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Vol. 281, Issue 2, 992-997, 1997
Department of Molecular and Cellular Toxicology, Harvard School of Public Health, 665 Huntington Ave., Boston, Massachusetts
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Abstract |
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Aminoglycoside antibiotics are indispensable for treatment of serious bacterial infections, and despite careful attention to dosage regimens, nephrotoxicity and ototoxicity still cause concern. In the present study, we tested whether side effects of aminoglycoside therapy could be limited by expression of prokaryotic genes of antibiotic resistance in vivo. We characterized the acute and tissue-specific toxicity of hygromycin B in transgenic mice bearing the hygromycin B phosphotransferase (hygR) gene under control of a constitutive promoter. We characterized the tissue-specific expression of hygR mRNA and also investigated the acute toxicity of hygromycin B in hygR and wild-type mice. The hygR mRNA reached its highest levels in brain and reached intermediate levels in spleen, muscle, kidney, liver and testis. The lowest levels were detected in heart and lungs. The hygR expression in transgenic animals caused an 89-fold increase in the approximate lethal dose of hygromycin B compared with wild-type mice. Serum biochemical analysis of hygR and wild-type mice treated with lethal doses of hygromycin B indicated liver and kidney damage measured as ALT, AST and BUN. On the morphological level, these changes led to acute tubular nephrosis in wild-type mice and acute liver damage in hygR mice. Our results show that constitutive expression of the bacterial hygR gene in transgenic mice in vivo confers resistance to hygromycin B.
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Introduction |
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Aminoglycoside antibiotics are
indispensable for treatment of serious bacterial infections, and
despite careful attention to dosage regimens, nephrotoxicity and
ototoxicity still cause concerns (Lortholary et al., 1995
).
In the present study, we tested whether side effects of aminoglycoside
therapy could be limited by expression of genes of antibiotic
resistance in vivo. As a model system, we used
aminoglycoside antibiotic hygromycin B and a transgenic mouse strain
bearing the antibiotic resistance gene hygR
under the control of the constitutive promoter Pgk1 (Johnson et al., 1995
).
Hygromycin B is an aminoglycoside antibiotic produced by
Streptomyces hygroscopicus (Pettinger et al.,
1953
) that is active against both prokaryotic and eukaryotic cells. It
has been shown that in eukaryotic cells, hygromycin B acts by
interfering with protein synthesis, especially by inhibition of
translocation, which is thought to be the result of its interaction
with the eukaryotic ribosome displacing EF-2 from the ribosome or
interfering with the activity of EF-2 and the stabilization of
peptidyl-t-RNA bound to the ribosomal acceptor site (Gonzalez et
al., 1978
). Toxic effects of hygromycin B in tissue culture can be
prevented by expression of hygR (Blochlinger and
Diggelmann, 1984
). This enzyme adds phosphate to position 7 of the
destomic acid ring of hygromycin B, which results in complete loss of
biological activity both in vitro and in vivo
(Pardo et al., 1985
). Therefore, hygR
has been widely used as a positive selective marker in the construction of transgenic animals via ESC. The transgenic construct
containing hygR is introduced into ESC. Then
clones of ESC bearing recombinant DNA with hygR
can be selected in medium containing hygromycin B. Although toxic effects of hygromycin B have been studied on the cellular level in
tissue culture (see, for instance, Chen et al., 1995
;
Gonzalez et al., 1978
; Pardo et al., 1985
), we
know of no previous reports on acute or tissue-specific hygromycin B
toxicity in transgenic mice bearing hygR. For
our experiments, we have used transgenic mice carrying
hygR driven by the constitutive Pgk1
promoter (Johnson et al., 1995
). These mice develop normally
and do not exhibit any apparent abnormal phenotype.
The aim of our study was to investigate the influence of constitutive expression of hygR on the toxic effects of hygromycin B in vivo. We have examined expression of hygR mRNA in different tissues, and we have determined the approximate lethal dose of hygromycin B for hygR and wild-type mice. Tissue-specific changes were then evaluated by histopathological examination and serum biochemical analysis. Our approach of using transgenic mice bearing hygR might contribute to better understanding of the mechanism of action and toxicity of aminoglycoside antibiotics.
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Materials and Methods |
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Animals and drug treatment.
Homozygous transgenic mice
C57BL/6J-TgN(pPWL512hyg)1Ems carrying hygR
(Johnson et al., 1995
) and wild-type C57BL/6J were obtained
from the Jackson Laboratory (Bar Harbor, ME). The animals were kept in
specific pathogen free conditions and were supplied with standard diet
and water ad libitum. The room was held at 22°C with
humidity 70% and a 12-hr dark-light cycle. Animal care and
experimental procedures were carried out in accordance with
institutional guidelines. Hygromycin B was purchased from Sigma
Chemical Corp (St. Louis, MO). The compound was dissolved in sterile
water before application, and the solution was injected i.p.
Acute toxicity, approximate lethal dose.
The approximate
lethal dose of hygromycin B after single i.p. injections was determined
according to Deichmann and LeBlanc (1943)
. This protocol significantly
reduces the number of experimental animals, limits unnecessary
suffering and complies with current guidelines on animal studies (IARC,
1993). Two sets of 6-month-old male mice (22-28 g) were used for all
acute toxicity experiments. The animals were treated with a single dose
of hygromycin B i.p. at doses that started at 2.7 mg/kg and increased
by 50% for each consecutive dose. Control mice were treated with the
same volume of sterile saline. Total volume injected was 0.5 ml. The
health status and body weights of animals were monitored daily for 10 consecutive days. The lowest dose in the dose response at which one
mouse died was considered the approximate lethal dose. Dead or
sacrificed moribund animals were necropsied, and the organs were stored
in 10% buffered neutral formalin until further analysis. The animals
were checked twice a day. The maximum theoretical time the animals
could be dead before necropsy was performed was 12 hr. Because animals
did not seem moribund when checked, we assume that the actual time was
much less.
Histopathological examination and serum biochemical
analysis.
The cadavers were necropsied, and the organs were stored
in 10% buffered neutral formalin. The organs were prepared as
paraffin-embedded glass slides stained with hematoxylin and eosin and
were evaluated in terms of the NTP (National Toxicology Program of
NIEHS) standards. When possible, a complete cross section of each organ
was evaluated (liver, spleen, gastrointestinal tract, femoral bone
marrow, mandibular and mesenteric lymph nodes, kidney, brain, testes,
lungs and heart). For liver, two cross sections, one of each of the two
largest liver lobes, were examined. For kidneys, an entire cross
section (left longitudinal, right transverse) was evaluated. Lungs had two cross sections (one of each of the two largest lobes). The entire
sections on the slides (all fields) were evaluated under blind
conditions for lesions and were scored (graded) on a subjective basis
compared with control animals. The grades were as follows: 1 = minimal, 2 = mild, 3 = moderate, 4 = marked and 0 = no pathological changes. The preparation and evaluation of slides used
the NTP criteria and terminology (Chhabra et al., 1990
).
Northern blot analysis.
Total RNA samples were isolated from
spleen, heart, thigh muscle, lung, kidney, liver, brain and testis by
guanidinium thiocyanate-phenol extraction (Chomczynski and Sacchi,
1987
), separated by electrophoresis in a formaldehyde/agarose gel and
transferred to a nylon HybondN+ membrane (Amersham, Arlington Heights,
IL) by capillary blotting. To compare loading of RNA samples we
photographed the ethidium bromide-stained gels. The blots were
hybridized to a hygR cDNA probe (Johnson
et al., 1995
) that was labeled with 32P dCTP
(DuPont NEN, Boston, MA) using random oligonucleotide primers (T7QuickPrime, Pharmacia, Piscataway, NJ). The
autoradiograms were exposed for 48 to 72 hr. The bands of
hygR mRNA on autoradiograms and the ethidium
bromide-stained 18S rRNA bands of corresponding samples were analyzed
by scanning densitometry with a BioImage (Millipore, Bedford, MA)
system. To compare expression of hygR mRNA, we
calculated the relative IOD as total IOD of the autoradiographed band
normalized to the intensity of the corresponding 18S ribosomal band
visualized by ethidium bromide.
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Results |
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Tissue-specific expression of hygR.
The steady-state levels of hygR mRNA in tissues
of transgenic mice were examined by Northern blot analysis. Total RNA
was isolated from spleen, heart, thigh muscle, lung, kidney, liver,
brain and testes of male hygR-bearing transgenic
and wild-type mice using guanidinium thiocyanate-phenol extraction. The
RNA samples were separated by electrophoresis in a formaldehyde/agarose
gel, transferred to a nylon membrane by capillary blotting and
hybridized with 32P-labeled hygR
cDNA probe. The autoradiograms were evaluated by densitometry, and the
results represent the average of three transgenic mice (fig.
1). The hygR mRNA reached
different levels in different tissues of the
hygR-bearing transgenic mice. No signal was
detectable in wild-type mice. The highest level of
hygR mRNA expression was detected in the brain.
Mid-level expression was detected in skeletal muscle, testis, kidney
spleen and liver, and somewhat lower levels were detected in heart and
lungs.
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Acute toxicity approximate lethal dose.
The approximate lethal
dose (Deichmann and LeBlanc, 1943
) of hygromycin B in transgenic
hygR-bearing as well as wild-type mice was
determined as a measure of the acute toxicity. The mice were treated
with single doses of hygromycin B i.p. (2 mice per dose) that increased
by 50% for each consecutive dose. The first dose in the increasing
sequence of doses at which the mice died was considered the approximate lethal dose. The health status of animals was monitored for consecutive 10 days. HygR transgenic and wild-type mice
tolerated a single i.p. injection of hygromycin B without immediate
toxic symptoms or distress. The approximate lethal dose of hygromycin B
for wild-type mice was 6 mg/kg (table 1). Expression of
hygR in transgenic mice caused a substantial
increase in resistance to hygromycin B. The approximate lethal dose for
hygR animals was 535 mg/kg, which represents an
89-fold increase over the wild-type strain. Lethal doses in both
hygR-expressing transgenic and wild-type strains
caused the same signs of decreased activity, which progressed to
lethargy and death. The body weight of animals after lethal doses
decreased, an effect that was less severe at shorter survival duration
after hygromycin treatment (table 1).
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Serum biochemical analysis. HygR mice were treated with the lethal dose of 803 mg/kg hygromycin B, and wild-type mice were treated with the lethal dose of 9 mg/kg hygromycin B. Control hygR mice were also treated with the nontoxic dose of 9 mg/kg. Serum samples taken 48 hr after treatment were evaluated for the levels of BUN, AST and ALT. Elevated BUN is associated with dehydration and/or renal insufficiency. Elevated activities of ALT and AST are characteristic of liver damage, particularly necrosis, cirrhosis and hepatitis. Increased AST levels are also characteristic for muscle trauma, myocardial infarction and myositis.
Administration of 9 mg/kg to wild-type mice resulted in clinically significant elevated levels of BUN, AST and ALT (table 2A), which suggests renal injury and hepatocellular damage. In contrast, the same dose given to hygR mice did not cause any change in those levels (table 2B). However, administration of 803 mg/kg of hygromycin B, a lethal dose to hygR animals, resulted in elevated levels of BUN, AST and ALT, just as the lethal dose of 9 mg/kg did in wild-type mice.
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Histopathological examination. Morphological manifestations of hygromycin B tissue-specific toxicity in animals treated with lethal doses was assessed by microscopic analysis. Lethal doses of hygromycin B (9 mg/kg) in wild-type animals caused nephrotoxicity (table 3). These mice had tubule eosinophilia, degeneration and necrosis characterized by cytoplasmic eosinophilia associated with necrosis, loss of tubule cellular and nuclear detail or degeneration and pyknotic nuclei and fragmentation of cells (fig. 2). These lesions are typical of acute tubular nephrosis. Remaining tissues (liver, spleen, GI tract, femoral bone marrow, mandibular and mesenteric lymph nodes, brain, testes, lungs and heart) were within normal limits (only kidney data are shown for comparison in fig. 2). The hygR mice treated with lethal doses of hygromycin B (803 mg/kg) had liver damage characterized as hepatocellular fatty change, acute inflammation and hepatocellular necrosis (table 3; fig. 3). Liver lesions in the hygR transgenic mice were typified by hepatocellular necrosis with nuclear pyknosis and loss of cellular detail, acute infiltration with small foci of neutrophils and fatty change with hepatocellular intracytoplasmic large, distinct, clear vacuoles that displaced nuclei. These liver lesions are characteristic of acute liver damage. The remaining tissues (spleen, GI tract, femoral bone marrow, mandibular and mesenteric lymph nodes, kidney, brain, testes, lungs and heart) were within normal limits (only liver data are shown for comparison in fig. 3).
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Discussion |
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In the present study, we characterized the acute and tissue-specific toxicity of hygromycin B in transgenic mice bearing the hygR gene under control of a constitutive promoter. We characterized the tissue-specific expression of hygR mRNA, and we investigated the acute toxicity of hygromycin B in hygR and wild-type mice. The hygR expression in transgenic animals caused an 89-fold increase in the approximate lethal dose of hygromycin B compared with wild-type mice. Serum biochemical analysis of hygR and wild-type mice treated with lethal doses of hygromycin B indicated liver and kidney damage as measured in terms of ALT, AST and BUN. On the morphological level, these changes were manifested as acute tubular nephrosis in wild-type mice and acute liver damage in hygR mice. Our results show that the constitutive expression of the bacterial hygR gene in transgenic mice in vivo confers resistance to hygromycin B.
To evaluate hygR expression in vivo,
we measured steady-state levels of hygR mRNA in
different mouse tissues by Northern blot analysis. Although hygR mRNA was detected in all tissues we
examined, the levels of expression varied. The highest level was
detected in brain, and mid-levels were measured in skeletal muscle,
testis, kidney, spleen and liver. Lower levels were measured in heart
and lungs. It has been reported that Pgk1-driven
transcription of lacZ in transgenic mice is not uniform
among the tissues and that the highest levels were reached in testes
and brain, that were measured mid-levels in kidney and heart followed
by liver and skeletal muscle and that the lowest levels were detected
in spleen (McBurney et al., 1994
). The slightly different
pattern of transgene expression in our study may be caused by the
length of the Pgk1 promoter sequence used for
hygR regulation, by the lack of introns and/or
by differences between integration sites in the genome. In case of the
hygR mouse, the Pgk1 promoter
fragment contained a promoter-specific enhancer placed directly
upstream of the hygR gene (Johnson et
al., 1995
). In contrast, the lacZ construct contained
the first three exons and two introns in addition to the
Pgk1 promoter-specific enhancer (McBurney et al.,
1994
), which may have influenced expression of the transgene (Palmiter
et al., 1991
).
As a quantitative parameter of hygromycin B toxicity, we determined the
approximate lethal dose that corresponds to the
LD50 ± 30% for most chemicals (Deichmann and
LeBlanc, 1943
). This protocol minimizes the number of animals
needed for the assessment of acute toxicity without unduly compromising
the accuracy (Ecobichon, 1992
). The approximate lethal dose in
wild-type mice for hygromycin B after i.p. application in our
experiments was 6 mg/kg. This value is identical to the
LD50 estimate after i.v. application using conventional
methods (Berdy, 1980), which indicates that the approximate lethal dose
is an appropriate parameter for evaluating the acute toxicity of
hygromycin B in vivo. Transgenic hygR
positive mice showed a dramatic 89-fold increase in the approximate lethal dose over the wild-type strain. This suggests that the level of
HygR enzyme present in the cells of the transgenic mice
effectively decreased hygromycin B toxicity in vivo.
To characterize the organ targets of hygromycin B toxicity in wild-type
and hygR transgenic mouse, we performed
biochemical analysis and histopathological evaluation of mice treated
with lethal doses of hygromycin B. The kidney damage was characterized
as an alteration in BUN levels, and liver damage was evaluated as a
change of ALT and AST activities. Serum biochemical analysis of both
wild-type and hygR mice treated with lethal
doses of hygromycin B (9 mg/kg and 803 mg/kg, respectively) revealed
renal injury characterized as increased levels of BUN and liver damage
characterized as an increase in ALT and AST enzymatic activities.
Morphological correlates to the serum biochemical results were
characterized using histopathological analysis. The wild-type mice
treated with lethal doses of hygromycin B showed histological signs of
nephrotoxicity identified as tubule eosinophilia, degeneration and
necrosis. In contrast, the transgenic hygR
transgenic mice treated with toxic doses of hygromycin B showed histopathological signs of liver damage characterized as hepatocellular fatty changes, acute inflammation and hepatocellular necrosis. Although
the serum biochemical analysis and histopathological findings in
wild-type and hygR mice differ, the liver and
kidney seem to be the targets of hygromycin B toxicity in both mouse
strains. The weak correlation between biochemical markers and
histopathological findings has been reported in other instances, so
organ-specific damage must be characterized by using more than one
parameter (Baum et al., 1975
; Herrera, 1993
). It seems that
in hygR mice, the lethal doses of hygromycin B
overloaded the metabolic capacities of HygR enzyme to
inactivate the drug. The absence of hepatic or renal histopathological
manifestation of hygromycin B toxicity in wild-type animals or
hygR mice, respectively, may be explained by
different availability of active hygromycin B molecules in liver and
kidney.
Pathological manifestations of renal toxicity associated with
aminoglycoside therapy consist largely of acute tubular lesions and
necrosis resulting in kidney failure (Laurent et al., 1990
; Tulkens, 1989
). This pathological pattern of tissue injury correlates with the pharmacokinetics and disposition of aminoglycosides. After
application, the aminoglycosides are excreted unchanged through the
kidneys (Sande and Mandell, 1985
), where a portion of the dose is
reabsorbed and cumulated in the tubular cells of the renal cortex
(Giuliano et al., 1986
; Kuhar et al., 1979
). The
association of aminoglycosides with negatively charged phospholipids and their accumulation in the lysosomes of tubular cells leads to
phospholipidosis by inhibition of lysosomal phospholipases (Laurent
et al., 1982
), which may trigger necrosis (Laurent et al., 1990
). On the other hand, it has also been shown on the
cellular level that hygromycin B interferes with protein synthesis,
especially by inhibition of translocation (Gonzalez et al.,
1978
). Our results indicate that compared with aminoglycosides used in
therapy, hygromycin B caused not only clinically similar kidney damage
but also liver toxicity. The exact molecular mechanism of hygromycin B
toxicity and the degree of its possible interaction with phospholipids and/or protein synthesis in vivo remain to be elucidated.
Aminoglycoside antibiotics are indispensable for treatment of serious
infectious diseases. Despite careful attention to dosage regimens
designed to achieve targeted levels in the serum, their toxicity still
causes concern (Lortholary et al., 1995
). Although hygromycin B is not used for treatment of human patients, our results
clearly show that its toxicity can be prevented by expression of
hygR in vivo. The general approach of using
transgenic animals with specific changes in drug metabolism pathways
can contribute to our understanding of the mode of action and toxicity
of drugs. This could ultimately lead to improvement of drug design and
treatment regimens.
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Acknowledgments |
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We thank the members of the Schiestl laboratory for discussions and comments on the manuscript. We thank Kristie Wetzel for providing histology support services and Charles P. Lerner for breeding mice.
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Footnotes |
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Accepted for publication January 22, 1997.
Received for publication August 12, 1996.
1 This work was supported by grant No. 1RO1ES07694 from the National Institutes of Health to R.H.S., grant No. MCB-9513537 from the National Science Foundation to E.M.S. and NIH Cancer Core Grant CA34196 at Jackson Laboratory.
2 Department of Veterinary Pathology, School of Veterinary Medicine, Louisiana State University, Baton Rouge, LA 70803.
3 The Jackson Laboratory, 600 Main Street, Bar Harbor, ME 04609.
Send reprint requests to: Robert H. Schiestl, Department of Molecular and Cellular Toxicology, Harvard School of Public Health, 665 Huntington Ave, Boston, MA 02115.
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Abbreviations |
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ALT, alanine aminotransferase; AST, aspartate aminotransferase; BUN, blood urea nitrogen; ESC, embryonic stem cells; hygR, hygromycin B phosphotransferase; IOD, integrated optical density; LD50, median lethal dose.
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References |
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