Contribution of dichloroacetate and trichloroacetate to liver tumor induction in mice by trichloroethylene
Toxicology and Applied Pharmacology 182,
55– 65 (2002)
Contribution of Dichloroacetate and Trichloroacetate to Liver Tumor
Richard J. Bull,*,†,2 Gayle A. Orner,* Rita S. Cheng,* Lisa Stillwell,* Anja J. Stauber,†
Lyle B. Sasser,* Melissa K. Lingohr,† and Brian D. Thrall*,†
*Molecular Biosciences Department, Pacific Northwest National Laboratory, Richland, Washington 99352;
†Pharmacology/Toxicology Program, Washington State University, Pullman, Washington 99163
Received August 13, 2001; accepted April 13, 2002
tumors were c-Jun
؉, 13 were c-Jun
؊, and 9 had a mixed pheno-
Contribution of Dichloroacetate and Trichloroacetate to Liver
type. Mutations of the H-ras protooncogene were also examined in
Tumor Induction in Mice by Trichloroethylene. Bull, R. J., Orner,
DCA-, TCA-, and TRI-induced tumors. The mutation frequency
G. A., Cheng, R. S., Stillwell, L., Stauber, A. J., Sasser, L. B.,
detected in tumors induced by TCA was significantly different
Lingohr, M. K., and Thrall, B. D. (2002). Toxicol. Appl. Pharma-
from that observed in TRI-induced tumors (0.44 vs 0.21, p < 0.05),
col. 182, 55– 65.
whereas that observed in DCA-induced tumors (0.33) was inter-
Determining the key events in the induction of liver cancer in
mediate between values obtained with TCA and TRI, but not
mice by trichloroethylene (TRI) is important in the determination
significantly different from TRI. No significant differences were
of how risks from this chemical should be treated at low doses. At
found in the mutation spectra of tumors produced by the three
least two metabolites can contribute to liver cancer in mice, di-
compounds. The presence of mutations in H-ras codon 61 ap-
chloroacetate (DCA) and trichloroacetate (TCA). TCA is pro-
peared to be a late event, but ras-dependent signaling pathways
duced from metabolism of TRI at systemic concentrations that can
were activated in all tumors. These data are not consistent with the
clearly contribute to this response. As a peroxisome proliferator
hypothesis that all liver tumors induced by TRI were produced by
and a species-specific carcinogen, TCA may not be important in
TCA. 2002 Elsevier Science (USA)
the induction of liver cancer in humans at the low doses of TRI
Key Words: trichloroethylene; dichloroacetate; trichloroacetate;
encountered in the environment. Because DCA is metabolized
trichloroethylene; mutation analysis; H-ras; c-Jun; liver tumors.
much more rapidly than TCA, it has not been possible to directly
determine whether it is produced at carcinogenic levels. Unlike
TCA, DCA is active as a carcinogen in both mice and rats. Its
Trichloroethylene (TRI) is a common contaminant of ground
low-dose effects are not associated with peroxisome proliferation.
The present study examines whether biomarkers for DCA and
water as a result of poor disposal practices of the past. As a
TCA can be used to determine if the liver tumor response to TRI
consequence, this solvent is the focus of many cleanup oper-
seen in mice is completely attributable to TCA or if other metab-
ations of uncontrolled hazardous waste sites. TRI is carcino-
olites, such as DCA, are involved. Previous work had shown that
genic in both mice and rats, but at different sites, the liver and
DCA produces tumors in mice that display a diffuse immunore-
kidney, respectively (NCI, 1976; NTP, 1988; NTP, 1990).
activity to a c-Jun antibody (Santa Cruz Biotechnology, SC-45),
Liver tumor induction in mice has been the tumor most critical
whereas TCA-induced tumors do not stain with this antibody. In
from the standpoint of environmental regulation (Bull, 2000).
the present study, we compared the c-Jun phenotype of tumors
Under the proposed cancer risk guidelines of the U.S. Envi-
induced by DCA or TCA alone to those induced when they are
ronmental Protection Agency (EPA, 1996), identifying the
given together in various combinations and to those induced by
TRI given in an aqueous vehicle. When given in various combi-
dose–response behavior of key events involved in carcinogenic
nations, DCA and TCA produced a few tumors that were c-Jun
responses can be used for developing alternative risk assess-
many that were c-Jun
؊, but a number with a mixed phenotype
that increased with the relative dose of DCA. Sixteen TRI-induced
A major difficulty in developing alternative approaches for
assessing risk from TRI is the fact that three of its metabolites
G. A. Orner was supported by Associated Western Universities, Inc.,
are capable of inducing liver cancer in mice (Bull et al.
Northwest Division (AWU NW) under Grant DE-FG06-89ER-75522 or DE-FG06-92RL-12451 with the U.S. Department of Energy (DOE). Research was
Daniel et al.
, 1992; DeAngelo et al.
, 1999; Pereria, 1996). Two
funded by U.S. DOE contract number DE-AC06 –76RL0 1830. A portion of
of these metabolites have distinct modes of action, dichloro-
this work was presented at the 37th Annual Meeting of the Society of
acetate (DCA) and trichloroacetate (TCA). The third metabo-
Toxicology, March, 1998, Seattle, WA.
lite, chloral hydrate, is probably active as a result of its con-
To whom correspondence should be addressed at Washington State Uni-
version to one or both of these two metabolites. DCA inhibits
versity–Tri-Cities, 2710 University Drive, Richland, WA 99352. Fax: (509)372-7552; E-mail: [email protected]
cell replication and apoptosis (Snyder et al.
, 1995) but stimu-
lates cell division in tumor cells that are immunoreactive to
Biosystems (Foster City, CA). All other chemicals were obtained from Sigma
c-Jun antibodies (Stauber and Bull, 1997). On the other hand,
TCA produces tumors that are uniformly negative with respectto the c-Jun phenotype. This phenotype is consistent with its
activity as a peroxisome proliferator (DeAngelo et al.
Male B6C3F1 mice were purchased from Charles River Laboratories (Ra-
leigh, NC) at 31–35 days of age with experiments beginning at 6 weeks of age
Ordinarily, the first approach to assigning causality to a
for all experiments. Protocols and animal care were approved by the Institu-
metabolite in tumorigenesis would be an attempt to measure its
tional Animal Care and Use Committtee at Pacific Northwest National Labo-
concentration in the body and associating that with tumorigenic
ratory. Animals were housed four to six per cage in shoebox cages and had free
concentrations observed when the compound is itself admin-
access to NIH-07 rodent chow and drinking water at all times. Control, TCA,and DCA drinking water solutions were prepared from deionized water and
istered. This can be done with relative ease with TCA (Fisher,
adjusted with sodium hydroxide to pH 7.0 Ϯ 0.2. Animal rooms were main-
2000; Clewell et al.
, 2000). However, it has been shown that
tained on a 12-h light– dark cycle with temperatures controlled to 22–24°C and
DCA administered directly in drinking water induces liver
cancer in mice where blood concentrations are below thedetection limit. (Kato-Weinstein et al.
1998; Merdink et al.
Mutations in the ras
protooncogene have been used to de-
After a 1-week acclimation period, animals were randomly
assigned to treatment groups and given 0, 0.5, or 2 g/L DCA or 2 g/L TCA in
termine if distinct patterns of DNA sequence alterations can
their drinking water for the duration of the study. The doses of DCA were
provide indications of the type of DNA damage that might be
selected to bracket the highest and lowest doses that have produced hepatic
produced by carcinogens. The presence of ras
tumors without adversely affecting body weight gain. The lowest of these
chemically induced tumors was originally suggested as a
doses result in blood levels of DCA and TCA that roughly match (Kato-
means of determining whether a chemical was genotoxic
Weinstein et al.
, 1998) those produced by administering the lowest dose of TRIthat was previously shown to be carcinogenic (Merdink et al.
, 1998; NTP,
(Reynolds et al.
, 1987). However, the discovery that sponta-
1990). A subset of mice was sampled after 52 weeks for high doses and
neous tumors also contain this oncogene indicated that this
associated control mice. Animals treated at 0.5 g/L were treated for an
assumption was incorrect (Fox and Watanabe, 1985). Several
additional 35 weeks and an equal number of control animals were maintained
nongenotoxic carcinogens have been shown to produce liver
for the same period. Times of euthanasia were selected based upon prior
tumors in male B6C3F1 mice with a mutation frequency con-
studies that established the appropriate latent periods for liver tumor develop-ment at these doses (Bull et al.
, 1990; Stauber and Bull, 1997). Only four
siderably below those that result spontaneously. Among these
animals were lost to miscellaneous causes in this experiment. There was no
chemicals are peroxisome proliferators (Maronpot et al.
evidence of treatment-related death. Tumors were identified at necropsy and
1995). DCA and TRI were found to induce tumors with similar
their diameters were measured in two dimensions (longest and shortest) to
mutation spectra (Anna et al.
, 1994), whereas only limited data
obtain a mean diameter. Histopathological examination was limited to 15
have been available on TCA (Fereira-Gonzalez et al.
randomly selected tumors to ensure that nonneoplastic lesions were not beingmisclassified.
Schroeder et al.
(1997) found H-ras
to be rare in liver tumorsinduced by 3.5 g/L DCA in female B6C3F1 mice and raise
DCA and TCA were administered as a mixture to male
B6C3F1 mice in drinking water. Twenty animals were assigned to each of 10
questions about the role such mutations play in DCA-induced
groups that received the following concentrations of DCA or TCA in their
drinking water for 52 weeks: 0, 0.5 g/L TCA, 2 g/L TCA, 0.1 g/L DCA, 0.5
In the present study, we examined the question of whether
g/L DCA, 2 g/L DCA, 0.1 g/L DCA ϩ 0.5 g/L TCA, 0.5 g/L DCA ϩ 0.5 g/L
TRI (administered in an aqueous vehicle) induces tumors that
TCA, 0.1 g/L DCA ϩ 2 g/L TCA, or 0.5 g/L DCA ϩ 2 g/L TCA. The animals
carry the c-JunϪ phenotype, which would be predicted if TCA
were euthanized at 52 weeks, the livers were examined for gross lesions asindicated above, and the histological sections were made for immunostaining
were entirely responsible. We also investigated whether vari-
and examination by a pathologist. Only two mice were lost during the course
ations in this phenotype could be produced by treating animals
of this experiment (one in the 2 g/L DCA group and another in the 0.5 g/L
with various mixtures of DCA and TCA in drinking water. In
addition, the mutation frequency and spectra in the H-ras
TRI was administered once daily, 7 days per week by
codon 61 in tumors produced by DCA, TCA, and TRI were
gavage in a 5% Alkamuls in distilled water vehicle to a group of 50 mice for
investigated to determine whether the hypothesis that TCA
a period of 79 weeks. This mode of administration was used because Ͼ10,000
alone was responsible for the liver tumors could be supported
mg/L TRI would be necessary to achieve a carcinogenic dose. Preliminaryexperiments established that such high concentrations would not be consumed
by mice. The use of the Alkamuls vehicle also avoided some of the pharma-cokinetic complications associated with corn oil gavage. A control group of 15
MATERIALS AND METHODS
mice received an equivalent volume of the vehicle by the same method ofadministration. At the time of euthanasia, the livers were removed, tumors
were identified, the size of the lesions was measured, and the tissues weresectioned for examination by a pathologist and for immunostaining. There
DCA was obtained from Fluka Chemical Corporation (Ronkonkoma, NY)
were six gavage-associated deaths during the course of this experiment among
and TCA was purchased from Aldrich Chemical Company (Milwaukee, WI).
a total of 10 animals that died with TRI treatment. No animals were lost in the
Reagents for PCR and sequencing were purchased from Perkin–Elmer Applied
CONTRIBUTION OF DCA AND TCA TO TRI–INDUCED LIVER TUMORS
Tumor Sampling, PCR Amplification, and Sequencing
spectra were compared using a mutation analysis program described by Cari-ello et al.
(1994). A p
value Յ 0.05 was considered significant.
At the conclusion of each experiment, animals were euthanized, livers were
removed, and macroscopically visible lesions (tumors) were identified, mea-
sured, and separated from surrounding tissue. A portion of tissue was excisedfrom 25 tumors per treatment group (where available), frozen in liquid nitro-
The serial liver sections were stained with the c-Jun antibody, SC-45 (Santa
gen, and stored at Ϫ80°C until used for ras
mutation analysis. Remaining
Cruz Biotechnology) in a 1 to 25 dilution by methods previously described
portions of the tumor were either snap-frozen in liquid nitrogen for use in
(Stauber and Bull, 1997). This antibody was raised against the sequence
Western blotting or were fixed in 10% neutral buffered formalin for 24 h and
TPTPTQFLCPKNVTD, which includes Thr 91 and 93 of mouse c-Jun. These
then were transferred into 70% ethanol until they were paraffin-embedded and
residues are phosphorylated by JNK and this activity is thought to lead to
examined histologically. Tumor samples (and samples from liver not including
dephosphorylation of c-Jun in the DNA-binding domain (Nakano et al.
tumors in Experiment 1) for H-ras
analysis were digested overnight at 50°C in
which leads to activation of c-Jun as a transcription factor. Therefore, this is
DNA lysis buffer (50 mM Tris–Cl, pH 8.0; 20 mM NaCl; 1 mM EDTA; 1%
potentially a deactivated form of c-Jun that accumulates in liver tumors of male
SDS; and 1 mg/mL proteinase K), proteinase heat inactivated by boiling,
mice (Kato-Weinstein et al.
diluted 1:10 in water, and 1– 4 L was used as template for PCR amplification.
DNA was amplified using a modification of the procedure described byManjanatha et al.
(1996). The primer pairs GCCGCTGTAGAAGCTATGA
and CTTGGTGTTGTTGATGGCAAATACA were used to amplify a 469-bpsection of H-ras
containing the first and second exon. PCR reaction mixtures
As previously reported (Bull et al.
, 1990), the percentage of
contained 4 mM magnesium chloride, 10 mM Tris, 50 mM potassium chloride,
body weight made up by liver (liver somatic index) was sig-
0.2 mM deoxynucleotides, 0.2 M of each primer, and 0.01 U/L Thermusaquaticus
DNA polymerase (Perkin–Elmer, Norwalk, CT). A second amplifi-
nificantly elevated by DCA or TCA treatment at the doses and
cation of an internal sequence containing codon 61 and adding M13 sequence
periods of treatment that were examined in this study (Table 1).
to both ends was then conducted (primers: TGTAAAACGACGGCCAGTA-
There were relatively minor effects on body weight. Only in
CAGCCCAGGTCT-TGTA and CAGGAAACAGCTATGACCGTTGATG-
the case of mixed treatments with DCA and TCA and with TRI
GCAAATAC). After amplification, PCR products were purified using Micro-
were there statistically significant effects on body weight. Mice
con 100 filter units (Amicon, Beverly, MA) and sequenced on an automatedcycle sequencer (ABI 377 DNA sequencer). PCR products were sequenced in
administered TRI for 79 weeks had body weights that were
the forward direction using Perkin–Elmer Applied Biosystems dye primers and
depressed 11% relative to concurrent controls. Administration
confirmed by sequencing in the reverse direction using either dye primer
of TRI in Alkamuls was done to obtain tumors independent of
(Experiment 1) or D-rhodamine terminator (Experiment 2) cycle sequencing.
the corn oil vehicle that was used in previous studies. The
DNA from several mutant tumors was reamplified and cloned using a
parallel study using mixtures of DCA and TCA in drinking
TOPO-TA Cloning Kit (Invitrogen, Carlsbad, CA), providing an additionaldegree of confidence in the detection of mutations.
water was done to determine whether the results obtained withTRI could be accounted for by these metabolites. The effects
on body weight and somatic index of the liver in mice treatedwith TRI, the mixtures of metabolites, and their concurrent
Tumors and adjacent noninvolved liver tissue were homogenized individu-
controls are also provided in Table 1. The relatively small
ally in ice-cold homogenization buffer (10 mM KPi, pH 7.5; 0.15 M KCl; 20%glycerol; 1 mM EDTA; 0.5 mM PMSF; 1.9 g/mL aprotinin; 2 g/mL
tumor burden seen at 52 weeks had little effect on liver weight,
leupeptin; and 200 M sodium orthovanadate). Proteins were separated by
so these data indicate that DCA and TCA produce a significant
sodium dodecyl sulfate–polyacrylamide gel electrophoresis on 10% acryl-
hepatomegaly. Effects seen on liver weight with longer treat-
amide gels (Laemmili, 1970) and electrophoretically transferred to PVDF
ment are complicated by increased tumor burdens.
membranes using a semidry blotter (Emprotech, Natick, MA). Blots were
All treatments gave rise to tumorigenic responses in the liver
probed with primary antibodies to Ras (Upstate Biotechnology, Lake Placid,NY), Mek (Transduction Laboratories, Lexington, KY), active Erk 1/2 (Pro-
consistent with our past experience. The magnitude of the
mega, Madison, WI), c-Fos, and insulin receptor ␤ (Santa Cruz Biotechnology,
response to 2 g/L DCA and TCA was about 50% of that seen
Santa Cruz, CA) followed by incubation with a horseradish peroxidase-linked
in past experiments (Bull et al.
, 1990; Stauber and Bull, 1997;
secondary antibody (Biorad, Hercules, CA) and the detection of immunoreac-
DeAngelo et al.
, 1999). The tumor yield with TRI was slightly
tive proteins by chemiluminescence (Amersham ECL kit, Amersham Corp.,
higher than was expected from prior NCI (1976) and NTP
(1990) bioassays. All gross lesions in this experiment were
examined by a pathologist and subjected to sequencing of theH-ras codon 61 and a random sample stained for c-Jun.
Sequencing chromatograms were compared using Sequencher software
Tumor incidence and multiplicity (number of nodules, ade-
(Ver. 3.0, Gene Codes Corporation, Ann Arbor, MI). Western blots were
nomas, and carcinomas per animal) were significantly higher in
scanned on a flatbed scanner and quantified on a Power Macintosh 7100 usingthe public domain software NIH Image, Version 1.57. Statistical analyses were
animals treated with 2 g/L DCA or TCA for 52 weeks than in
conducted using Sigma Stat Version 2.0 (Jandel Scientific, San Rafael, CA)
control mice (Table 1). In addition, tumors were induced in
except as otherwise noted. Animal weights were compared by one-way
animals treated with 0.5 or 2 g/L DCA for 87 weeks. Mixtures
ANOVA followed by the Tukey test for pairwise comparisons. Tumor inci-
of DCA and TCA increased tumor induction in all combina-
dence was compared using Fisher’s Exact test. Tumor size, multiplicity, and
tions. TRI at a daily dose of 1 g/kg per day for 79 weeks also
liver somatic indices were compared using the Kruskal–Wallis nonparametricone-way analysis of variance on ranks. Comparisons of mutation frequencies
increased the gross tumor response significantly over the con-
between treatments were tested for significance by 2 analysis and the mutation
current vehicle control. The only treatment that did not in-
Effect of Dichloroacetate and Trichloroacetate on Terminal Body Weight, Liver Somatic Index,
and Tumor Incidence, Number, and Mean Diameter
Values are means Ϯ SEM.
Total number of tumors divided by total number of animals.b
Drinking water vehicle.c
Significantly different from 52-week controls at p
Significantly different from 79- or 87-week controls at p
5%Alkamuls in water vehicle.
crease tumor incidence or multiplicity was 0.1 g/L of DCA in
nodules were identified. One of these was found to be a
myelogenous lymphoid lesion. The remaining tumors found in
The dose–response relationships between tumor responses
the liver were hyperplastic nodules. TRI treatment significantly
produced by DCA or TCA alone or in combination at 52 weeksof treatment are displayed in Fig. 1. In this figure, the results ofboth experiments using DCA given alone are combined asbeing more representative than found in the DCA alone treat-ment group in the mixture study. The experiments utilizingmixtures of DCA and TCA in drinking water produced re-sponses that were very close to additive when compared to alow dose of DCA (0.1 g/L) was combined with higher doselevels of TCA (0.5 and 2 g/L) when the chemicals wereadministered alone. However, DCA at 0.5 g/L failed to pro-duce a higher tumor incidence in combination with 2 g/L TCAthan was observed with TCA alone. Consequently, the onlyevidence of an interaction was a smaller number of tumors thanwould be expected in this latter group. However, the differencebetween the sum of the responses and that seen in the mixturewas not statistically significant.
Dose–response relationships for tumor induction by treating male
Table 2 displays the pathological characterization of the
B6C3F1 mice with varying doses of dichloroacetate (DCA) and trichloroac-
tumors that were produced in the TRI experiment. Of the
etate (TCA) alone and in combination in drinking water for 52 weeks. The
tumors identified in control mice for the TRI study, only one
-axis provides the concentration of either DCA or TCA in drinking water. Thelegend indicates the concentration of the second compound when provided in
was a carcinoma and four were adenomas. These occurred in
combination. Results are expressed as mean number of tumors per animal Ϯ
three animals, giving an incidence of 0.20 at 79 weeks of
SEM. See Table 2 for more explicit description of incidence data and number
treatment (Table 2). In addition, four histocytic proliferative
CONTRIBUTION OF DCA AND TCA TO TRI–INDUCED LIVER TUMORS
Pathological Characterization of Tumors Produced by Trichloroethylene and Selected Tumors
Induced by Dichloroacetate or Trichloroacetate
Values in parentheses are percentages.
increased the incidence of all three classes of hepatocellular
produced by TRI, DCA, and TCA expressed c-Jun. As previ-
lesions over that observed in control mice. Adenomas were
ously shown, the c-Jun immunoreactivity found in tumor cells
observed at an incidence of 0.64, carcinomas at 0.19, and their
was distributed primarily in the cytosolic compartment when it
combined incidence was 0.75. Several mice had more than one
was present. Earlier work by Stauber and Bull (1997) indicated
adenoma and/or carcinoma (Table 2). Histocytic proliferative
that the occurrence of a c-JunϪ lesion was diagnostic of TCA,
nodules were observed at the same incidence in TRI-treated
whereas almost all lesions induced by DCA were c-Jun posi-
and control mice and including these lesions in the total count
tive. This result was generally borne out in the present study,
raises the incidence to 0.83 in the TRI-treated mice.
but a higher proportion of c-Jun tumors were observed when
The pathological characterization of hepatic tumors from
DCA was administered alone. Nevertheless, approximately
mice treated with DCA and TCA and mixtures of these two
50% of DCA-induced tumors were c-Junϩ. When mixtures of
metabolites are also displayed in Table 2. The incidence ofhyperplastic nodules, hepatocellular adenomas, and hepatocel-
lular carcinomas are reported and the total number of lesions of
Frequency of Immunoreactivity of Tumors Produced by DCA,
each type is also provided. The pathology data presented have
TCA, and TRI to c-Jun Antibody (Santa Cruz, SC-45)
been confined to those treatments with DCA that were runconcurrently with the mixture studies to avoid confusing the
results with longer periods of treatment. As previously shown,
both DCA and TCA produce dose-related increases in tumor
incidence within a 52-week period at doses of 0.5 g/L of
drinking water and above. In general, DCA induces a greater
number of tumors at a given dose, but a higher fraction of the
tumors produced by TCA are hepatocellular carcinomas. Tu-
mor responses with mixed exposures of the two haloacetates
were significantly increased in the mixed exposures. In terms
of the total tumor yields, the effects appeared to be approxi-
mately additive. However, it was notable that the addition of
DCA to fixed doses of TCA substantially enhanced the yield of
hepatocellular adenomas and produced little, if any, enhance-
ment of the incidence or total numbers of hepatocellular car-
Table 3 indicates the relative frequency at which tumors
Values in parentheses are frequencies.
104 weeks. However, the present study utilized lower dosesand was of a shorter duration than the Ferreira-Gonzalez study.
The mutation spectrum of the TCA-treated animals from thecurrent study is not significantly different from that of thehistorical controls and the AAA sequence at codon 61 was themost common mutation.
When the H-ras
mutation frequencies for all studies of
DCA-induced tumors that were conducted below the maxi-mally tolerated dose are analyzed, a clear increase in the H-rasmutation frequency in tumors is seen with time of treatment (orage) (see Maronpot et al.
, 1995 as well as the data presented inthis manuscript). Data from different time points were notavailable for the TCA and TRI, however.
mutations also seem to be a late event in TRI-
Mutation frequency and spectra for the H-ras
codon 61 in mouse
induced hepatic tumors. In a limited subset of tumors that were
liver tumors induced by TRI (1 g/kg per day), TCA (0.5 and 2 g/L drinkingwater), and DCA (0.5 and 2 g/L of drinking water). The number of tumors
both sequenced and classified histologically, only 8 of 34
sequenced for each treatment is indicated by n
. The mutation frequency seen
(24%) of the adenomas contained codon 61 mutations while 9
in TCA-induced tumors was significantly different than those induced by TRI
of 15 (60%) carcinomas contained mutant H-ras
at this codon.
Ͻ 0.05 by Fisher’s Exact test). The difference in mutation frequency in TRI-
The percentage of mutant sequence within each tumor (as
and DCA-induced tumors was not statistically significant.
judged by the ratio of mutant to wild-type peak heights) waslower than would be expected if the tumors were the result of
DCA or TCA were administered, a large fraction of the tumors
clonal expansion of cells bearing mutant ras.
displayed a mixed c-Jun phenotype. While half the lesions seen
contained less than 50% mutant sequence and only one was
with DCA alone were c-Junϩ, the mixtures gave rise to tumors
completely without wild-type sequence. The average Ϯ SE
that were c-Junϩ in one part of the tumor and c-JunϪ in other
ranged from 38 Ϯ 5% in the 0.5 g/L DCA treatment group to
portions. When TRI was administered, 42% of the lesions
49 Ϯ 13% in the 2 g/L DCA for the 87 weeks group. There
displayed a c-Junϩ phenotype, only 34% exhibited a c-JunϪ
were no significant differences in this measure classified by
phenotype, and 24% were of the mixed phenotype.
Mutation frequencies and spectra from tumors from animals
Proteins involved in the MAP kinase-signaling cascade were
treated with TRI, DCA, and TCA are shown in Fig. 2. No
examined in order to determine if the three common codon 61
mutations were detected in DNA from normal tissue of
mutations of ras
had different effects on downstream effectors.
B6C3F1 mice. Few tumors were observed in control mice
Figure 3 contains Western blots of TCA tumor and nonin-
sampled at the times examined in this study (nine control
volved tissue probed with antibodies to ras, Mek, active Erk
tumors were sequenced, of these only two contained a codon
1/2, and c-Fos. The antibody used in the current experiment
61 mutation). Therefore, for statistical purposes, mutation data
recognized several proteins in mouse liver homogenates. A
from this study were compared to historical control data
28-kDa protein was present as a doublet in nontumor tissue,
(Maronpot et al.
, 1995). However, we have chosen to depict
but in tumor tissue only the higher-molecular-weight protein
mutation spectra in a way that includes the wild-type sequence
was present (Fig. 3). Ras has been reported to migrate as a
(CAA), as it provides a simultaneous view of the mutation
doublet in Jurkat cells treated with lovastatin, where the faster
migrating band was identified as farnesylated, membrane-
codon 61 mutation frequency in tumors of mice
bound p21 and the slower migrating band was identified as
differed significantly (p
Ͻ 0.05) between TRI and TCA (Fig.
unprocessed, cytosolic p21 (Goldman et al.,
1996). It is pos-
2). Only 21% of the tumors from TRI-treated animals had a
sible that the ras
-immunoreactive protein accumulating in
mutation in codon 61, whereas 44% of the tumors from TCA-
TCA and DCA tumors is the unprocessed, inactive form. This
treated animals had mutations. This difference in mutation
is supported by our observation (not shown) that this protein is
frequency was statistically different (p
Ͻ 0.05) by Fisher’s
primarily expressed in the cytosol of tumors. Conversely, our
exact test. Tumors from DCA-treated mice were intermediate
finding that levels of Mek and the dually phosphorylated (ac-
in their frequency of H-ras mutations (33%), but this was not
tive) forms of MAPK (p44Erk1 and p42Erk2) are strongly
significantly different from tumors induced by TRI. In all
induced in tumor tissue would not support this view. Each pair
cases, these frequencies are below the frequency of codon 61
(T/NT) is from tumor vs adjacent, noninvolved tissue from the
mutations in spontaneous tumors in this strain of mice (56%)
same liver. A ras
-immunoreactive protein is present as a single
(Maronpot et al.
, 1995). The mutation frequency reported by
intense band in tumors and as a doublet in the noninvolved
Ferreira-Gonzalez et al.
(1995) was 55% in 11 hepatocellular
tissue (both identified by the single arrow in Fig. 3). Mek levels
carcinomas of male B6C3F1 mice treated with 4.5 g/L TCA for
are increased in tumor relative to adjacent tissue, as is phos-
CONTRIBUTION OF DCA AND TCA TO TRI–INDUCED LIVER TUMORS
Western blots of tissue extracts of tumors carrying different mutations in codon 61 of the H-ras
gene and surrounding normal tissue for Ras, Mek,
active Erk 1/2, and c-Fos. The high and low MW bands for Ras referred to in the text are both in the doublet identified by the arrow. Differences in proteinexpression were consistently detected when normal tissue was compared to tumors from the same animal. The expression of proteins within tumors did notdepend upon the sequence in H-ras
phorylation of the MAP kinases Erk 1/2. These differences are
also observed in tumors from control and DCA-treated ani-mals. Interestingly, there was no difference in the levels of any
These results strongly suggest that TCA is not solely respon-
of these signaling proteins between different mutation types or
sible for liver tumors when mice are treated with TRI. The liver
even between codon 61 mutant and wild-type tumors.
tumor response to TRI has been exclusively attributed to TCA
Figure 4 provides information about the cell-signaling envi-
in the past (Elcombe, 1985). However, the c-Junϩ phenotype
ronment within DCA-induced tumors relative to surrounding
is not produced when TCA is administered alone to B6C3F1
tissue and in tissue from control mice. These data indicate a
mice (Stauber and Bull, 1997) nor by other peroxisome pro-
consistent upregulation of the insulin receptor, ras
liferators (Nakano et al.
, 1994). Furthermore, the metabolites
and ERK 1/2 activity in tumors relative to normal tissue. It is
display the same proclivity for producing a particular pheno-
of note that these same changes were seen in tumors that arose
type when they stimulate the growth of colonies from suspen-
spontaneously in control animals as well.
sions of primary mouse hepatocytes on soft agar (Stauber et al.
Figure 5 provides more direct comparison of insulin receptor
1998). In the TRI-treated mice, two-thirds of the tumors that
expression in the tumor and nontumor portions of liver from
were immunohistochemically examined expressed the c-Junϩ
mice treated with TRI, TCA, and two concentrations of DCA.
phenotype exclusively or in part. A caution must be expressed
It appears that insulin receptor upregulation occurs in most
that this result does not necessarily implicate c-Jun in the
liver tumors induced in the male B6C3F1 mouse relative to
development of the tumor, because the antibody used in this
normal portions of the liver. Therefore, this parameter does not
study recognizes a form of the transcription factor that islargely located in the cytosol that surrounds the nucleus, rather
distinguish between tumors induced by any of these three
than within the nucleus. Other antibodies gave different pat-
terns to the staining because they interacted differently tophosphorylated and nonphosphorylated forms of the antibodyat different epitopes (Kato-Weinstein et al.
The detection of a mixed phenotypic expression of c-Junϩ
cells with TRI treatment clearly indicates that TCA is notentirely responsible for the liver tumors produced by TRI.
When given alone, DCA induced 45–50% c-Junϩ lesionswhile c-Junϩ lesions have never been observed with TCA.
Even higher percentages of tumors were found to express thec-Junϩ phenotype with prior studies (Stauber and Bull, 1997;Richmond et al.
, 1991). Since the tumor response seen at 2 g/LDCA in the present study was lower than that seen previous
Differences in insulin-receptor protein (IR), Ras, and phosphory-
experiments, the greater uniformity of DCA tumors could have
lated forms of Erk 1/2 (designated P44 and P42) in normal liver and tumorsfrom control mice and mice that were treated with dichloroacetate (DCA).
been related to the higher tumor yields at this high dose in past
Insulin receptor (IR) expression in normal liver (N) and tumors (T) of male B6C3F1 mice induced by trichloroethylene (TRI), trichloroacetate (TCA),
and the two indicated dose levels of dichloroacetate (DCA). The dose of TRI was 1 g/L daily for 87 weeks and that of TCA was 2 g/L of drinking water for52 weeks.
studies. Inconsistent findings can be anticipated at the interme-
within the tumor? Alternatively, they could represent the fu-
diate dose range because blood levels are seen to increase from
sion of two distinct lesions that arose independently. The
Ͻ1 M to 300 to 500 M when the concentrations in drinking former possibility suggests that exploration of the differentwater are increased from 0.5 to 2 g/L (Kato-Weinstein et al.
portions of these lesions for minimal differences at the
1998). The disproportionate increases in blood levels arise
genomic level could provide important insights into the ques-
from the fact that DCA is a suicide inhibitor of its own
tion of liver tumor progression. These two compounds may be
metabolism in mice in this dose range (Gonzalez-Leon et al.,
very convenient models since neither appears to be mutagenic
1999). Thus, the tumor response would be expected to vary in
at concentrations that are active in vivo
(discussed more fully
this dose region because relatively small variations in dose
(i.e., by drinking more or less water) could result in large
codon 61 mutation frequencies and spectra pro-
variations in the systemic concentrations of DCA.
vided a second test of the hypothesis that TCA was a primary,
An unanticipated finding was that the pattern of expression
if not exclusive, contributor to TRI-induced liver tumors in
in tumors from mice treated with varying combinations of
mice. This was based on the simple hypothesis that there
DCA and TCA did not give rise to tumors with distinct
should be congruence between the mutation frequency and
phenotypes but to tumors that displayed the two phenotypes in
spectra if TCA were solely responsible for the tumors. Clearly,
different parts of the same tumor. While some tumors produced
this was not the case, as the H-ras
codon mutation frequency
by TRI were found to have a mixed phenotype, a substantial
was significantly lower in TRI-induced tumors than in TCA-
fraction of the tumors that resulted expressed only the c-Junϩ
induced tumors. The mutation frequency seen in DCA-induced
phenotype. The concentrations of DCA and TCA selected for
tumors was not significantly different from that of TRI, al-
the mixture study should produce approximately the same in
though examination of the data also makes it difficult to
ratio and individual peak concentrations of DCA and TCA
attribute the tumors exclusively to DCA. Therefore, these data
that would be predicted to arise from the metabolism of a
support the hypothesis that neither metabolite is the exclusive
1-g/kg dose of TRI (Merdink et al.
, 1998). These data rule out
cause of liver tumors in TRI-treated mice.
TCA as the sole cause of liver tumors induced by TRI. Con-
The contribution of DCA to the liver tumor response in mice
versely, these data do not prove that the c-Junϩ tumors are
has been somewhat controversial primarily because of the very
entirely the result of metabolism of TRI to DCA or arise from
low levels of DCA that are produced in the metabolism of TRI
an interaction between the two metabolites. The possibility of
(Merdink et al.
, 1998). Minimally effective systemic concen-
a third factor cannot be ruled out. Because of the complexity of
trations of DCA are less than 1 M in the blood of mice
the metabolism of TRI, there are several possibilities that could
(Barton et al.
, 1999). The present study suggests that low levels
account for this change. One possible candidate is dichlorovi-
of DCA superimposed on high levels of TCA are additive, at
nyl cysteine (DCVC). It is possible that the genotoxic effects of
least at low doses. The total tumor response seen at 0.1 g/L
this metabolite could contribute to the noncongruence between
DCA and 2 g/L of TCA was not significantly greater than
findings with TRI and mixtures of DCA and TCA. However,
would be expected by the sum of their individual responses.
DCVC has not been subjected to cancer bioassay in animals.
Increasing the concentrations of DCA to 0.5 and TCA to 2 g/L
The expression of both phenotypes in the same tumors
produced a tumor response that was no greater than produced
produced by TRI or combinations of DCA and TCA is of
by 2 g/L TCA alone but remained within the confidence limits
interest. Do these lesions arise as clones and then the second
of the sum of the responses to the independent treatments at
metabolite “encourages” the growth of mutant cells that arise
CONTRIBUTION OF DCA AND TCA TO TRI–INDUCED LIVER TUMORS
Mutation spectra have been useful for backtracking mecha-
ing as the tumor grows in size. This supposition is supported by
nistically to the adducts to DNA bases produced by genotoxic
the observation that the major effect of DCA in liver tumori-
carcinogens. The utility of mutation spectra for the study of
genesis is on tumor growth rates (Miller et al.
nongenotoxic chemicals is not as clear. The H-ras
Bacterial mutagenicity assays of DCA and TCA have gen-
frequency and spectrum of the tumors from male B6C3F1 mice
erally been negative (Bull, 2000). Recently DCA was found to
treated with 2 g/L TCA resembled those of historical controls.
be weakly, but clearly mutagenic in the mouse lymphoma
This is comparable to what Ferreira-Gonzalez et al.
assay and cytogenetic analyses revealed an increase in chro-
observed in a limited number of tumors from mice given a
mosome aberrations (Harrington-Brock et al.
, 1998). However,
higher dose (3.5 g/L) of TCA for 104 weeks. Tumors induced
these effects occurred at concentrations in the test systems that
by most other nongenotoxic carcinogens, including phenobar-
are several orders of magnitude greater than required for DCA
bital, chloroform, and the peroxisome proliferators ciprofibrate
induction of liver cancer (Kato-Weinstein et al.
, 1998; Merdink
and methyl clofenapate, have lower ras
, 1998). In the Big Blue transgenic mouse mutagenesis
than spontaneous tumors (Fox et al.,
1990; Hegi et al.,
assay, an increased frequency of mutations in the bacterial lac
Stanley et al.,
1994). One notable exception occurred in lesions
target gene occurred in mice treated with DCA at 3.5 g/L for
of female B6C3F1 mice treated with the peroxisome prolifera-
60, but not for 4 or 10 weeks nor with any lower doses (Leavitt
tor LY171883, in which the H-ras
mutation frequency was
, 1997). High doses of DCA (Ն2 g/L in drinking water)
64% (Helvering et al.,
1994). Although LY171883 is a perox-
cause substantial increases in cell replication within cells with
isome proliferator, it activates a different member of the per-
a c-Junϩ phenotype and many small foci of such cells are
oxisome proliferator receptor family (PPAR-␥) than does cip-
detected in the liver of mice treated with these high concen-
rofibrate (Kliewer et al.,
1994). TCA has been shown to
trations of DCA (Stauber and Bull, 1997). Therefore, there are
activate both PPAR-␣ and PPAR-␥ (Maloney and Waxman,
alternative explanations for this observation based upon mea-
surement of DCA’s effects on tumor growth rates (Miller et al.
mutation frequency of the DCA-induced tumors
in this study was lower than reported previously (Anna et al.
Expression and activity of proteins involved in the MAP
1994; Ferreira-Gonzalez et al.
, 1995). A number of factors
kinase signaling cascade were measured in order to determine
could account for this, including differences in mutation de-
if there were differential effects on this pathway in tumors
tection methodologies, treatment duration, and/or dose. Our
possessing codon 61 mutations in H-ras
. Activation of the
analysis of the H-ras
mutation frequency in DCA-induced
MAP kinase cascade occurred in all tumors examined and was
tumors over time suggests that codon 61 mutations may be late
independent of H-ras
codon 61 mutation status. This is con-
events in male B6C3F1 mice. This is supported by the obser-
sistent with a recent study by Kalkuhl et al.
(1998) in which
vation that when the time of euthanasia is considered over all
Raf activity was found to be activated in mouse liver tumors
available studies with the frequency of codon 61 H-ras
without regard to the H- or K-ras
mutation status. Levels of
tions increases with time (Maronpot et al.
, 1995). It should be
mRNA have been found to be elevated in tumors of
noted that treatments of 5 g/L DCA (Fereira-Gonzalez et al.
,1995), which substantially exceeds the maximally tolerated
DCA- or TCA-treated mice (Nelson et al.
, 1990; Richmond et
dose in that it results in very substantial decreases in water
, 1991). Nesnow and DeAngelo (1995) also reported that
consumption and losses in body weight does result in a higher
DCA-induced tumors lacking H-ras
mutation frequency in a shorter time period. Moreover, it
would be anticipated that a large portion of this group did not
Examination of insulin receptor expression revealed that this
survive the treatment to the 76 weeks duration of the study.
did not distinguish tumors produced by DCA, TCA, or TRI. In
Therefore, it is likely that these data represent a censored
all cases, insulin receptor protein expression was increased in
population. In a limited number of tumors that were both
tumor regardless of cause. In the case of DCA treatment,
sequenced and classified histologically, we observed that the
Lingohr et al.
(2001) have shown that there is a consistent
mutation frequency was higher in hepatocellular carcinomas
downregulation of the insulin receptor in normal hepatocytes,
than in adenomas. Anna et al.
(1994) also reported a higher
an effect that is reproducible in isolated hepatocytes.
frequency of H-ras
mutations in carcinomas compared to ad-
In summary, the occurrence of two distinct c-Jun phenotypes
enomas in their TRI- and DCA-treated animals, and Nelson et
of liver tumors in mice treated with TRI is inconsistent with
(1990) noted that the expression of H-ras
TCA being solely responsible for these tumors. It is probable
highly correlated with malignancy. This is in contrast to studies
that DCA contributes to the development of liver tumors in
of strong DNA-alkylating agents for which ras
mice treated with TRI, but mixtures of DCA and TCA tend to
pears to be an early event (Wiseman et al.,
1986; Watson et al.,
produce tumors with a mixed phenotype, whereas TRI pro-
1995). Therefore, these studies indicate that the effects of DCA
hepatic tumors that appeared uniformly Junϩ.
and TRI are not typical of genotoxic agents. A more likely role
codon 61 mutation frequencies and spectra support these
is increasing clonal expansion with DNA damage accumulat-
conclusions. However, activation of ras
pathways are activated in all hepatic tumors examined irre-
with genotoxic and nongenotoxic hepatocarcinogens. Cancer Res. 50,
Fox, T. R., and Watanabe, P. G. (1985). Detection of a cellular oncogene in
spontaneous liver tumors of B6C3F1 mice. Science 228,
Goldman, F., Hohl, R. J., Crabtree, J., Lewistibesar, K., and Koretzky, G.
(1996). Lovastatin inhibits T-cell antigen receptor signaling independent of
The authors thank the following individuals for their assistance: Drs. Rod-
its effects on ras. Blood 88,
ney A. Miller and Gerald Dagle for pathology; Teresa Luders, Barb A. Meyers,Kristine G. Studniski, and Freddie L. Wallace for animal care; Jessica A.
Gonzalez-Leon, A., Merdink, J. L., Bull, R. J., and Schultz, I. R. (1999). Effect
Malone for technical assistance; and Faith Barker and Junko Kato-Weinstein
of pre-treatment with dichloroacetic acid or trichloroacetic acid in drinking
water on the pharmacokinetics of a subsequent dose in B6C3F1 mice.Chem.—Biol. Interact. 123,
Harrington-Brock, K., Doerr, C. L., and Moore, M. M. (1998). Mutagenicity of
three disinfection by-products: Di- and trichloroacetic acid, and chloral
hydrate in L5178Y/TKϩ/Ϫ-3.7. LC mouse lymphoma cells. Mutat. Res. 413,
Anna, C. H., Maronpot, R. R., Pereira, M. A., Foley, J. F., Malarkey, D. E., and
Anderson, M. W. (1994). ras proto-oncogene activation in dichloroacetic-,
Hegi, M. E., Fox, R. R., Belinsky, S. A., Devereux, T. R., and Anderson,
trichloroethylene- and tetrachloroethylene-induced liver tumors in B6C3F1
M. W. (1993). Analysis of activated protooncogenes in B6C3F1 mouse liver
mice. Carcinogenesis 15,
tumors induced by ciprofibrate, a potent peroxisome proliferators. Carcino-
Barton, H.A., Bull, R., Schultz, I., and Anderson, M. E. (1999). Dichloro-
acetate (DCA) dosimetry: Interpreting DCA-induced liver cancer dose re-sponse and the potential for DCA to contribute to trichloroethylene-induced
Helvering, L. M., Richardson, F. C., Horn, D. M., Rexroat, M. A., Engelhardt,
liver cancer. Toxicol. Lett. 106,
J. A., and Richardson, K. K. (1994). H-ras
61st codon activation in archivalproliferative hepatic lesions isolated from female B6C3F1 mice exposed to
Bull, R. J. (2000). Mode of action of liver tumor induction by trichloroethylene
the leukotriene D4-antagonist, LY171883. Carcinogenesis 15,
and its metabolites, trichloracetate and dichloroacetate. Environ. Health
(Suppl. 2), 241–259.
Kalkuhl, A., Troppmair, J., Buchmann, A., Stinchcombe, S., Buenemann,
C. L., Rapp, U. R., Kaestner, I. K., and Schwarz, M. (1998). p21 (Ras)
Bull, R. J., Sanchez, I. M., Nelson, M. A., Larson, J. L., and Lansing, A. J.
downstream effectors are increased in activity or expression in mouse liver
(1990). Liver tumor induction in B6C3F1 mice by dichloroacetate and
tumors but do not differentiate between RAS-mutated and RAS-wild-type
trichloroacetate. Toxicology 63,
lesions. Hepatology 27,
Cariello, N. F, Piegorsch, W. W., Adams, W. T., and Skopek, T. R. (1994).
Kato-Weinstein, J., Lingohr, M. K., Thrall, B. D., and Bull, R. J. (1998).
Computer program for the analysis of mutational spectra: Application to p53
Effects of dichloroacetate-treatment on carbohydrate metabolism in B6C3F1
mutations. Carcinogenesis 15,
mice. Toxicology 130,
Clewell III, H. J., Gentry, P. R., Covington, T. R., and Gearhart, J. M. (2000).
Kato-Weinstein, J., Orner, G. A., Thrall, B. D., and Bull, R. J. (2001).
Development of a physiologically based pharmacokinetic model of trichlo-
Differences in the detection of c-Jun/ubiquitin immunoreactive proteins by
roethylene and its metabolites for use in risk assessment. Environ. Health
different c-Jun antibodies. Toxicol. Methods 11
(Suppl. 2), 283–305.
Kliewer, S. A., Forman, B. M., Blumberg, B., Ong, E. S., Borgmeyer, U.,
Daniel, F. B., DeAngelo, A. B., Stober, J. A., Olson, G. R., and Page, N. P.
Mangelsdorf, D. J., Umesono, K., and Evens, R. M. (1994). Differential
(1992). Hepatocarcinogenicity of chloral hydrate, 2-chloroacetaldehyde, and
expression and activation of a family of murine peroxisome proliferator-
dichloroacetic acid in male B6C3F1 mouse. Fundam. Appl. Toxicol. 19,
activated receptors. Proc. Natl. Acad. Sci. USA 91,
Laemmili, U. K. (1970). Cleavage of structural proteins during the assembly of
DeAngelo, A. B., Daniel, F. B., McMillan, L., Wernsing, P., and Savage, R. E.,
the head of bacteriophage T4. Nature 227,
680 – 685.
Jr. (1989). Species and strain sensitivity to the induction of peroxisome
proliferation by chloroacetic acids. Toxicol. Appl. Pharmacol. 101,
Leavitt, S. A., DeAngelo, A. B., George, M. H., and Ross, J. A. (1997).
Assessment of the mutagenicity of dichloroacetic acid in lac
B6C3F1 mouse liver. Carcinogenesis 18,
DeAngelo, A. B., George, M. H., and House, D. E. (1999). Hepatocarcinoge-
nicity in the male B6C3F1 mouse following a lifetime exposure to dichlo-
Lingohr, M. K., Thrall, B. D., and Bull, R. J. (2001). Effects of dichloroacetate
roacetic acid in the drinking water: Dose–response determination and modes
(DCA) on serum insulin levels and insulin-controlled signaling proteins in
of action. J. Toxicol. Environ. Health 58,
livers of male B6C3F1 mice. Toxicol. Sci. 59,
Elcombe, C. R. (1985). Species differences in carcinogenicity and peroxisome
Maloney, E. K., and Waxman, D. J. (1999). trans-
Activation of PPAR␣ and
proliferation due to trichloroethylene: A biochemical human hazard assess-
PPAR␥ by structurally diverse environmental chemicals. Toxicol. Appl.
ment. Arch. Toxicol. Suppl. 8,
EPA (1996). U. S. Environmental Protection Agency: Proposed Guidelines for
Manjanatha, M. G., Li, E., Fu, P. P., and Heflich, R. H. (1996). H- and K-ras
carcinogen risk assessment; notice. Fed. Reg. 61,
mutational profiles in chemically induced liver tumors from B6C3F1 and
Ferreira-Gonzalez, A., DeAngelo, A. B., Nasim, S., and Garett, C. T. (1995).
CD-1 mice. J. Toxicol. Environ. Health 47,
oncogene activation during hepatocarcinogenesis in B6C3F1 mice by
Maronpot, R. R., Fox, T., Malarkey, D. E., and Goldsworthy, T. L. (1995).
dichloroacetic and trichloroacetic acids. Carcinogenesis 16,
Mutations in the ras
proto-oncogene: Clues to etiology and molecular
Fisher, J. W. (2000). Physiologically based pharmacokinetic models for tri-
pathogenesis of mouse liver tumors. Toxicology 101,
chloroethylene and its oxidative metabolites. Environ. Health Perspect.
Merdink, J. L., Gonzalez-Leon, A., Bull, R. J., and Schultz, I. R. (1998). The
(Suppl. 2), 265–273.
extent of dichloroacetate formation from trichloroethylene, chloral hydrate,
Fox, T. R., Schumann, A. M., Watanabe, P. G., Yano, B. L., Maher, V. M., and
trichloroacetate, and trichloroethanol in B6C3F1 mice. Toxicol. Sci. 45,
McCormick, J. J. (1990). Mutational analysis of the H-ras
spontaneous C57BL/6 ϫ C3H/He mouse liver tumors and tumors induced
Miller, J. H., Minard, K. M., Wind, R. A., Orner, G. A., and Bull, R. J. (2000).
CONTRIBUTION OF DCA AND TCA TO TRI–INDUCED LIVER TUMORS
MRI measurements of tumor growth induced by dichloroacetate:
roacetic acid in the liver of female B6C3F1 mice. Fundam. Appl. Toxicol.
Implications for mode of action. Toxicology 145,
Nakano, H., Hatayama, I., Satoh, K., Suzuki, S., Sato, K., and Tsuchida, S.
Reynolds, S. H., Stowers, S. J., Patterson, R. M., Maronpot, R. R., Aaronson,
(1994). c-Jun expression in single cells and preneoplastic foci induced by
S. A., and Anderson, M. W. (1987). Activated oncogenes in B6C3F1 mouse
diethylnitrosamine in B6C3F1 mice: Comparison with the expression of
liver tumors: Implications for risk assessment. Science 237,
pi-class glutathione S
-transferase. Carcinogenesis 15,
Richmond, R. E., DeAngelo, A. B., Potter, C. L., and Daniel, F. B. (1991). The
National Cancer Institute (NCI) (1976). Carcinogenesis Bioassay of Trichlo-
role of hyperplastic nodules in dichloroacetic acid-induced hepatocarcino-
roethylene (CAS No. 79-01-6).
NCI-CG-TR-2, DHEW publication no.
genesis in B6C3F1 male mice. Carcinogenesis 12,
(NIH)76-802. National Cancer Institute, Division of Cancer Cause and
Schroeder, M., DeAngelo, A. B., and Mass M. J. (1997). Dichloroacetic acid
Prevention, Carcinogenesis Program, Carcinogen Bioassay and Program
reduces Ha-ras codon 61 mutations in liver tumors from female B6C3F1
mice. Carcinogenesis 18,
National Toxicology Program (NTP) (1988). Toxicology and Carcinogenesis
Snyder, R. D., Pullman, J., Carter, J. H., Carter, H. W., and DeAngelo, A. B.
Studies of Trichloroethylene (CAS No. 79-01-6) in Four Strains of Rats
(1995). In vivo administration of dichloroacetic acid suppresses spontaneous
(ACI, August, Marshall, Osborne-Mendel) (Gavage Studies).
apoptosis in murine hepatocytes. Cancer Res. 55,
cal Report 273. NIH publication no. 88-2525. U.S. Department of Healthand Human Services, Public Health Service, National Institutes of Health,
Stanley, L. A., Blackburn, D. R., Devereaux, S., Foley, J., Lord, P. G.,
Maronpot, R. R., Orton, T. C., and Anderson, M. W. (1994). Ras
mutationsin methylclofenapate-induced B6C3F1 and C57BL/10J mouse liver tu-
National Toxicology Program (NTP) (1990). Carcinogenesis Studies of Tri-
mours. Carcinogenesis 15,
chloroethylene (Without Epichlorohydrin)(CAS No. 79-01-6) in Fischer-344/N Rats and B6C3F1 Mice (Gavage Studies).
NTP Technical Report
Stauber, A. J., and Bull, R. J. (1997). Differences in phenotype and cell
243. NIH publication no. 90-1799. U.S. Department of Health and Human
replicative behavior of hepatic tumors inducted by dichloroacetate (DCA)
Services, Public Health Service, National Institutes of Health, Research
and trichloroacetate (TCA). Toxicol. Appl. Pharmacol. 144,
Stauber, A. J., Bull, R. J., and Thrall, B. D. (1998). Dichloroacetate and
Nelson, M. A., Sanchez, I. M., Bull, R. J., and Sylvester, S. R. (1990).
trichloroacetate promote clonal expansion of anchorage-independent hepa-
Increased expression of c-myc
, and c-H-ras
in dichloroacetate- and trichlo-
tocytes in vivo and in vitro. Toxicol. Appl. Pharmacol. 150,
roacetate-induced liver tumors in B6C3F1 mice. Toxicology 64,
Watson, M. A., Devereux, T. R., Malarkey, D. E., Anderson, M. W., and
Nesnow, S., and DeAngelo, A. B. (1995). Overview on the mechanisms of
Maronpot, R. R. (1995). H-ras
oncogene mutation spectra in B6C3F1 and
carcinogenic action of dichloroacetic acid in the male B6C3F1 mouse:
C57BL/6 mouse liver tumors provide evidence for TCDD promotion of
Application to the construction of a biologically-based dose–response
spontaneous and vinyl carbamate-initiated liver cells. Carcinogenesis 16,
model. In Disinfection By-Products in Drinking Water: Critical Issues in
Health Effects Research. Summary report of a workshop organized by ILSI
Wiseman, R. W., Stowers, S. J., Miller, E. C., Anderson, M. W., and Miller,
Health and Environmental Science Insititute.
Chapel Hill, NC. Oct. 23–25,
J. A. (1986). Activating mutations of the c-Ha-ras
protooncogene in chem-
ically induced hepatomas of the male B6C3F1 mouse. Proc. Natl. Acad. Sci.
Pereira, M. A. (1996). Carcinogenic activity of dichloroacetic acid and trichlo-
International Journal of Neuropsychopharmacology (2008), 11, 985–997. Copyright f 2008 CINPhaloperidol in ﬁrst-episode schizophrenia:8-week results of a randomized controlled trialwithin the German Research Networkon SchizophreniaHans-Ju¨rgen Mo¨ller1, Michael Riedel1, Markus Ja¨ger1, Florian Wickelmaier1,Wolfgang Maier2, Kai-Uwe Ku¨hn2, Gerhard Buchkremer3, Isabella Heuser4,Joachim Kl
Working in Weather If you enjoy plein air painting, working on the spot-as I do-you're going to encounter weather of one kind or another at somepoint. Knowing how to deal with it can make the differencebetween a delightful painting excursion and a miserable failure!• Of course, painting in heat requires WATER, and not just foryour paints. Make sure you hav