The `light' cytoplasm of
cells contains more numerous
mitochondria and more branched tubular reticulum (TR) bearing
Na+-K+-ATPase and Ca2+-ATPase than β
cells (Wilson and Laurent,
2002
). Recently described PNA-positive MRCs that were
distinguished from other MRCs by their ability to bind peanut-lectin
agglutinin (PNA) and called β cells
(Goss et al., 2001
;
Hawkings et al., 2004
), fit the
description of
cells defined by Pisam et al.
(Pisam et al., 1987
). It is
still not clear whether
and β cells represent different subtypes
of the MRC or different developmental stages in the life cycle of these cells
(Wendelaar Bonga and van der Meij,
1989
; Perry,
1997
).
The most prominent feature of the PVC is the complex pattern of microridges
that expand the area of interaction between the cell surface and ambient
water. PVC cytoplasm contains few mitochondria, well-developed rough
endoplasmic reticulum, and Golgi apparatus that produce microvesicles with an
electron-dense core consisting of glycoproteins
(Laurent and Perry, 1991
;
Wilson and Laurent, 2002
).
When these vesicles fuse with the apical cell membrane, glycoproteins are
released to the cell surface and become a component of the glycocalyx or
mucous layer. Specialized MCs produce granules of polyanionic mucous
containing glycoproteins, mucopolysacharides and carbohydrates
(Shephard, 1994
). When
granules are discharged and burst onto the epithelial surface, their content
forms a mucous layer that might be part of the stress response in fish, or may
participate in ion and water balance
(Shephard, 1994
;
Wendelaar Bonga, 1997
). In a
number of teleost fish, the gill epithelium contains rodlet cells (RCs),
however, their origin and function remain unknown. They have been proposed to
act as non-specific immune cells (Manera
and Dezfuli, 2004
) or have a secretory function based upon the
presence of rodlet granules rich in glycoproteins and carbohydrates that are
released on the epithelial surface (Leino,
1982
; Leino, 2001
;
Matey, 1996
).
The scaleless carp (Gymnocypris przewalskii) is an endangered
species that inhabits Lake Qinghai, a saline (9–13 p.p.t.), alkaline (pH
9.3) lake on the Qinghai–Tibet plateau at 3200 m. At this altitude,
air and water O2 tensions are about 60% those at sea-level and
thus, fish are exposed to chronically reduced O2 levels
(approximately 6 mg O2 l–1). Mean annual air
temperature is –0.6°C, and surface lake water temperatures rarely
exceed 13°C in August (Walker et al.,
1996
). The scaleless carp, however, has an interesting life
history relative to most carp species, in that it undergoes an annual spawning
migration from the lake into freshwater rivers
(Wang et al., 2003
;
Wood et al., 2006
) when they
swim 40–50 km over several weeks before reaching their spawning grounds
(Walker et al., 1996
). Thus,
although this species inhabits moderately hypoxic, cool waters, like those of
crucian carp or goldfish, it is dependent upon exercise to reach its spawning
ground and its body form is superficially more salmonid-like than
carp-like.
The objective of this study was to test the hypothesis that gill remodeling
during hypoxia is a general characteristic of cold water-dwelling carp, and
gill remodeling in hypoxia is associated with an ionoregulatory disturbance.
Because the scale-less carp resides in moderate hypoxia (i.e. 3200 m) and has
an active lifestyle, the degree of remodeling was expected a priori
to be reduced relative to that of carp and goldfish
(Sollid et al., 2003
;
Sollid et al., 2005
). Special
attention was paid to the ultrastructure of filament epithelium cells, such as
MRCs, PVCs, MCs and RCs, as in previous studies investigating the effect of
hypoxia on gill remodeling, this has not been examined. Fish were collected
during their annual spawning migration, allowed to recover for several days,
and then exposed to hypoxia (0.3 mg O2 l–1 at
11–15°C) to probe the relative morphological changes of the gills in
general, and gill epithelia in particular. Plasma ion levels were measured
during exposure to hypoxia to determine the degree to which ionoregulatory
status was affected during hypoxia. The scaleless carp is currently listed as
endangered, and thus any information that can be gained about its physiology
may be important to conservation of this species.
| MATERIALS AND METHODS |
|---|
|
|
|---|
Hypoxia exposure and sampling
The night prior to experiments, 30 fish were transferred to each of two 160
l exposure chambers and left overnight in flow-through, aerated well-water.
Hypoxia was achieved by covering the surface of the water with translucent
plastic and bubbling the water with nitrogen. Water [O2] decreased
from aerated values of 6 mg l–1 (approximately 60% of sea
level values at 3200 m but referred to as normoxia throughout this study) to
0.3 mg O2 l–1 (N=10) over the first 1 h
of bubbling and then were maintained at 0.3 mg O2
l–1 in both of the chambers for the duration of the hypoxic
exposure during which time water O2 level was continuously
monitored using a YSI-85 dissolved oxygen meter (Yellow Springs, OH, USA).
Three or four fish were removed from each replicate chamber at 0, 4, 8, 12 and
24 h of hypoxia, or 6 and 12 h after being transferred back to aerated water
(N=7 per treatment). Upon removal, fish were immediately euthanized
using neutralized MS-222 and terminally sampled. Blood was removed from the
caudal vein into a heparinized syringe and plasma was separated and frozen for
later ion analysis (at McMaster University, Hamilton, ON, Canada). Plasma
Na+, K+, Ca2+, Mg2+ were measured
using atomic absorption spectrophotometery (AAS; Varian AA 1275, Mississauga,
ON, Canada) and plasma Cl– was measured using the
colorimetric mercuric thiocyanate method
(Zall et al., 1956
). The
second gill arch from the right hand side of four fish from each treatment
were dissected out, rinsed, and immediately fixed in cold Karnovsky's fixative
and transported to San Diego State University, CA, USA (SDSU) for later
scanning electron microscopy (SEM), transmission electron microscopy (TEM) and
light microscopy (LM) as described below. The second gill arch from the left
hand side of the fish was immediately frozen for later measurement of gill
caspase 3 activity (commonly used as a biomarker for apoptosis) at Queens
University, Kingston, ON, Canada, according to the instruction of the Enzcheck
Caspase 3 Assay Kit no. 1 [Z-DEVD-amino-4-methylcumorin (AMC) substrate, cat.
no. E13183, Molecular Probes, Invitrogen, Carlsbad, CA, USA] with the
following modification. Frozen gill tissue was homogenized in 1x cell
lysis buffer (pH 7.5, 1 mmol l–1 EDTA, 0.01% Triton X-100).
7-AMC reference standards were made in a 1:1 volume ratio of 1x reaction
buffer (pH 7.4, 10 mmol l–1 Pipes, 2 mmol
l–1 EDTA, 0.1% CHAPS) and 1x cell lysis buffer. The
caspase 3 activities were assayed by measuring fluorescence
(excitation/emission, 342/441 nm) using a 96-well fluoremeter (Molecular
Devices, Sunnyvale, CA, USA). The caspase 3 activities were expressed as AMC
min–1 mg–1 protein, where protein content in
the homogenate was measured using the bicinchoninic acid (BCA) assay.
Morphological analyses
At SDSU the middle part of each fixed gill arch (
5 mm long) bearing up
to 20 filaments in both anterior and posterior rows was used for scanning
electron microscopy. Individual filaments were cut for transmission electron
microscopy and light microscopy studies. All fixed gill tissue was rinsed in
phosphate-buffered saline (PBS), and post-fixed in 1% osmium tetroxide for 1
h.
Scanning electron microscopy
Gill tissue was dehydrated in ascending concentrations of ethanol from 30%
to 100%, critical-point dried with liquid CO2, mounted on stubs,
sputter-coated with gold–palladium, and examined with a Hitachi S 2700
scanning electron microscope at the accelerating voltage of 20 kV.
Transmission electron microscopy and light microscopy
Samples were dehydrated in a graded ethanol–acetone series to 100%
acetone and embedded in Epon epoxy resin. Longitudinal semi-thin (1 µm) and
ultra-thin (60–70 nm) sections were prepared parallel to the long axis
of the filaments and cut with an ultramicrotome (EM-Leica microtome,
Bannockburn, IL, USA). Semi-thin sections for LM analyses were mounted on
glass slides, stained with 0.5% Methylene Blue and examined in a Nikon Eclipse
E200 microscope (Melville, NY, USA). Ultra-thin sections for TEM analyses were
mounted on the copper grids, double stained with 2% uranyl acetate, followed
by 1% lead citrate, and examined in a Tecnai 12 transmission electron
microscope (FEI) at the accelerating voltage of 80 kV.
Morphometry
Various gill parameters were measured in control and experimental fish.
These included: (1) protruding lamellar height in contact with ambient water
(by LM); (2) lamellar thickness (by LM); (3) protruding lamellar basal length
(by SEM); (4) water–blood diffusion distance, from the outer edge of the
lamellar epithelium to the inner edge of the endothelium of the lamellar blood
vessel (by TEM); (5) thickness of filament epithelium, from the outer edge of
the filament to the basal lamina (by LM); (6) number of cell nuclei in the
interlamellar space between two neighboring lamellae (by LM); and (7) diameter
of apical crypts of MRCs (by SEM). A total of 30 measurements (in ten randomly
selected lamellae in three fish, and ten randomly selected filaments in three
fish) of each of these parameters was performed in each experimental and
control group. The surface area of protruding lamellae (functional respiratory
surface) in both control and experimental fish was approximated to a half
ellipse and calculated according to the formula proposed by Sollid et al.
(Sollid et al., 2003
). Three
measurements were used for these calculations: (1) basal length of the
protruding part of lamellae (l); (2) the height of the protruding
part of lamellae (h); (3) the thickness of lamellae (t). The
respiratory surface area of lamella was calculated as a=pl,
where p is the ellipse perimeter formula divided by 2:
![]() |
Statistical analyses
Morphometric data, gill caspase 3 activity, and plasma [Na+] and
[Cl–] levels were expressed as means ±1 s.e.m. and
analyzed by one-way ANOVA followed by a post-hoc Dunnet's test to
identify means that were significantly different (P<0.05) from
normoxic control values.
| RESULTS |
|---|
|
|
|---|
|
|
|
|
|
Following 6 h recovery, noticeable reversible changes in gill morphology were observed. Filament epithelium thickness was slightly increased, resulting in a reduction in protruding lamellar height, length and surface area (Fig. 3A,C; Table 1). While lamellae became thicker, water–blood diffusion distance remained thin (Fig. 3B). The reduction of exposed respiratory lamellar surface area, the thickness of filament epithelium and water–blood diffusion distance approached that of 8 h hypoxia exposed fish (Fig. 1D, Fig. 2D, Fig. 3; Table 1), however, recovery was not complete within 12 h exposure to normoxia.
|
- and β-MRCs were present in the filament
epithelium of the scaleless carp (Fig.
5D,E).
-MRCs predominated and their apical surface
exhibited either long and highly ramified or short and slightly branched
microvilli (Fig. 5B,C). The
apical surface of β-MRCs possessed only short and slightly branched
microvilli. In PVCs, the apical surface was complex and consisted of long microridges (Fig. 5A). The cell cytoplasm contained numerous microvesicles with an electron-dense filamentous core (Fig. 6A). Fully developed MCs were located in the outermost layer of the filament epithelium and were filled with numerous secretory granules of different electron density (Fig. 6B). There were large pores through which granules can be discharged on the epithelial surface (Fig. 5A). A few developing oval to circular RCs were located in the basal and intermediate layers of the filamental epithelium. They had no access to the epithelial surface but contained rodlet granules in various stages of maturity, with extensively developed rough endoplasmic reticulum and Golgi apparatus (Fig. 6C).
|
-MRCs
were located in the outermost epithelial layer and contained swollen
mitochondria, poorly branched tubular reticulum with irregular meshes, and a
high density of ribosomes (Fig.
8A). However, the vast majority of
-MRCs did not show any
changes in ultrastructure except for an unusually high density of apical
microvesicles (Fig. 8B). No
changes were observed in the ultrastructure of the less abundant β-MRCs.
Following 8 h exposure to hypoxia, MRCs consisted mainly of the
-subtype with smaller apical crypts (8.7x5.4 µm) and short and
`stumpy' surface microvilli (Fig.
7B, Fig. 8C).
Abundant microvesicles were not concentrated exclusively in the apical area
but were distributed along the cell up to its perinuclear area
(Fig. 8C). No MRCs with altered
organelles were observed in the epithelium.
|
|
Following 12 h exposure to hypoxia, the epithelial surface exhibited
numerous small and deep openings (2.8x1.4 µm) with the appearance of
apical crypts of `deep-hole' MRCs (Fig.
7C). However, TEM revealed that these were not deep-hole but
`shallow-basin' MRCs. They had flat apical surfaces bearing a few short and
wide microvilli and were situated below neighboring PVCs on the bottom of the
cavities formed with the flanks of PVCs
(Fig. 8D). MRCs remained
predominantly of the
subtype and contained numerous apical
microvesicles located beneath a flattened apical membrane
(Fig. 8E). Following 24 h,
numerous typical shallow-basin MRCs with large variations in size (from
3.0x2.2 µm to 7.6x3.9 µm) and shape of apical crypts opened
directly onto the epithelial surface (Fig.
7D). Few microvesicles were located in the apical area of these
MRCs (Fig. 8F). The
ultrastructure of both
-MRCs (which still predominated) and β-MRCs
did not differ from those in control fish.
Pavement cells
Following 4–8 h of exposure to hypoxia, the surface of most PVCs
consisted of shorter, less branched microridges and an expanded
microridge-free central area, whereas the remaining PVCs had a surface similar
to that of control fish (Fig.
7A,B). At 12–24 h exposure to hypoxia, PVCs displayed a
dense array of short microvilli partially or completely masked by mucous
(Fig. 7C,D). No alterations
were observed in the ultrastructure of PVCs where the cytoplasm was saturated
with microvesicles containing an electron-dense core.
Mucous cells and rodlet cells
Following 4 h exposure to hypoxia, MCs appeared to have released mucous
that partially masked the convex apical surface and filled apical crypts of
the MRCs, complicating identification of MRCs under SEM
(Fig. 7B). Patches of thick
mucous were deposited on the epithelial surface following 12 h exposure to
hypoxia (Fig. 7C). Following 24
h exposure to hypoxia, a thick film of mucous precipitated within the MRC
apical cavities, filled spaces between PVCs and covered a large area of the
gill filaments (Fig. 7D). TEM
indicated groups of two or more MCs filled with secretory granules and
numerous RCs at the secretory stage located in the outermost epithelial layer
which opened directly on to the apical surface
(Fig. 9B,C).
|
Recovery
After 6 h recovery in normoxia, MRCs consisted of a few shallow-basin and
numerous wavy-convex forms. The former had slightly concave large apical
crypts (6.2x5.5 µm) with few long branched microvilli masked by
mucous (Fig. 10A,B).
Wavy-convex MRCs with smaller apical crypts (4.4x3.7 µm) possessed
short and wide microvilli (Fig.
10A,C). As in hypoxia-exposed fish, shallow-basin MRCs with few
apical microvesicles and wavy-convex MRCs without microvesicles consisted
mostly of
-MRC (Fig.
10B,C). Following 12 h recovery, shallow-basin MRCs almost
disappeared, and wavy-convex MRCs were opened on to the epithelial surface
(Fig. 10D–F). Some MRCs
had smaller apical crypts (6.9x5.0 µm) and possessed long, highly
ramified microvilli, whereas others had larger apical crypts (8.3x5.3
µm) with short and slightly branched microvilli. The epithelial surface was
free of mucous that was concentrated only within the crypts of shallow-basin
MRCs, similar to that seen following 6 h of recovery. Fewer MCs and solitary
RCs were observed in the outermost layers of the filament epithelium. The
ultrastructure of PVCs were similar to that following 8 h exposure to hypoxia,
exhibiting a simple pattern of short microridges with a microridge-free
central zone and abundant microvesicles with an electron-dense core within the
cytoplasm (Fig. 10A,D).
|
|
| DISCUSSION |
|---|
|
|
|---|
The adjustments to hypoxia, which include the morphological changes in the
gills, along with possible changes in gill ventilation and perfusion, were
associated with up to a 10 and 15% reduction in plasma Na+ and
Cl– levels, respectively, indicating that these adjustments
to secure O2 uptake have a negative effect on the ionoregulatory
status of the fish. Interestingly this was not the case with other ions
(Mg2+, Ca2+ and K+), however, these ions
occur at much lower concentrations where small changes of 10–15% may not
be detectable. There was an increase in plasma [K+] during hypoxia,
which may be indicative of cell damage or muscle depolarization, however,
further studies are required to investigate this. The concept of the
osmorespiratory compromise was originally developed to describe the trade-off
between gas exchange and ionoregulatory requirements during exercise in fish
(e.g. Gonzalez and McDonald,
1992
). However, the present data illustrate that it applies
equally well during hypoxia. Indeed the consequences of the compromise for
ionoregulation during hypoxia (approximately 10–15% loss of plasma ions
in 24 h) appear to be far greater in the scaleless carp than seen in recent
studies on a very hypoxia-tolerant teleost, the Amazonian oscar
(Richards et al., 2007
;
Wood et al., 2007
). Thus,
although changes in gill morphology during hypoxia probably contribute greatly
to hypoxia tolerance in this and other species, the maintenance of this high
gill diffusion capacity would probably be a liability to ionoregulation.
The expansion of respiratory lamellae surface area in the scaleless carp is
associated with the reduction of filament epithelium thickness due to removal
of the interlamellar mass, consistent with the data of Sollid and co-workers
(Sollid et al., 2003
). Whereas
in the crucian carp it is caused by depression of cell proliferation and
activation of apoptotic activity of the filament epithelium, in the scaleless
carp it may be caused by cell shedding from the outermost epithelial layer.
The number of cell nuclei in the interlamellar epithelium decreased by almost
40% after 24 h exposure to hypoxia and became elevated by 30% (relative to 24
h hypoxia) after 12 h of recovery in normoxic water
(Table 1). The removal of the
interlamellar mass in the scaleless carp may also involve apoptotic pathways
as there was a significant elevation in caspase 3 activity (which is commonly
used as a biomarker for apoptosis) following 24 h exposure to hypoxia.
However, this elevation occurred at a time when most of the morphological
changes neared completion and there were no morphological indicators of
apoptosis such as nuclear and cytoplasm condensation and distention of
mitochondria and components of tubular reticulum
(Sardella et al., 2004
). In
contrast to the cyprinids, morphological changes in the gills during exposure
to hypoxia have also been seen in the zebrafish, however, the mechanism
appears to be different. During hypoxia there is cell proliferation within the
respiratory lamellae combined with a reduction in cell size and change in the
cell surface, leading to an extension of the lamellar respiratory surface that
correlates with changes in gene expression patterns
(van der Meer et al.,
2005
).
Specific changes in filament epithelial cells during hypoxia
Hypoxia clearly induced overproduction and deposition of mucous on the gill
surface of exposed fish, which is a generalized response of fish gills to a
range of environmental stressors (Mallatt,
1985
; Wendelaar Bonga,
1997
). Although specialized mucous cells were likely predominantly
responsible for the mucous production, other cells may also have contributed.
For example, rodlet cells in the secretory stage were observed in close
proximity to the mucous cells following 24 h of hypoxia and it is thought that
the contents of discharged rodlet granules are mixed with the secretion of MCs
becoming a component of gill mucus (Leino,
1982
). PVCs possess numerous glycoprotein-containing microvesicles
that can fuse to the apical membrane and release their content on the gill
surface, and may also have contributed to gill mucous production
(Laurent and Perry, 1991
). The
role of mucous deposition on the gill surface of the scaleless carp during
hypoxia is not clear. Although we did not observe the presence of mucous on
the lamellar surfaces, the layer of mucous covering gill filaments could be
distributed along the gill surface, cover the lamellae, and impair gas
diffusion through the respiratory epithelium. However, because of its acidity,
polyanionic mucous has been proposed to increase local ion concentrations at
the gill surface, facilitate ion exchange and limit water influx
(Handy et al., 1980
;
Shephard, 1994
). Thus, mucous
may actually reduce the magnitude of the ionoregulatory disturbance associated
with the changes in gill morphology noted above, but this clearly requires
further investigation.
Acute hypoxia exposure affected MRC morphology, reducing the apical surface area that was exposed to ambient water. In normoxic water, MRCs were exclusively of the wavy-convex type, which have a large surface area and microvilli that may be either long and branched or short and straight. Exposure to hypoxia led to the disappearance of large MRCs with long and highly branched microvilli. Following 4–8 h of exposure to hypoxia, MRCs with larger apical crypts but few short, wide and slightly branched or stumpy microvilli were opened onto the epithelial surface. TEM revealed a high density of apical microvesicles directly under the apical membrane, indicating that portions of the MRC deeply folded apical membrane were pinched off, forming microvesicles that remained in the apical zone and spread along the MRC cytoplasm. This would limit the extent of the cell surface and resulted in a more smooth appearance. As a result wavy-convex MRCs were transformed into shallow-basin MRCs following 12 h of hypoxia exposure. At this time the shallow-basin MRCs were almost completely covered with neighboring PVCs and had limited access to ambient water. Given that the apical membrane of MRCs is the site for active ion uptake from the water, a reduction in apical surface area may contribute to the progressive reduction in plasma [Na+] and [Cl–] observed during hypoxia.
The alterations in apical morphology of the MRCs were reversible. When fish
were returned to normoxic water, MRCs restored their complex surface
structure. We hypothesize that this occurred through the fusion of
microvesicles (formed from MRC apical membrane removed during hypoxia) with
the apical cell membrane. These data indicate that MRCs may regulate their
apical surface in response not only to the ionic composition of the water,
which has been well documented (Lee et
al., 1996
; Lee et al.,
2000
; Chang et al.,
2001
; Chang et al.,
2002
; Shieh et al.,
2003
), but also in response to the oxygen levels of ambient
water.
Although hypoxia exposure had a pronounced effect on the apical surface
architecture of MRCs, it did not significantly change the internal structure
of both the
- and β-type MRCs. Ultrastructure of mitochondria and
tubular reticulum and key organelles of MRCs directly linked with ionic
regulation appeared similar in control and hypoxia-exposed fish. We
hypothesize that the reduction of plasma [Na+] and
[Cl–] during exposure to hypoxia is probably a result of the
dramatic increase in total gill surface area and the osmorespiratory
compromise in conjunction with the reduction in MRC apical surface exposed to
the ambient water. Although the former represents a prioritization of gas
exchange over ionoregulation during exposure to hypoxia, the basis for the
reduction in MRC microvilli during hypoxia is less clear. The large
morphological changes in the gill observed in the scaleless carp support the
hypothesis that gill remodeling during hypoxia is a general characteristic of
cold water carp species and is associated with an ionoregulatory disturbance,
however, the reduced magnitude of the response in scaleless carp relative to
goldfish and crucian carp may be a reflection of their more active lifestyle
or because they reside in a moderately hypoxic environment at altitude.
| Acknowledgments |
|---|
| References |
|---|
|
|
|---|
Brauner, C. J., Matey, V., Wilson, J. M., Bernier, N. J. and
Val, A. L. (2004). Transition in organ function during the
evolution of air-breathing; insights from Arapaima gigas, an obligate
air-breathing teleost from the Amazon. J. Exp. Biol.
207,1433
-1438.
Chang, I. C., Lee, T. H., Yang, C. H., Wei, Y. Y., Chou, F. I. and Hwang, P. P. (2001). Morphology and function of gill mitochondria-rich cells in fish acclimated to different environments. Physiol. Biochem. Zool. 74,111 -119.[CrossRef][Medline]
Chang, I. C., Lee, T. H., Wu, H. C. and Hwang, P. P. (2002). Effect of environmental Cl– levels on Cl– uptake and mitochondria-rich cell morphology in gills of the stenohaline goldfish, Carassius auratus. Zool. Stud. 41,236 -243.
Evans, D. H., Piermarini, P. M. and Choe, K. P.
(2005). The multifunctional fish gills: dominant site for gas
exchange, osmoregulation, acid-base regulation, and excretion of nitrogenous
waste. Physiol. Rev. 85,97
-177.
Gonzalez, R. J. and McDonald, D. G. (1992). The
relationship between oxygen consumption and ion loss in a freshwater fish.
J. Exp. Biol. 163,317
-332.
Goss, G. G., Adamia, S. and Galvez, F. (2001). Peanut lectin binds to a subpopulation of mitochondria-rich cells in the rainbow trout epithelium. Am. J. Physiol. 281,R1718 -R1725.
Handy, R. D., Eddy, F. B. and Romain, G. (1980). In vitro evidence for the ionoregulatory role of rainbow trout mucus in acid, acid/aluminium and zinc toxicity. J. Fish Biol. 35,737 -747.[CrossRef]
Hawkings, G. S., Galvez, F. and Gross, G. G.
(2004). Seawater acclimation caused independent alterations in
Na+/K+- and H+-ATPase activity in isolated
mitochondria-rich cell subtypes of the rainbow trout gill. J. Exp.
Biol. 207,905
-914.
Laurent, P. and Perry, S. (1991). Environmental effects on fish gill morphology. Physiol. Zool. 64, 4-25.
Lee, T. H., Hwang, P. P., Lin, H. C. and Hung, F. L. (1996). Mitochondria-rich cells in the branchial epithelium of the teleosts, Oreochromis mossambicus, acclimated to various hypotonic environments. Fish Physiol. Biochem. 15,513 -523.[CrossRef]
Lee, T. H., Hwang, P. P., Shieh, Y. E. and Lin, C. H. (2000). The relation between "deep-hole" mitochondria-rich cells and salinity adaptation in the euryhaline teleosts, Oreochromis mossambicus. Fish Physiol. Biochem. 23,133 -140.[CrossRef]
Leino, R. L. (1982). Rodlet cells in the gill and intestine of Catostomus commersoni and Perca flavescens: a comparison of their light and electron microscopic cytochemistry with that of mucus and granular cells. Can. J. Zool. 60,2768 -2782.
Leino, R. L. (2001). Formation and release of the secretory product in rodlet cells. Proceedings of the First International Rodlet Cell Workshop. June 14-16, Ferrara, Italy, p6 .
Mallatt, J. (1985). Fish gill structural changes induced by toxicants and other irritants: a statistical review. Can. J. Fish. Aquat. Sci. 42,630 -648.
Manera, M. and Dezfuli, B. S. (2004). Rodlet cells in teleosts: a new insight into their nature and functions. J. Fish Biol. 65,597 -619.[CrossRef]
Matey, V. E. (1996). Gills of freshwater teleost fishes: morphofunctional organization, adaptation, and evolution. St. Petersburg: Nauka. [in Russian].
Ong, K. J., Stevens, E. D. and Wright, P. A.
(2007). Gill morphology of the mangrove killifish
(Kryptolebias marmoratus) is plastic and changes in response to
terrestrial air exposure. J. Exp. Biol.
210,1109
-1115.
Perry, S. F. (1997). The chloride cell: structure and functions in the gills of freshwater fishes. Annu. Rev. Physiol. 59,325 -347.[CrossRef][Medline]
Pisam, M., Caroff, A. and Rambourg, A. (1987). Two types of chloride cells in the gill epithelium of freshwater-adapted euryhaline fish, Lebistes reticulatus; their modifications during adaptation to seawater. Am. J. Anat. 179, 40-50.[CrossRef][Medline]
Richards, J. G., Wang, Y. S., Brauner, C. J., Gonzalez, R. J., Patrick, M. L., Schulte, P. M., Choppari-Gomes, A. R., Almeida-Val, V. M. and Val, A. L. (2007). Metabolic and ionoregulatory responses of the Amazonian cichlid, Astronotus ocellatus, to severe hypoxia. J. Comp. Physiol. B 177,361 -374.[CrossRef][Medline]
Sardella, B. A., Matey, V., Cooper, J., Gonzalez, R. J. and
Brauner, C. J. (2004). Physiological, biochemical and
morphological indicators of osmoregulatory stress in `California' Mozambique
tilapia (Oreochromis mossambicus x O. urolepis
hornorum) exposed to hypersaline water. J. Exp.
Biol. 207,1399
-1413.
Shephard, K. L. (1994). Functions for fish mucus. Rev. Fish Biol. Fish. 4, 401-429.[CrossRef]
Shieh, Y. E., Tsai, R. S. and Hwang, P. P. (2003). Morphological modification of mitochondria-rich cells of the opercular epithelium of freshwater tilapia, Oreochromis mossambicus.Zool. Stud. 42,522 -528.
Sollid, J. and Nilsson, G. E. (2006). Plasticity of respiratory structures: adaptive remodeling of fish gills induced by ambient oxygen and temperature. Respir. Physiol. Neurobiol. 154,241 -251.[CrossRef][Medline]
Sollid, J., De Angelis, P., Gundersen, K. and Nilsson, G.
(2003). Hypoxia induced adaptive and reversible gross
morphological changes in crucian carp gills. J. Exp.
Biol. 206,3667
-3673.
Sollid, J., Weber, R. E. and Nilsson, G. E.
(2005). Temperature alters the respiratory surface area of
crucian carp Carassius carassius and goldfish Carassius auratus.J. Exp. Biol. 208,1109
-1116.
Van der Meer, D. L., van der Thillart, G. E. E. J. M., Witte, F., de Bakker, M. A. G., Besser, J., Richardson, M. K., Spaink, H. P., Leito, J. T. D. and Bagowski, C. P. (2005). Gene expression profiling of the long-term adaptive response to hypoxia in the gills of adult zebrafish. Am. J. Physiol. 289,R1512 -R1519.
Walker, K. F., Dunn, I. G., Edwards, D., Petr, T. and Yang, H. Z. (1996). A fishery in a changing lake environment: the naked carp Gymnocypris przewalskii (Kessler) (Cyprinidae: Schizothoracinae) in Qinghai Hu, China. Int. J. Salt Lake Res. 4,169 -222.[CrossRef]
Wang, Y. S., Gonzalez, R. J., Patrick, M. L., Grosell, M., Zhang, C., Feng, Q., Du, J., Walsh, P. J. and Wood, C. M. (2003). Unusual physiology of scale-less carp, Gymnocypris przewalskii, in Lake Qinghai: a high altitude alkaline saline lake. Comp. Biochem. Physiol. 134A,409 -421.
Wendelaar Bonga, S. (1997). The stress response
in fish. Physiol. Rev.
77,591
-625.
Wendelaar Bonga, S. E. and van der Meij, C. J. M. (1989). Degeneration and death, by apoptosis and necrosis, of the pavement and chloride cells in the gills of teleost Oreochromis mossambicus. Cell Tissue Res. 255,235 -243.
Wilson, J. M. and Laurent, P. (2002). Fish gill morphology: inside out. J. Exp. Zool. 293,192 -213.[CrossRef][Medline]
Wood, C. M., Du, J., Rogers, J., Brauner, C. J., Richards, J. G., Semple, J. W., Murray, B. W., Chen, X-Q and Wang, Y. (2006). Przewalski's naked carp (Gymnocyypris przewalski): an endangered species taking a metabolic holiday in Lake Qinghai, China. Physiol. Biochem. Zool. 80, 59-77.[CrossRef]
Wood, C. M., Kajimura, K., Sloman, K. A., Scott, G. R., Almeida-Val, F. F. and Val, A. L. (2007). Rapid regulation of Na+ fluxes and ammonia excretion in response to severe hypoxia in the amazonian oscar, Astronotus ocellatus. Am. J. Physiol. 292,R2048 -R2058.
Zall, D. M., Fisher, D. and Garner, M. D. (1956). Photometric determination of chlorides in water. Anal. Chem. 28,1665 -1678.
![]()
CiteULike
Complore
Connotea
Del.icio.us
Digg
Reddit
Technorati
Twitter What's this?
This article has been cited by other articles:
![]() |
C. M. Wood, F. I. Iftikar, G. R. Scott, G. De Boeck, K. A. Sloman, V. Matey, F. X. Valdez Domingos, R. M. Duarte, V. M. F. Almeida-Val, and A. L. Val Regulation of gill transcellular permeability and renal function during acute hypoxia in the Amazonian oscar (Astronotus ocellatus): new angles to the osmorespiratory compromise J. Exp. Biol., June 15, 2009; 212(12): 1949 - 1964. [Abstract] [Full Text] [PDF] |
||||
![]() |
M. Inokuchi, J. Hiroi, S. Watanabe, P.-P. Hwang, and T. Kaneko Morphological and functional classification of ion-absorbing mitochondria-rich cells in the gills of Mozambique tilapia J. Exp. Biol., April 1, 2009; 212(7): 1003 - 1010. [Abstract] [Full Text] [PDF] |
||||
| |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||