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Bacteriophage l and Plasmid pUR288 Transgenic FishModels for Detecting In Vivo Mutations
Richard N. Winn,* Michelle Norris, Stacy Muller, Cecilia Torres, and Kathryn Brayer
Aquatic Biotechnology and Environmental Laboratory, Warnell School of Forest Resources, University of Georgia,
Athens, GA 30602, USA
Abstract: We adapted transgenic rodent mutation assays based on fish carrying bacteriophage l and plasmid
pUR288 vectors to address the needs for improved methods to assess health risks from exposure to environ-
mental mutagens and also to establish new animal models to study in vivo mutagenesis. The approach entails
separating the vectors from fish genomic DNA and then shuttling them into specialized strains of E. coli bacteria
to analyze spontaneous and induced mutations in either lacI and cII or lacZ mutational targets. Fish exhibited
low frequencies of spontaneous mutants comparable to the sensitivity of transgenic rodent models. Mutations
detected after treating fish with chemical mutagens showed concentration-dependent, tissue-specific, and
time-dependent relationships. Spontaneous and induced mutational spectra also were consistent with the
specificity of known mutagens, further supporting the utility of transgenic fish for studies of in vivo muta-
genesis.
Key words: transgenic, medaka, Fundulus, mutation, lambda, plasmid.
INTRODUCTION
Detection and analysis of mutations in vivo is the basis for
understanding their ultimate sources and roles after expo-
sure of animals to mutagenic agents in the environment.
Despite the importance of detecting mutations in whole
animals, routine mutation analyses have been hampered by
a lack of methods to efficiently recover and accurately iden-
tify mutant genes. Transgenic rodent models that carry spe-
cific genes for quantitating spontaneous and induced mu-
tations were developed to improve in vivo mutation analy-
ses (Mirsalis et al., 1995). In this approach, a transgenic
animal carries a prokaryotic vector harboring a gene that
serves as a mutational target. After exposure to mutagens,
the vector is separated from the animal’s genomic DNA and
shuttled into indicator bacteria where mutant and nonmu-
tant genes are readily identified (Gossen et al., 1993; Sum-
mer et al., 1989).
Mutation assays in transgenic animals provide numer-
ous benefits for in vivo mutation analyses not available
using other approaches. By combining the simplicity of an
in vitro approach in a whole animal, mutations are quan-
tified directly at the level of single genes, the ultimate end
point of DNA damage and repair. Transgenic mutational
target genes are genetically neutral, affording a distinct ad-
vantage over assays involving endogenous genes that are
limited to very specific tissues or developmental stages. As a
consequence, mutations persist and accumulate without
being subjected to selection in the animal, thereby permit-
ting examination of mutations in virtually any tissue or
developmental stage (Cosentino and Heddle, 1996; Swiger
Received January 31, 2001; accepted March 30, 2001
*Corresponding author: telephone 706-542-6227; fax 706-542-4942; e-mail
Mar. Biotechnol. 3, S185–S195, 2001DOI: 10.1007/s10126-001-0041-2
© 2001 Springer-Verlag New York Inc.
et al., 1999; Tao et al., 1993). Mutations among different cell
types can be compared to determine how such factors as cell
proliferation, metabolism, toxicity, and DNA repair influ-
ence mutagenesis. Large numbers of copies of the locus can
be rapidly screened to provide statistically meaningful re-
sults while also reducing the need for large numbers of
animals. Mutation analyses can be combined also with
analyses of neoplasia or enzyme induction, DNA sequenc-
ing, or other end points within the same animal to disclose
possible mechanisms of mutagen action.
Taking advantage of the adaptability of transgenic mu-
tation assays to different species, transgenic fish were de-
veloped to address the need to improve methods to assess
environmentally induced mutations and also the need for
new and better animal models to study in vivo mutagenesis
(Amanuma et al., 2000; Winn et al., 1995, 2000). Mutation
assays originally developed in rodents were readily adapted
to fish and may increase the efficiency of transgenic assays.
As fish become recognized as valuable animal models, the
generation of transgenic fish will enhance the overall value
of fish in research. In some applications, such as in assessing
health hazards associated with exposure to complex chemi-
cal mixtures or in low-dose chronic exposures, fish offer
distinct advantages over other animal models in providing
insights into the mechanisms of disease processes (Hawkins
et al., 1995).
We review the development and application of trans-
genic fish for mutation analyses to demonstrate that they
meet the fundamental practical requirements for study of
in vivo mutagenesis. Our focus is on the recently intro-
duced transgenic medaka (Oryzias latipes) that carry the
bacteriophage l vector harboring cII and lacI genes as
mutational targets (Winn et al., 2000). Our initial results
also are discussed on a new mutation assay based on the
plasmid pUR288 vector that carries the lacZ gene as a mu-
tational target in transgenic medaka and mummichog
(Fundulus heteroclitus). The findings illustrate that many
features of the fish models are shared among the transgenic
mutation models, including those based on transgenic ro-
dents carrying identical mutational target genes, further
supporting the continued use of fish in studies of in vivo
mutagenesis.
BACTERIOPHAGE l TRANSGENIC MEDAKA
Choice of Species
The medaka was selected for development as a transgenic
mutation model because it is widely used in environmental
toxicology and is the fish species of choice in carcinogenesis
bioassays (Bunton, 1999) and in studies of germ-cell mu-
tagenesis (Shima and Shimada, 1994). In addition, the
medaka’s small size, short generation time, cost-effective
husbandry, well-characterized histopathology, and amena-
bility to transgenic development are ideal for this applica-
tion. The transgenic medaka promises to enhance the ac-
knowledged utility of this species as a comparative animal
model.
l CII AND LACI MUTATION ASSAYS
Bacteriophage l-based mutation systems have numerous
beneficial features for developing a transgenic fish model
with broad applicability. The l-transgenic rodent mutation
assay is used widely, has an extensive database on a variety
of test compounds and test conditions, and has well-
described standardized procedures to enhance its compara-
bility. Bacteriophage lLIZ (∼45 kb) contains two muta-
tional target genes, lacI and cII, flanked at each end by cos
sites that allow excision and packaging of the l phage to
recover the vector from the animal’s genomic DNA. Muta-
tions in the cII and lacI target genes are analyzed by using
different assays described as follows (Figure 1).
lacI Mutation Assay
The most extensively used transgenic rodent in vivo
mutation assay is based on the lacI gene (1089 bp) con-
tained within the lLIZ bacteriophage vector (Kohler et al.,
1991a). Mutations are analyzed by using in vitro packaging
procedures to excise and package the l vector as viable
bacteriophage. The individually packaged phage infect and
lyse the Escherichia coli host whereby mutation-induced in-
activation of the lacI gene is detected by scoring the mutant
plaques by blue-white screening on a Dlac E. coli lawn on
agar plates containing 5-bromo-4-chloro-3-indolyl b-D-
galactoside (X-gal). The assay’s mutation spectrum has been
well characterized (De Boer et al., 1998), as well as its quan-
titative and statistical aspects (Piergorsch et al., 1995). Da-
tabases containing thousands of lacI mutations also have
been established (Cariello et al., 1997; De Boer, 1995). The
system detects most classes of mutations, including base
substitutions, single-base frameshifts, insertions, duplica-
tions, and deletions (Mirsalis, 1993; Provost et al., 1993).
cII Mutation Assay
A positive-selection assay, originally developed for l
transgenic rodents that uses the cII gene as a mutational
S186 Richard N. Winn et al.
target, was introduced as a logistically simple, cost-effective
alternative to the lacI mutation assay (Jakubczak et al.,
1996). The cII mutation assay was the focus of l transgenic
medaka studies because it has numerous characteristics that
increase the efficiency of developing and testing the fish
mutation model (Winn et al., 2000). The assay is based on
the role the cII protein plays in the commitment of bacte-
riophage l to the lysogenic cycle in E. coli host cells. A
specialized E. coli strain (hfl−) extends the longevity of the
cII product, facilitating selection of mutant cII l. The l
phage with wild-type cII produce lysogens that are indis-
tinguishable in the E. coli lawn, whereas l phage that carry
a mutation in cII are selected as they form plaques on the
bacterial lawn when incubated at 24°C. The smaller size of
cII target (296 basepairs vs. 1080 bp for lacI) also facilitates
efficient characterization of specific mutations because the
entire gene can be directly sequenced. Despite the more
limited analysis of the cII locus compared to lacI, results
from rodent and fish studies support its continued use as an
acceptable alternative target to lacI (Harbach et al., 1998;
Watson et al., 1998; Winn et al., 2000; Zimmer et al., 1998).
Production of l Transgenic Medaka
Transgenic medaka were produced using lLIZ vector DNA
ligated at cohesive termini (cos ligation) to form linear con-
catamers before microinjection into one-cell-stage medaka
zygotes (Winn et al., 2000). The cos ligation of the l vector
apparently improves the number of rescued phage per ge-
nome by protecting the integrity of most intervening cohe-
sive termini that are important in phage assembly (Dycaico
et al., 1994). Nine germ-line transmitting medaka founders
were identified. Mosaic integration of the transgene in the
germ-line of the founders was indicated by the variable
frequencies of transmission observed among offspring.
Mendelian inheritance of the transgene in the offspring ob-
tained from sibling crosses (>5 generations) supported the
conclusion that the l vector is integrated in a single chro-
mosomal site in each transgenic lineage.
Recovery of l Vector from Fish Genomic DNA
The l-based mutation assays rely on in vitro packaging
extracts to excise the intact l vector from the transgenic
Figure 1. Bacteriophage l-based transgenic medaka mutation as-
says using lacI (1089 bp) or cII (297 bp) mutational targets. After
isolating genomic DNA, the l vector (∼45 kb) is excised and
packaged similarly for each using in vitro packaging procedures.
Individually packaged phage infect and lyse the E. coli host
whereby mutation-induced inactivation of the lacI gene is detected
by scoring mutant plaques by blue-white screening on a Dlac E.
coli lawn on agar plates containing X-gal. In the cII assay, packaged
phage infect a hfl− E. coli host which extends the longevity of the
cII product to facilitate selection of mutant cII. Phage containing
wild-type cII produce lysogens and are indistinguishable in the E.
coli lawn, whereas l phage with a mutation in cII are selected by
forming plaques when incubated at 24°C.
Transgenic Fish Models for Detecting Mutations S187
animal’s genomic DNA and package it into viable phage
particles for subsequent infection of E. coli host cells. The
efficiency with which the vector can be recovered was
shown to be a practical requirement for transgenic rodent
mutation assays (Dycaico et al., 1994). Using standard in
vitro packaging methods and cII mutation assay procedures,
efficiencies in recovering l vector from fish genomic DNA
were variable, with the numbers of plaque forming units
(PFU) recovered associated with the number of l copies
carried among the medaka lineages (Winn et al., 2000).
Lineage l310, shown to carry ∼74 l copies/haploid genome,
exhibited unprecedented vector recovery with an average of
∼60,000–70,000 PFU/µg DNA from various tissues. The
highly efficient recovery of the vector from this lineage in-
dicated that it would satisfy practical assay requirements
and would permit analysis of mutations in individual fish,
precluding the pooling of multiple samples. Previous stud-
ies of transgenic rodents (Dycaico et al., 1994) and fish
(Winn et al., 1995) demonstrated a similarly enhanced re-
covery of the vector from animals carrying multiple copies
of bacteriophage vectors.
Spontaneous cII Mutant Frequencies
Determining the frequency of spontaneous mutations at the
cII locus was essential in establishing the utility of the fish
model for detecting induced mutations. The sensitivity of
mutation assays is defined by the magnitude of induced
mutational response compared to the frequency of sponta-
neous mutation (Heddle et al., 2000). Mutation analyses
were performed using offspring from transgenic parents
that were homozygous for the l transgene. Ranges of spon-
taneous mutant frequencies observed in individual trans-
genic fish were slightly lower than, but comparable to,
ranges of cII mutant frequencies in l transgenic rodents,
indicating that fish have at least equivalent, if not a some-
what greater sensitivity of the two in detecting induced
mutations. Frequencies of cII mutants in medaka lineage
l310 varied significantly among tissues with the lowest fre-
quency in testes, followed by whole fish and liver (Winn et
al., 2000) (Table 1). Subsequently, spontaneous mutant fre-
quencies were obtained for eyes, whole blood, and skin
(Table 1). A benefit afforded by the efficient recovery of the
vector and low variability in spontaneous mutant frequen-
cies in fish is that few animals (6–7 fish/treatment) are
required to detect a significant induction of mutations over
background. Analysis of spontaneous mutant frequencies in
l310 fish indicate that no de novo mutations have accu-
mulated in the germ-line of this lineage in over five gen-
erations.
Response of cII to Chemical Mutagens
Responsiveness of the cII target gene to mutagen treatment
was examined after exposing fish to ethyl-N-nitrosourea
(ENU) and dimethylnitrosoamine (DMN). ENU is a well-
characterized mutagen that directly ethylates oxygen and
nitrogen in the bases of DNA (Singer, 1976; Singer et al.,
1978). ENU is widely used as a mutagen in saturation mu-
tagenesis screens (Mullins et al., 1994; Solnica-Kretzel et al.,
1994) and as a standard control mutagen in transgenic ro-
dent assays (Mirsalis et al., 1994). The cII target was highly
responsive to ENU treatment, reflecting the induction of
mutations consistent with the mutagen’s concentration, tis-
sue-specificity, manifestation time, and known modes of
ENU action (Winn et al., 2000). cII mutant frequencies in
whole fish were induced 2.7-fold and 4-fold over untreated
fish sampled 15 days after 1 hour of treatment at 60 and 120
mg/liter ENU, respectively. Frequencies of cII mutants in
fish sampled at 5, 15, 20, and 30 days after ENU treatment
illustrated the tissue-specific influence of sampling time on
mutagenesis. Mutant frequencies in livers of fish treated
with ENU did not increase significantly above those of un-
treated fish sampled five days after treatment but increased
significantly by 3.5-fold at 15 days and continued to in-
crease to nearly 7-fold above background at 30 days. In
contrast, mutant frequencies in the testes were induced 5.2-
fold over the mean background mutant frequency at 5 days
and reached a peak of 10-fold induction at 15 days, followed
by a nonsignificant decline to 8.8-fold above background at
20 and 30 days after ENU treatment.
Table 1. Recovery and Spontaneous cII Mutant Frequencies in
Tissue from Transgenic Medaka Lineage l310
Tissue
Total
fish
Total
mutants
Mean
PFU
Mean mutants
×10−5 PFU
(± SEM)
Whole fish 12 599 1,468,917 3.9 (0.4)
Testes 26 537 1,123,455 1.9 (0.2)
Liver 29 1352 1,342,701 3.1 (0.2)
Eyes 10 207 426,500 2.8 (0.1)
Skin 4 95 1,666,250 1.5 (0.3)
Blood 3 70 1,018,333 2.4 (0.4)
S188 Richard N. Winn et al.
We examined induction of mutations in cII further by
using dimethylnitrosoamine (DMN), a potent liver carcino-
gen used extensively as a model mutagen in assays with
transgenic rodents. DMN is among a class of nitrosamines
that induce hepatocarcinogenesis in fish with progressive
stages similar to those characterized in rodent hepatic neo-
plasia (Hawkins et al., 1995). We observed significant in-
ductions of cII mutants in liver 15 days after treatment with
DMN at 0, 300, and 600 mg/liter administered over 96
hours in a static renewal exposure regimen (Figure 2). Mu-
tants were induced 7.1-fold (16.7 ± 2.8 × 10−5), and 16.4-
fold (38.4 ± 6.6 × 10−5) above controls (2.1 ± 0.25 × 10−5)
at 300 and 600 mg/liter, respectively.
The different frequencies of induced mutations ob-
served in various fish tissues at equivalent mutagen treat-
ments illustrate a valuable attribute of the transgenic fish
mutation assay. The interval between mutagen treatment
and analyses, termed mutation manifestation time, is af-
fected by several variables, including tissue/cell type, muta-
gen, and mutagen-treatment regimen, that must be consid-
ered in designing and interpreting mutation studies (Hara
et al., 1999; Sun et al., 1999; Walker et al., 1999). For ex-
ample, the relatively higher magnitude of mutation induc-
tion and their shorter manifestation time in testes com-
pared to liver suggests that these differences reflect differ-
ences in cell proliferation rates and ENU action among
these tissues. These results also indicated that a 15-day sam-
pling time may be sufficient to detect a significant 2-fold
induction in most fish tissues, although an expression time
>30 days may be required for weak mutagens; a 5-day ex-
pression time is probably suitable only for the most potent
mutagens. Because cell proliferation is a prerequisite for
DMN-produced methyl DNA adducts to become fixed as
mutations (Mirsalis, 1993), results from the DMN exposure
study illustrate further the importance of considering cell
proliferation in designing exposure regimens. A distinct
value of using transgenes that are genetically neutral is that
mutations persist and accumulate without being subjected
to selection in the animal. Repeated exposures may, there-
fore, more closely mimic realistic environmental exposures
if chemicals are administered during periods of cell prolif-
eration induced by a previous exposure. As a consequence,
accumulation of mutations in transgene targets indicates
that repeated or chronic mutagen treatments should in-
crease the sensitivity of the assay (Heddle et al., 2000). The
amenability of fish to a wide range of exposure regimens
suggests that transgenic fish are ideally suited for such
evaluations.
Spontaneous and Chemically InducedMutational Spectra
An important benefit of transgenic mutation systems is the
ability to analyze mutations at the level of the DNA se-
quence. Sequencing the target gene recovered from the ani-
mal can provide important information on the spectra of
mutations induced by specific compounds and indicate
possible mechanisms of mutagen action. Sequencing the
target gene also may prove to be particularly useful in ex-
amining whether small increases in mutant frequencies after
exposure to chemicals at low environmental concentrations
are accompanied by shifts in mutational spectra. After veri-
fying the phenotype of cII mutant phage using selective
plating conditions, a 446-bp product that included the en-
tire 294 bp cII gene was sequenced. Spontaneous and
chemically induced cII mutational spectra in fish appear to
be similar to spectra in transgenic rodents. Single-base sub-
stitutions comprised the majority of spontaneous and ENU-
(Winn et al., 2000) and DMN-induced mutations in fish,
with a large percentage of the G:C → A:T mutations at CpG
sites (Table 2). The different modes of action of ENU and
DMN are reflected in the mutational spectra. The propor-
tions of mutations at A:T basepairs were higher in ENU-
treated livers compared to untreated livers, with the bulk of
the increase being A:T → T:A transversions, consistent with
the greater mutagenic effect of ENU at A:T basepairs (Shane
et al., 1997; Walter et al., 1998). ENU produces O6-
ethylguanine, O4-ethylthymidine, and O2-ethylthymidine in
DNA, promoting G:C → A:T and A:T → G:C transitions
and A:T → T:A transversions (Shelby and Tindall, 1997;
Shibuya and Morimoto, 1993), respectively. The majority of
Figure 2. cII mutant frequencies (± SEM) in livers from medaka
15 days following exposure to 0, 300, or 600 mg/liter DMN in a
static renewal regimen. Mutant frequencies were significantly el-
evated over the mean background (2.1 ± 0.25 × 10−5) at 300 (16.7
± 2.8 × 10−5) and 600 (38.4 ± 6.6 × 10−5) mg/liter DMN.
Transgenic Fish Models for Detecting Mutations S189
frameshifts observed in the spontaneous mutation spectrum
in the fish were either insertions or deletions within a
known cII hotspot (Watson et al., 1998). Their percentage
decreased in the ENU-exposed fish consistent with studies
showing ENU does not induce high numbers of frameshift
mutations (Shelby and Tindall, 1997). Single-base substitu-
tions were the most frequent mutations in the liver of
DMN-treated fish, with G:C → A:T transitions being more
numerous than transversions which is characteristic of
DMN exposure and attributable to the mispairing of O6-
methylguanine with thymine, eventually leading to G:C →A:T transitions during replication (Wang et al., 1998).
Spontaneous and ENU-Induced Mutations in lacI
A significant advantage of the l-based transgenic medaka is
afforded by the ability to analyze mutations in the lacI target
gene also contained in the lLIZ vector. Despite limited
studies of the lacI target in the l transgenic medaka, recent
work demonstrated the feasibility of analyzing spontaneous
and ENU-induced mutations in the lacI locus recovered
from these fish (Shih et al., 2001). Comparable numbers of
l-lacI phage were recovered from untreated and ENU-
treated fish, with PFU numbers approaching those typically
obtained from transgenic rodents. Frequencies of sponta-
neous lacI mutants in whole fish also were comparable to
ranges in most rodent tissues (Dycaico et al., 1994; Kohler
et al., 1991b) and somewhat lower than cII mutant frequen-
cies in fish (Winn et al., 2000). The frequencies of lacI
mutants were increased 7-fold after a 1-hour exposure to
120 ppm ENU over untreated fish, compared with a 4-fold
induction in cII with identical ENU treatment. Sequencing
of the lacI mutants disclosed spontaneous and ENU-
induced mutational spectra similar to those in rodent mod-
els.
PLASMID PUR288 TRANSGENIC MEDAKAAND MUMMICHOG
Choice of Species
The mummichog also was selected for this application be-
cause this species has many attributes that are well-suited
for transgenic development and environmental toxicology.
The mummichog has well-described embryology, a small
adult size, controllable year-round spawning, a transparent
chorion, short embryogenesis and generation time, and a
proven amenability to transgenic production (Winn et al.,
1995). In addition, as a common inhabitant of coastal and
estuarine environments, the mummichog is one of the most
extensively used organisms in studies of the risks of envi-
ronmental contaminants (Atz, 1986; Eisler, 1986) and in
ecotoxicological studies (Lotrich, 1975; Vogelbein, 1990).
lacZ Mutation Assay
A transgenic mouse model based on a plasmid pUR288
vector containing the lacZ gene as the mutation target was
introduced as an alternative to the bacteriophage l-based
mutation assays (Boerrigter et al., 1995) and was adapted to
the two species of fish discussed here (Figure 3). In this
approach, the pUR288 vector, flanked by HindIII restriction
sites and containing the entire lacZ sequence as the muta-
tional target (3096 bp), is recovered from the transgenic
animal’s genomic DNA by binding the lac repressor protein
to the operator sequence located in front of the lacZ gene.
After exposure to a mutagen, the transgenic animal’s geno-
mic DNA is digested with HindIII to release monomeric
plasmid sequences. The plasmid then is separated from the
genomic DNA by affinity capture using magnetic beads to
recover the lacZ plasmid sequences. After being circularized
Table 2. Mutational Spectra for Spontaneous cII Mutants (Liver,
Testes, and Whole Fish Combined) and DMN-Exposed Livers
Spontaneous
300
mg/liter
600
mg/liter
Total mutations 89 42 44
Mutations outside cII 5 0 6
Independent mutations 74 37 34
Transitions % (N) % (N) % (N)
G:C → A:T 20 (15) 67 (25) 73 (25)
A:T → G:C 12 (9) 5 (2) 3 (1)
Transversions
G:C → T:A 20 (15) 11 (4) 0
G:C → C:G 11 (8) 0 6 (2)
A:T → T:A 4 (3) 3 (1) 3 (1)
A:T → C:G 7 (5) 3 (1) 0
CpG 47 (7) 20 (5) 12 (3)
Frameshift
(+) 13 (10) 0 3 (1)
(−) 11 (8) 11 (4) 9 (3)
Other 0 0 3 (1)
S190 Richard N. Winn et al.
by ligation, concentrated plasmids are transferred into
lacZ−, galE− E. coli by electroporation in the presence of
phenyl-b-D-galactoside (P-gal) (Gossen et al., 1992). Mu-
tant frequencies are determined as the ratio between the
numbers of colonies on selective (P-gal) LB agar plates ver-
sus the number of colonies on nonselective plates.
The plasmid pUR288 vector and associated lacZ rodent
mutation assay has several advantages over bacteriophage-
based rodent assays that may be useful in a transgenic fish
model. The pUR288 plasmid-based system is more efficient
than the bacteriophage system at rescuing lac genes from
transgenic mice (Gossen et al., 1993) due, in part, to the
high capacity of the lacI repressor magnetic bead to purify
the plasmid from the restriction-enzyme-digested genomic
DNA in a single step. In addition, in contrast to the llacI
mutation assay, mutations are detected by a selective pro-
cedure rather than by scoring colors, thereby reducing am-
biguity in analyses. Possibly more importantly, the plasmid-
based mutation assay appears to have a superior ability to
detect point mutations, small deletions and insertions, as
well as large-scale deletions and rearrangements induced by
clastogenic agents, such as radiation (Tao et al., 1993). Res-
cue of plasmids is not as size-dependent as are bacterio-
phage l vectors that require two intact cos sites for vector
packaging whereby deletions extending into regions adja-
cent to the l transgene may prevent recovery of the vector.
Production of Plasmid pUR288 Transgenic Fish
Plasmid pUR288 DNA (from Dr. Jan Vijg, University of
Texas Health Science Center, San Antonio, TX, USA) was
prepared as linear concatamers and microinjected into the
one-cell zygotes of medaka and mummichog using similar
procedures to those previously described (Winn et al., 1995,
2000). Fifteen medaka shown to be positive for the plasmid
sequence by PCR analyses (15/165 fish) were mated with
nontransgenic fish, and germ-line transmission was con-
firmed in six founders (6/15 fish). Mosaic integration of the
transgene into the germline was indicated by the variable
transmission frequency among the founders (4%–44%). In-
tegration of the plasmid in a single chromosomal site in the
transgenic lineages was confirmed from subsequent Men-
delian inheritance of the transgene beyond three genera-
tions. Nineteen mummichog were confirmed positive for
the plasmid sequence by PCR (19/304 fish), and Mendelian
inheritance of the plasmid was confirmed in two founders
(2/19 fish).
Figure 3. The plasmid pUR288 (∼5 kb)
is flanked by HindIII restriction sites and
contains the entire lacZ gene (3089 bp) as
the mutational target that is recovered
from the transgenic animal’s genomic
DNA by binding the lac repressor protein
to the operator sequence in front of lacZ.
Genomic DNA is digested with the
restriction enzyme to release monomeric
plasmids, which are recovered using
affinity capture with magnetic beads.
Plasmids are circularized by ligation and
transferred into lacZ-, galE- E. coli by
electroporation in the presence of p-Gal.
Mutant frequencies are determined as the
ratio between the number of colonies on
selective (P-gal) plates versus the number
of colonies on non-selective plates.
Transgenic Fish Models for Detecting Mutations S191
pUR288 Recovery and lacZSpontaneous-Mutant Frequencies
By using the positive selection mutation assay (Boerrigter et
al., 1995; Boerrigter, 1998; Dolle et al., 1996), pUR288 plas-
mids were recovered from genomic DNA isolated from one
medaka and mummichog lineage (Table 3). Rescue of plas-
mids ranged from 910,000 to 3,400,000 CFU/sample in
medaka lineage pUR127, to 52,000 CFU/sample in the
mummichog lineage, indicating that the recovery of the
vector is sufficient to perform the mutation assay. Medaka
lineage 127 and mummichog lineage 99 showed spontane-
ous lacZ mutant frequencies within ranges comparable to
those of transgenic mice carrying the identical target (Boer-
rigter et al., 1995). Studies are underway to characterize the
remaining lineages and to test the relative responsiveness of
the lacZ target after exposing fish to chemical mutagens.
UTILITY OF TRANSGENIC FISHMUTATION MODELS
Transgenic rodent models developed for assessing sponta-
neous and induced mutations have demonstrated numer-
ous benefits for studies of in vivo mutagenesis over other
approaches (Mirsalis et al., 1995). Among their more dis-
tinctive advantages is their amenability to comparisons of
mutagenesis among different cells, tissues, and species. Al-
though transgenic fish mutation models were introduced
only recently, the results demonstrate that fish share many
features of mutation analyses in rodent models and support
their continued use in studies of in vivo mutations. Studies
on bacteriophage l fish mutation assays based on lacI, and
to a greater extent, on cII, establish a good basis for evalu-
ating the relative utility and efficacy of using transgenic fish
models for mutation analyses. The efficient vector recovery
and low variability among fish has facilitated analyses of
mutations in a variety of tissues using a relatively small
number of animals. Spontaneous mutant frequencies in the
two target genes are low, comparable to that in transgenic
rodents, indicating sufficient sensitivity for detecting in-
duced mutations. Treating fish with chemical mutagens re-
sulted in concentration-dependent inductions in each target
gene and in tissue-specific and time-dependent inductions
in the cII locus. Sequencing of the cII and lacI mutants
recovered from fish illustrate that the mutational spectral
shifts are consistent with known mechanisms of mutagen
action. Initial results on developing the pUR288 plasmid
medaka and mummichog demonstrate that these models
also have promise as alternative mutation models that may
be useful for detecting a broad spectrum of mutations com-
parable to the existing pUR288 plasmid mouse model.
Two additional transgenic fish mutation assays adapted
from rodent assays have been introduced. Transgenic mum-
michog were produced based on the bacteriophage
fX174am3cs70, in which mutations are detected by rever-
sion of am3 to wild-type phage by one transition and two
transversions of a single A:T basepair (Winn et al., 1995).
The spontaneous mutation frequency in these fish was com-
parable to that of transgenic mice (Burkhart et al., 1993). A
transgenic zebrafish (Danio rerio) was derived from a mouse
mutation assay (Gondo et al., 1996), based on the pML4
plasmid containing mutations in the rpsl gene as the mu-
tational target (Amanuma et al., 2000). Spontaneous and
chemically induced mutant frequencies were consistent
with studies in the transgenic mouse. Further testing of
these systems may provide valuable comparisons of muta-
tions detected in different transgene targets and species.
By extending transgenic mutation systems to another
species such as fish, various factors influencing mutagenesis
can be identified in identical DNA sequences in different
cells, tissues, and species in applications that could not be
attempted or performed otherwise. Transgenic fish muta-
tion assays also offer excellent opportunities to improve the
assessment of genetic risks associated with exposure to
chemicals in aquatic systems. By taking advantage of the
amendability of fish at all life stages to a variety of exposure
regimens ranging from microinjection of embryos (Walker
et al., 1996) to static renewal and flow-through chronic
exposures (Kane et al., 1996), transgenic fish can be used in
a wide range of applications to enhance the assessment of
risks from exposure to waterborne and sediment-associated
Table 3. Transmission Frequency, Recovery, and Spontaneous
Mutant Frequencies in pUR288 Transgenic Medaka and Mum-
michog Lineages
Lineage
Transmission
frequency
(%)
Total
(CFU)
Mutant
frequency
×10−5
CFU
Medaka
127 44 910,000– 3,400,000 6.6–9.4
Mummichog
99 37 52,000 5.6–12.0
S192 Richard N. Winn et al.
chemical contaminants. When used in combination with
measures of other toxicological end points in fish, mutation
analyses may prove useful to more fully characterize bio-
logical impacts of environmental hazards. Finally, the trans-
genic fish may make important contributions to emerging
issues related to environmentally induced developmental
and heritable diseases.
ACKNOWLEDGMENTS
This work was supported in part by grant R24RR11733
from the National Institutes of Health National Center for
Research Resources, grant RR251139 from the Georgia Ad-
vanced Technology Development Center, and grant
RR389930 from the Georgia Research Alliance.
REFERENCES
Amanuma, K., Takeda, H., Amanuma, H., and Aoki, Y. (2000).
Transgenic zebrafish for detecting mutations caused by com-
pounds in aquatic environments. Nat Biotechnol 18:62–65.
Atz, J.W. (1986). Fundulus heteroclitus in the laboratory: a history.
Am Zool 26:111–120.
Boerrigter, M., Dolle, M., Martus, H., Gossen, J.A., and Vijg, J.
(1995). Plasmid based transgenic mouse model for studying in
vivo mutations. Nature 377:657–659.
Boerrigter, M.E.T.I. (1998). High sensitivity for color mutants in
lacZ plasmid-based transgenic mice, as detected by positive selec-
tion. Environ Mol Mutagen 32:148–154.
Bunton, T.E. (1999). Use of non-mammalian species in bioassays
for carcinogenicity. In Data on Genetic Effects in Carcinogenic Haz-
ard Evaluation, McGregor, J.D.B., Rice, J.M., and Venitt, S. (eds.).
Lyon: IARC Scientific Publications, 151–184.
Burkhart, J.G., Burkhart, B.A., Sampson, K.S., and Malling, H.V.
(1993). ENU-induced mutagenesis at a single A:T base pair in
transgenic mice containing FX174. Mutat Res 292:69–81.
Cariello, N.F., Douglas, G.R., Dycaico, M.J., Gorelick, N.J., Pro-
vost, G.S., and Soussi, T. (1997). Databases and software for the
analysis of mutations in the human p53 gene, the human hprt gene
and both the lacI and the lacZ gene in transgenic rodents. Nucleic
Acids Res 25:136–137.
Cosentino, L., and Heddle, J.A. (1996). A test for neutrality of
mutations of the lacZ transgene. Environ Mol Mutagen 28:313–
316.
De Boer, J.G. (1995). Software package for the management of
sequencing projects using lacI transgenic animals. Environ Mol
Mutagen 25:256–262.
De Boer, J.G., Provost, S., Gorelick, N., Tindall, K., and Glickman,
B.W. (1998). Spontaneous mutation in lacI transgenic mice: a
comparison of tissues. Mutagenesis 13(2):109–114.
Dolle, M.E.T., Martus, H., Gossen, J.A., Boerrigter, M.E.T.I., and
Vigj, J. (1996). Evaluation of a plasmid-based transgenic mouse
model for detecting in vivo mutations. Mutagenesis 11(1):111–118.
Dycaico, M.J., Provost, G.S., Kretz, P.L., Ransom, S.L., Moores,
J.C., and Short, J.M. (1994). The use of shuttle vectors for muta-
tion analysis in transgenic mice and rats. Mutat Res 307:461–478.
Eisler, R. (1986). Use of Fundulus heteroclitus in pollution studies.
Am Zool 26:283–288.
Gondo, Y., Shioyama, Y., Nakao, K., and Katsuki, M. (1996). A
novel positive detection system of IN VIVO mutations in rpsL
(strA) transgenic mouse. Mutat. Res. 360:1–14.
Gossen, J.A., Molijn, A.C., Douglas, G.R., and Vigj, J. (1992).
Application of galactose-sensitive E. coli strains as selective hosts
for LacZ− plasmids. Nucleic Acids Res 20:12.
Gossen, J.A., De Leeuw, W.J., Molijin, A.C., and Vigj, J. (1993).
Plasmid rescue from transgenic mouse DNA using lacI repressor
protein conjugated to magnetic beads. Biotechniques 14:624–629.
Hara, T., Sui, H., Kawakami, K., Shimada, Y., and Shibuya, T.
(1999). Partial hepatectomy strongly increased in the mutagenicity
of N-ethyl-N-nitrosourea in Muta™Mouse liver. Environ Mol Mu-
tagen 34:121–123.
Harbach, P.R., Zimmer, D.M., Filipunas, A.L., Mattes, W.B., and
Aaron, C.S. (1998). Spontaneous and ENU-induced cII mutation
spectra in Big Bluet mice. Environ Mol Mutagen 31(suppl 29):14.
Hawkins, W.E., Walker, W.W., and Overstreet, R.M. (1995). Car-
cinogenicity tests using aquarium fish. In Fundamentals of Aquatic
Toxicology: Effects, Environmental Fate, and Risk Assessment, Rand,
G.M. (ed.). Taylor and Francis, Washington, D.C., 421–446.
Heddle, J.A., Dean, S., Nohmi, T., Boerrigter, M., Casciano, D.,
Douglas, G.R., Glickman, B.W., Gorelick, N.J., Mirsalis, J.C., Mar-
tus, H., Skopek, T.R., Thybuad, V., Tindall, K.R., and Yajima, N.
(2000). In vivo transgenic mutation assays. Environ Mol Mutagen
35:253–259.
Jakubczak, J.L., Merlina, G., French, J.E., Muller, W.J., Paul, B.,
Adhya, S., and Garges, S. (1996). Analysis of genetic instability
during mammary tumor progression using a novel selection-based
assay for in vivo mutations in a bacteriophage l transgene target.
Proc Natl Acad Sci USA 93:9073–9078.
Transgenic Fish Models for Detecting Mutations S193
Kane, A.S., Jacobson, S.V., and Reimschuessel, R. (1996). Con-
struction and use of a large-scale dosing system to expose fish to
waterborne contaminants. In Techniques in Aquatic Toxicology,
Ostander, G.K. (ed.). Boca Raton, FL: CRC Press, 589–607.
Kohler, S.W., Provost, G.S., Fieck, A., Kretz, P.L., Bullock, W.O.,
Sorge, J.A., Putman, D.L., and Short, J.M. (1991a). Spectra of
spontaneous and mutagen-induced mutations in the lacI gene in
transgenic mice. Proc Natl Acad Sci USA 88:7958–7962.
Kohler, S.W., Provost, G.S., Kretz, P.L., Fieck, A., Bullock, W.O.,
Sorge, J.A., Putman, D.L., and Short, J.M. (1991b). Analysis of
spontaneous and induced mutations in transgenic mice using a
lambda ZAPt/lacI shuttle vector. Environ Mol Mutagen 18:316–
321.
Lotrich, V.A. (1975). Summer home range and movements of
Fundulus heteroclitus (Pices: Cyprinodontidae) in a tidal creek.
Ecology 56:191–198.
Mirsalis, J. (1993). Dosing regimens for transgenic animal muta-
genesis assays. Environ Mol Mutagen 21:118–119.
Mirsalis, J.C., Monforte, J.A., and Winegar, R.A. (1994). Trans-
genic animal models of measuring mutations in vivo. Crit Rev
Toxicol 24(3):255–280.
Mirsalis, J.C., Monforte, J.A., and Winger, R.A. (1995). Transgenic
animal models for detection of in vivo mutations. Annu Rev Phar-
macol Toxicol 35:135–164.
Mullins, M., Hammerschmidt, M., Haffter, P., and Nusslein-
Volhard, C. (1994). Large-scale mutagenesis in the zebrafish: in
search of genes controlling development in a vertebrate. Curr Biol
4:189–202.
Piergorsch, W.W., Margolin, B.H., Shelby, N.M., Johnson, A.,
French, J.E., Tennant, R.W., and Tindall, K.R. (1995). Study de-
sign and sample sizes for lacI trangenic mouse mutation assay.
Environ Mol Mutagen 25:231–245.
Provost, G.S., Kretz, P.L., Hammer, R.T., Matthews, C.D., Rogers,
B.J., Lundberg, K.S., Dycaico, M.J., and Short, J.M. (1993). Trans-
genic systems for in vivo mutation analysis. Mutat Res 288:133–
149.
Shane, B.S., Lockhart, A.-M.C., Winston, G.W., and Tindall, K.R.
(1997). Mutant frequency of lacI in transgenic mice following
benzo[a]pyrene treatment and partial hepatectomy. Mutat Res
377:1–11.
Shelby, M.D., and Tindall, K.R. (1997). Mammalian germ cell
mutagenicity of ENU, IPMS, and MMS, chemicals selected for a
transgenic mouse collaboratory study. Mutat Res 388:99–109.
Shibuya, T., and Morimoto, K. (1993). A review of the genotox-
icity of 1-ethyl-1-nitrosourea. Mutat Res 297:3–38.
Shih, P.M.T., Winn, R.N., Norris, M., Brayer, K., and Shane, B.S.
(2001). Mutagenesis of ethylnitrosourea (ENU) at the lacI locus in
a transgenic fish (Oryzias latipes). Carcinogenesis (in press).
Shima, A., and Shimada, A. (1994). The japanese medaka, Oryzias
latipes, as a new model organism for studying environmental
germ-cell mutagenesis. Environ Health Perspect 102(suppl 12):33–
35.
Singer, B. (1976). All oxygens in nucleic acids react with carcino-
genic ethylating agents. Nature 264:333–339.
Singer, B., Bodell, W.J., Cleaver, J.E., Thomas, G.H., Rajewsky,
M.F., and Thon, W. (1978). Oxygens in DNA are the main targets
for ethylnitrosourea in normal xeroderma pigmentosum fibro-
blasts and fetal rat brain cells. Nature 276:85–88.
Solnica-Kretzel, L., Schier, A., and Driever, W. (1994). Efficient
recovery of ENU-induced mutations from the zebrafish germ-line.
Genetics 136:1401–1420.
Summer, W.C., Glazer, P.M., and Malkevich, D. (1989). Lambda
phage shuttle vectors for analysis of mutations in mammalian cells
in culture and in transgenic mice. Mutat Res 220:263–268.
Sun, B., Shima, N., and Heddle, J.A. (1999). Somatic mutation in
the mammary gland: influence of time and estrus. Mutat Res
427(1):11–19.
Swiger, R.R., Cosentino, L., Shima, N., Bielas, J.H., Cruz-Munoz,
W., and Heddle, A. (1999). The cII locus in the Muta™Mouse
system. Environ Mol Mutagen 34(2–3):201–207.
Tao, K.S., Urlando, C., and Heddle, J.A. (1993). Comparison of
somatic mutation in a transgenic versus host locus. Proc Natl Acad
Sci USA 90:10681–10685.
Vogelbein, K., Fournie, J.W., Van Veld, P.A., and Huggett, R.J.
(1990). Hepatic neoplasms in the mummichog Fundulus hetero-
clitus from a creosote-contaminated site. Cancer Res 50:5978–5986.
Walker, M.K., Zabel, E.W., Akerman, G., Balk, L., Wright, P., and
Tillitt, D.E. (1996). Fish egg injection as an alternative exposure
route for early life stage toxicity studies: description of two unique
methods. Techniques in aquatic toxicology, Ostrander, G.K. (ed.).
Boca Raton, FL: CRC Press.
Walker, V.E., Jones, I.M., Crippen, T.L., Meng, Q., Walker, D.M.,
Bauer, M.J., Reilly, A.A., Tates, A.D., Nakamura, J., Upton, P.B.,
and Skopek, T.R. (1999). Relationships between exposure, cell loss
and proliferation, and manifestation of Hprt mutant T cells fol-
lowing treatment of preweaning, weaning, and adult male mice
with N-ethyl-N-nitrosourea. Mutat Res 431:371–388.
Walter, C.A., Intano, G.W., McCarrey, J.R., McMahan, C.A., and
Walter, R.B. (1998). Mutation frequency declines during sper-
matogenesis in young mice but increases in old mice. Proc Natl
Acad Sci USA 95:10015–10019.
S194 Richard N. Winn et al.
Wang, X., Suzuki, T., Itoh, T., Honma, M., Nishikawa, A., Fu-
rukawa, F., Takahashi, M., Hayashi, M., Kato, T., and Sofuni, T.
(1998). Specific mutational spectrum of dimethylnitrosamine in
the lacI transgene of Big Blue C57BL/6 mice. Mutagenesis 13(6):
625–630.
Watson, D.E., Cunningham, M.L., and Tindall, K.R. (1998). Spon-
taneous and ENU-induced mutation spectra at the cII locus in Big
Blue Rat2 embryonic fibroblasts. Mutagenesis 13(5):487–497.
Winn, R.N., Van Beneden, R.J., and Burkhart, J.G. (1995). Trans-
fer, methylation and spontaneous mutation frequency of
fX174am3cs70 sequences in medaka (Oryzias latipes) and mum-
michog (Fundulus heteroclitus): implications for gene transfer and
environmental mutagenesis in aquatic species. Mar Environ Res
40(3):247–265.
Winn, R.N., Norris, M.B., Brayer, K.J., Torres, C., and Muller, S.L.
(2000). Detection of mutations in transgenic fish carrying a bac-
teriophage lambda cII transgene target. Proc Natl Acad Sci USA
97(23):12655–12660.
Zimmer, D.M., Harbach, P.R., Mattes, W.B., and Aaron, C.S.
(1998). Comparison of mutant frequencies at the transgenic
lambda lacI and cII loci in control and ENU-treated Big Bluet
mice. Environ Mol Mutagen 33:249–256.
Transgenic Fish Models for Detecting Mutations S195