Introduction
Dioxins and related compounds are widespread toxic contaminants that persist
in the environment and accumulate in the food chain. The most potent dioxin,
2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), produces a wide range of
toxic effects, many of which involve disruption of endocrine functions (1-4).
It is generally accepted that the diverse toxic effects of TCDD are mediated
by the arylhydrocarbon receptor (AhR) (5,6), a basic helix-loop-helix
transcription factor with a Per-ARNT-Sim homology domain (7-9).
Ligand-bound AhR forms a heterodimer with AhR nuclear transporter (ARNT) or
ARNT2, then binds to the xenobiotic response element (XRE; also called dioxin
response element, DRE) and alters transcription of target genes (10,11).
In addition to these genomic effects, there is evidence that TCDD binding to
the AhR also alters signal transduction by activating protein kinases (12).
Thus, the mechanisms of TCDD toxicity are complex and probably involve AhR-mediated
disruption of multiple cellular signaling processes.
TCDD disrupts a variety of physiological functions; however, the finding that
exposure to low doses of TCDD during development permanently alters reproductive
functions is of particular concern. In male Holtzman rats, perinatal exposure
to TCDD partially demasculinizes sexual behaviors (13,14) and interferes
with defeminization of both sexual behaviors (15) and gonadotropin release
patterns (13). Prenatal exposure to TCDD also demasculinizes sexual behaviors
and delays the onset of puberty in male Long Evans rats but does not appear
to block defeminization of behaviors in this rat strain (16). In female
rats, a single prenatal exposure to TCDD delays the onset of puberty, prolongs
the time required to achieve pregnancy in continuous breeding situations, and
increases the incidence of constant estrus before old age (16-18).
How developmental exposure to TCDD produces the observed effects on reproductive
functions in adulthood is not clear. However, both gonadotropin release patterns
and sexual behavioral potentials of adults are established during the critical
period of perinatal life when the neural substrates controlling these functions
undergo sexual differentiation (19,20). Sexual dimorphism of the brain
is established by exposure of male brains to testosterone produced by the developing
testes (21-24) and aromatized to estradiol (E2), the
hormone that defeminizes and masculinizes neural functions (25). Interestingly,
the behavioral deficits and altered gonadotropin release observed in males exposed
to TCDD are reminiscent of the effects caused by administration of antiaromatase
or antiestrogenic drugs (25-27). Considering that TCDD appears to
be antiestrogenic in some tissues (4), it is possible that it also interferes
with estrogen action in the brain, thereby disrupting sexual differentiation
of brain regions important for reproduction.
Support for the idea that TCDD may exert antiestrogenic actions in neural
tissue comes from our previous work showing that AhR, ARNT, and ARNT2 mRNAs
are found in several brain regions that contain estrogen receptors (28).
Most notably, we found members of the AhR pathway in the preoptic area (POA)
of the brain, a region that contains sexually dimorphic nuclei (29,30).
Importantly, neurotransmitter systems in the POA show sex differences in adulthood
as a result of perinatal steroid hormone manipulations (31,32). Furthermore,
specific subdivisions of the POA are required for estrogen-dependent luteinizing
hormone (LH) surge release (33,34) and for the expression of male sexual
behaviors (35,36). Therefore, it seems likely that developmental exposure
to TCDD may permanently demasculinize and feminize the male brain by interfering
with estrogen action in the POA.
The neural targets that mediate the organizational effects of steroids and
might also be targets of TCDD have not been clearly delineated. However,
-aminobutyric
acid (GABA)-ergic neurons throughout the adult rat brain, including regions
of the POA that control reproduction, express the AhR gene (37).
In addition, the promoter regions of both glutamic acid decarboxylase (GAD)
67 and GAD 65 genes contain multiple canonical XRE sequences (38,39).
Other lines of evidence suggest that GABAergic neurons may also be targets of
estrogen and play a role in differentiation of the POA. Neurons of the POA concentrate
tritiated E2 (40) and express estrogen receptor (ER)-
and ER-ß mRNA (41). Furthermore, GABA affects neurogenesis, neural
migration, and apoptosis (42), processes that are all influenced by steroids
and involved in creating sexually dimorphic components of the POA (43).
Taken together, this evidence supports the hypothesis that TCDD interferes with
sexual differentiation of the brain by interfering with estrogen action in GABAergic
neurons.
To test this hypothesis, we first examined the effects of TCDD on GAD 67
gene expression in POA regions of male and female offspring of Holtzman rat
dams. We treated dams with 1 µg TCDD/kg body weight on gestational day
15 (GD 15) to replicate conditions previously used to show that TCDD disrupts
masculinization and defeminization of sexual behaviors and gonadotropin release
patterns (13). We measured GAD 67 mRNA levels as an index of GABAergic
activity because in adult rats changes in GAD 67, but not in GAD 65,
gene expression are closely linked to changes in GABA release into the POA (44).
In the present studies, we used in situ hybridization histochemistry
(ISHH) so that we could focus on three subdivisions of the POA that lie in close
proximity: a) the rostral POA containing the anteroventral periventricular
nucleus (rPOA/AVPV), b) the region containing the rostralmost portion
of the medial POA (mPOA), and c) the region containing the caudalmost
mPOA. The AVPV region is critical for the induction of LH surge release by E2
(33,34), and the caudal mPOA is a site at which androgen regulates display
of male sexual behaviors (35,36,45).
We next used dual-label ISHH to verify that mRNAs encoding the AhR are present
in GABAergic neurons of the POA of developing brains as they are in adults.
We focused on the AhR gene because it mediates antiestrogenic effects
of TCDD (4,5) and because our previous work demonstrates that ARNT
and/or ARNT2 genes are expressed in all POA regions that express the
AhR gene (28). To verify that TCDD effects are not mediated by
decreases in testosterone production or interference with aromatase activity,
we used ISHH to measure sex differences in progestin receptor (PR) mRNA levels
in the mPOA. This approach took advantage of previous findings that males have
significantly higher levels of PR than females, because E2 derived
from aromatization of testosterone induces PR expression (46,47). Finally,
to confirm that all pups used in the study received similar exposures to TCDD,
we used ISHH to measure CYP1B1 mRNA levels in their livers. We used CYP1B1
as a marker of exposure because it is a target gene of the AhR (48).
Although TCDD induction of CYP1A1 gene expression is more robust than
that of CYP1B1, results of preliminary studies showed that levels of
CYP1B1 gene expression in the liver of TCDD-exposed dams are more variable
than those of CYP1A1 and also more clearly correlated with pup survival
rates (49). Thus, they appear to be a more sensitive measure of individual
responsiveness to TCDD.
Materials and Methods
Animals and Tissue Preparation
All the animals in this study were maintained in accordance with the National
Institutes of Health Guidelines for the Care and Use of Laboratory Animals
(50), and the Institutional Animal Care and Use Committee of the
University of Massachusetts approved all treatment protocols used.
For this study, 14 pregnant Holtzman Sprague-Dawley rats (Harlan Sprague-Dawley,
Madison, WI, USA) were delivered to the Animal Care Facility at the University
of Massachusetts on day 3 of gestation (GD 3). The rats were individually housed
and maintained in a temperature- and light-controlled room (14:10 light:dark
cycle; lights on at 0500 hr) with food and water available ad libitum.
Each animal was given a Keebler Golden Vanilla Wafer (Keebler Co., Elmhurst,
IL, USA) and weighed daily from GD 10 through GD 14. By GD 14, rats readily
consumed the cookies, usually within 5 min after they were presented. On GD
15, rats were weighed and randomly divided into two groups. One group (n
= 7) received vanilla wafers containing TCDD (1 µg/kg; AccuStandard, Inc.,
New Haven, CT, USA), and the control group (n = 7) received wafers treated
with dimethylsulfoxide (DMSO) vehicle (Sigma-Aldrich, St. Louis, MO, USA). Wafers
were prepared by applying 75 µL TCDD or DMSO solution and allowing them
to dry 24 hr before distribution to the rats. Each rat was closely monitored
to ensure that it consumed the entire treated cookie. Dams were weighed on GD
16, 18, 19, and 20. On GD 20, it was determined that one TCDD-treated animal
and two controls were no longer pregnant. In addition, one TCDD-treated dam
and pups died during parturition and pups of another TCDD-treated rat did not
survive longer than 24 hr. Pups from surviving litters were weighed on postnatal
day 3 (PND 3; day of birth designated PND 0) and those used in this study were
sacrificed by decapitation. Both heads and trunks were collected, rapidly frozen
on powdered dry ice, wrapped in Parafilm, and stored in sealed containers at
-80°C until cryosectioned (Leica CM3000, Nussloch, Germany).
Brains of one male pup and one female pup from each litter (five TCDD-treated
and seven vehicle-treated litters) were cryosectioned at 14 µm through
the entire POA, from the region containing the organum vasculosum of the lamina
terminalis through the region containing the medial POA. No available brain
atlas details the POA region of neonatal rats; therefore, we used an atlas of
the adult brain (51) that shows the features we observed in tissues of
PND-3 animals. The region we refer to as the rPOA/AVPV region in PND-3 animals
corresponds to plates 17 and 18 of this atlas. The rostral MPN region in our
studies corresponds to plate 19, and the region we termed caudal MPN includes
features shown in plates 20 and 21. Cryosections 14 µm thick from the trunk
region containing the liver were also obtained from each of these pups. For
both brain and liver, cryosections were collected and thaw-mounted onto gelatin-coated
slides (two sections/slide), allowed to dry on a warming tray at 42°C,
then stored at -80°C until ISHH was performed.
Single-Label ISHH
For these studies, brain sections from the POA of each of the animals in the
study were hybridized to 33P-labeled cRNA probes specific for mRNAs
encoding PR or to 35S-labeled cRNA probes for GAD 65 or GAD 67 mRNAs.
In addition, sections containing liver were hybridized to 33P-labeled
cRNA probes for CYP1B1 mRNA.
Transcription templates. The cDNA template for probes to PR
mRNA was a 550-bp BamHI-SalI cDNA fragment corresponding to bases 383-933
of the full-length clone kindly provided by O.K. Park-Sarge, University of Kentucky
(Lexington, KY, USA) (52). For antisense cRNA transcripts, the plasmid
was linearized with BamHI, and for control sense strand transcripts, the plasmid
was linearized with SalI.
The template used to prepare radiolabeled cRNA probe specific for GAD 65 was
an 824-bp XbaI-HindIII cDNA fragment corresponding to bases 944-1769 that
we subcloned from the full-length clone (38) generously provided by A.
Tobin, UCLA (Los Angeles, CA, USA). For antisense cRNA transcripts, the plasmid
was linearized with XbaI, while HindIII was used in the preparation of templates
for control sense strand transcripts.
To prepare radiolabeled cRNA probe specific for GAD 67, we used a 535-bp HindIII-SacI
cDNA fragment corresponding to bases 232-769 that we subcloned from the
full-length clone (38) provided by A. Tobin. For antisense cRNA transcripts,
the plasmid was linearized with HindIII, and for control sense strand transcripts,
the plasmid was linearized with SacI.
The cDNA transcription template for CYP1B1 mRNA was a 604-bp BamHI-EcoRV cDNA
fragment corresponding to bases 85-689 of the rat CYP1B1 cDNA prepared
using reverse transcription-polymerase chain reaction (RT-PCR). The forward
primer was 5´CATCTCAACCGCAACTCCAA3´ and the reverse primer was 5´AGCCTGATGGATGGCACTCT3´.
PCR was performed by first mixing buffer (Life Technologies, Gaithersburg, MD,
USA) with 200 pM forward and reverse primers, 200 µM dNTPs, and 1.5 mM
MgCl2 in a final volume of 200 µL. The mixture was heated to
94°C for 3 min in a thermal cycler before the addition of 10 U Taq polymerase.
Subsequent temperature cycles were 35 cycles at 94°C for 1 min, 57°C
for 1 min, 72°C for 1 min, and a final incubation at 72°C for 10 min.
The PCR-generated cDNA fragments were cloned into pCRII-TOPO (Invitrogen, Carlsbad,
CA, USA) and the identity was confirmed by sequencing. The plasmid was linearized
with BamHI for transcription of antisense probes and with EcoRV for sense strand
probes.
In vitro transcription. All cRNA probes were prepared using
in vitro transcription methods described previously (53,54), with
minor modifications. Briefly, for transcription of probes for PR, GAD 65, and
GAD 67 mRNAs, 90 pmol (9 µM final concentration) of 33P-UTP
(New England Nuclear, Boston, MA, USA) were dried down in a DNA Speed Vac (Savant,
Farmingdale, NY, USA) and 1.0 µg linearized template, 1
transcription buffer, 10 mM dithiothreitol (DTT), 20 U RNAsin (Promega, Madison,
WI, USA), 0.5 mM ATP, CTP, and GTP, 3 µM UTP, and 10 U of RNA polymerase
were added in a total volume of 10 µL. For transcription of CYP1B1 cRNA
probes, 120 pmol (12 µM final concentration) of 33P-UTP was
used and no unlabeled UTP was added to the transcription mixture. For each reaction,
the mixture was incubated for 30 min at 37°C. A second aliquot of RNA polymerase
(10 U) was added, and the mixture was incubated again for 30 min at 37°C.
The template was degraded with 2 U DNAse in the presence of 20 U RNAsin, 5 µM
Tris HCl, 1 µM MgCl2, and 0.5 µL tRNA (25 µg/µL).
The radiolabeled cRNA probes were extracted with phenol/chloroform, then precipitated
twice with NaCl and EtOH and resuspended in 100 µL of 1 mM EDTA and 10
mM Tris.
Hybridization procedures. Separate hybridization runs were conducted
for each of the probes used. In studies of PR, GAD 65, and GAD 67 mRNAs, every
fourth slide (~24 sections) from the POA of each pup was included. Similarly,
every fourth section containing liver tissue was included for each pup in a
single hybridization run, using the CYP1B1 cRNA probe. In each run, every 12th
section was hybridized to sense strand probes to verify specificity of the probe.
After warming for 10 min at room temperature, sections were processed as described
previously (55). They were first fixed with 4% formalin-phosphate-buffered
saline for 15 min, then treated with 0.25% acetic anhydride in 0.1 M triethanolamine,
0.9% NaCl (pH 8.0), dehydrated and delipidated in a series of ethanol and chloroform
rinses, and rehydrated to 95% ethanol. After the sections were dried, the cRNA
probes (~1
106
cpm) were applied to each tissue section in 25 µL of hybridization buffer.
The hybridization buffer contained 2
standard saline citrate solution (2
SSC; 1
SSC = 0.15 M
NaCl and 0.015 M sodium citrate, pH 7.2), 50% (v/v) formamide, 10% (w/v) dextran
sulfate, 250 µg/mL tRNA, 500 µg/mL sheared single-stranded salmon
sperm DNA, 1
Denhardt's
solution (0.02% Ficoll, 0.02% polyvinylpyrrolidone, and 0.02% bovine serum albumin),
and 200 mM freshly prepared DTT. Sections were covered with glass coverslips
and incubated in humid chambers overnight at 55°C.
After hybridization, coverslips were gently removed and sections washed in
two changes of 1
SSC
for 10 min each on an orbital shaker at room temperature. The slides were then
washed twice with 50% (v/v) formamide/2
SSC for 20 min at 52°C and rinsed twice in 2
SSC for 10 min each rinse. The slides were then incubated in RNAse buffer with
100 µg/mL of RNAse A (Roche Corporation, Indianapolis, IN, USA) at 37°C
for 30 min, rinsed twice in 2
SSC for 10 min each, and then incubated in 50% formamide/2
SSC (v/v) for 20 min at 52°C. Finally, slides were rinsed quickly in distilled
water, then in three separate washes of 70, 80, and 95% ethanol for 1 min each.
Dried slides were apposed to Kodak BIOMAX X-ray film (Eastman Kodak, Rochester,
NY, USA) and exposed for varying times, determined from preliminary studies
using a small number of test slides. Sets of identical 14C standards
were exposed to X-ray films in each cassette with tissue sections and were used
to verify that the films did not differ. The exposure times were 72 hr for sections
hybridized to CYP1B1 or PR probes, 24 hr for GAD 65 probes, and 48 hr for GAD
67 probes. Films were developed using a Konica SRX-101A film processor (Konica
Corporation, Tokyo, Japan).
Dual-Label ISHH
For dual-label ISHH studies co-localizing AhR and GAD mRNAs in cells of the
POA, we used a mixture of two 33P-labeled cRNA probes for AhR and
digoxigenin-labeled probes for GAD 65 and GAD 67 mRNAs. Sections from the POAs
of three vehicle-treated pups were used for this study.
Transcription templates. The templates for preparation of radiolabeled
cRNA probes for AhR mRNA were a 1.2-kb SpeI-BamHI and a 517-bp fragment of the
rat AhR cDNA that we subcloned from the full-length AhR cDNA kindly provided
by C. Bradfield, University of Wisconsin (Madison, WI, USA) (56) into
pBluescript II KS+. For antisense transcripts, the plasmid containing the 1.2-kb
fragment was linearized with SpeI and the plasmid containing the 517-bp fragment
was linearized with BamHI.
We used three separate templates to prepare digoxigenin-labeled cRNA probes
specific for GAD mRNA. GAD 65 and GAD 67 isoforms are found primarily in the
same cells, and combining the cRNA probes yields a more easily detectable signal
than one probe alone. Full-length clones described above were subcloned to prepare
several different constructs. The first was a 628-bp fragment corresponding
to bases 315-944 of the full-length GAD 65 clone. Plasmid was linearized
with XbaI for antisense transcripts. The second was a 535-bp fragment corresponding
to bases 232-767 of the full-length GAD 67 clone. This plasmid was linearized
with HindII for antisense transcripts. The third was an 824-bp fragment corresponding
to bases 944-1769 of the full-length GAD 65 clone. This plasmid was linearized
with XbaI for antisense transcripts.
In vitro transcription of digoxigenin-labeled cRNA probes. 33P-Labeled
probes for AhR were prepared as described above for preparation of CYP1B1 cRNA
probes, using 120 pmol 33P-UTP with no unlabeled UTP in the reaction.
Digoxigenin-UTP-labeled cRNA probes were transcribed using 1 µg linearized
cDNA template, 20 U T3 polymerase (Promega), transcription buffer, 250 µM
ATP, 250 µM CTP, 250 µM GTP, 50 µM UTP, 250 µM digoxigenin-UTP
(Roche Corp.), 10 µM DTT, and 1 U RNAsin. This mixture was incubated for
1 hr, then an additional aliquot of 20 U T3 polymerase was added and the mixture
incubated for 1 hr at 37°C. The reaction was brought to 100 µL with
nuclease-free water, and the DNA template was digested with DNAse I (2 U), in
the presence of 1 U RNAsin. The probe was precipitated twice with NaCl and EtOH
and resuspended in a solution of 50 µL of 1 mM EDTA and 10 µM Tris.
Dual-Label ISHH Procedure
Dual-label in situ hybridization was performed as described previously
(54,57). A mixture of radiolabeled probes (1.5
106 cpm for each probe) and digoxigenin-labeled probes (~20 ng of
each GAD probe) were applied to each tissue section in 25 µL of hybridization
buffer containing 50% formamide, 10% dextran sulfate, 1
Denhardt's solution, 2
SSC, 500 mg/mL heparin sodium salt, and 0.5 mg/mL tRNA. Sections were hybridized
under glass coverslips overnight at 55°C. After hybridization, slides were
cooled and coverslips removed in 1
SSC at room temperature, then in two 20-min 2
SSC/50% formamide washes at 52°C, followed by two 1-min rinses in 2
SSC. The sections were then incubated in RNAse solution (0.5 M NaCl; 10 mM Tris,
pH 8.0; 1.0 mM EDTA, pH 8.0; containing 100 mg/mL RNAse A) for 30 min at 37°C,
followed by two washes in 2
SSC for 10 min each at room temperature. Next, sections were incubated in a
20-min wash of 2
SSC/50%
formamide at 52°C, followed by a brief rinse in 2
SSC.
To prevent nonspecific antibody binding, we blocked tissue sections for 1
hr in 5% blocking reagent (Roche Corp.) at room temperature. After blocking,
slides were washed twice in maleate buffer (0.15 M NaCl; 0.1 M maleic acid,
pH 7.5) for 3 min each wash. Sections were then incubated in antidigoxigenin
conjugated to horseradish peroxidase (Roche Corp.; 1:200 in 2% blocking reagent)
for 48 hr at 4°C, washed 3 times in maleate buffer for 5 min, then 3 times
in TNT buffer (0.15 M Tris HCl, 0.15 M NaCl, 0.05% Triton-X) for 5 min each.
Digoxigenin signal was amplified using the NEN Renaissance Kit (New England
Nuclear, Boston, MA, USA) and visualized using the ABC Elite Kit (Vector Laboratories,
Burlingame, CA, USA) and freshly prepared 3,3´-diaminobenzidine tetrahydrochloride
solution (DAB; Sigma Chemicals, St. Louis, MO, USA). DAB solution was prepared
by mixing 10 mg DAB in 50 mL 0.1 M Tris (pH 7.6), filtering the solution through
Whatman #1 paper (Whatman International Ltd., Maidstone, England), and adding
8 mL of 30% hydrogen peroxide. The reaction was stopped in 0.1 M Tris and slides
were dipped briefly in water and 70% ethanol.
After immunocytochemical detection of digoxigenin-labeled cRNA probes, autoradiographical
detection of radiolabeled probes was carried out by dipping the sections in
NTB3 emulsion (Eastman Kodak) diluted 1:1 with deionized, distilled water. Slides
were exposed for 4-6 weeks at 4°C and then developed in Dektol and
Kodak fixer.
Data Analysis
The percentage of change in body weight between GD 15 and GD 20 in TCDD-treated
and control dams was determined and values were compared using Student's t-test.
Body weights of both male and female pups exposed to TCDD on GD 15 were compared
with those of unexposed pups using two-way analysis of variance (ANOVA) with
sex and treatment as the main effects.
The effects of TCDD on GAD, PR, and CYP1B1 gene expression
in pups were evaluated by determining relative corrected film density of the
autoradiographic signals on X-ray films as described previously (53,58).
X-ray films were placed on a light box and images were obtained with a 3CCD
Video Camera (Hitachi Denshi America, Ltd., Woodbury, NY, USA) and an AF MicroNikkor
60-mm objective lens (Nikon USA, Melville, NY, USA). Images were digitized using
BioQuant Windows image analysis software (R and M Biometrics, Nashville, TN,
USA), and a threshold was set to highlight pixels representing specific labeling.
The region of interest was then circumscribed and the average gray level of
highlighted pixels (film density) was obtained for each region. To control for
possible differences in background signal among sections, we also obtained density
readings for adjacent background regions. To determine background level, we
set the threshold to highlight all pixels in the field over a tissue region
that had no specific signal (areas containing only white matter). This value
was subtracted from the value of the specific signal to obtain corrected density
readings. All sections were examined using the same threshold settings so that
relative treatment differences could be determined. Computer-assisted image
analysis compresses film autoradiographic responses into a 255-level gray scale,
of which only 60-80 gray levels fall in the range of film density. Furthermore,
X-ray film responses to radioactivity are logarithmic, not linear; therefore,
a change in gray scale range of 20 corresponds to as much as a 5-fold change
in radioactivity in the specimen [see Vizi et al. (59) for discussion
of this issue]. Thus, values obtained using this method of analysis represent
relative changes in gene expression, not changes in absolute levels of mRNA,
which are substantially larger. However, ISHH measurement of relative differences
using film autoradiographical analysis provides the only reliable method of
detecting region-specific changes in levels of gene expression.
For statistical analyses, we calculated the mean corrected density of replicate
sections from individual animals in specific regions (6-8 sections/region/animal)
and obtained from these a grand mean for each group and each region. These data
were analyzed using two-way ANOVA, followed by Bonferroni's t-tests when
we detected a significant interaction between sex and treatment.
Results
We found no significant treatment effects on weights of dams at any time point
and no sex differences or treatment effects on body weights of pups. We found
that CYP1B1 gene expression in pup livers (see Figure 1 for an example
of autoradiographic signals) was significantly higher in TCDD-treated than in
control animals (Figure 2). We found no significant differences in the expression
of CYP1B1 in pup livers between sexes. In contrast, PR mRNA levels (see
Figure 3 for an example of autoradiographic signals) were significantly lower
in females than in males on PND 3. These differences were not altered by TCDD
exposure (Figure 4).
 |
Figure 1. Photographs of X-ray film autoradiograms
resulting from hybridizing 12-µm liver sections to 33P-labeled
antisense (A,C) or sense (B,D) strand cRNA probes for CYP1B1
mRNA. Tissues were obtained from PND-3 pups of dams treated with 1 µg
TCDD/kg body weight (A,B) or vehicle (C,D) on GD 15. |
 |
Figure 2. Effects of TCDD
on CYP1B1 mRNA levels in liver sections from PND-3 pups exposed to TCDD
(1 µg/kg po to dams; n = 5) or vehicle (n = 7) on
GD 15. Bars represent mean (±SE) of autoradiographic signals corrected
for background differences. ****Significantly different from vehicle-treated
counterparts (p < 0.0001).
|
 |
Figure 3. Representative
film autoradiogram resulting from hybridization of MPN brain sections
of untreated male (A) and female (B) PND-3 pups to 35S-labeled
cRNA probes for PR mRNA.
|
 |
Figure 4. Sexual differences
in PR mRNA levels in caudal MPN region of untreated PND-3 pups. Bars
represent mean (±SE) of autoradiographic signals corrected for
background. ****Significantly different from male counterparts (p
< 0.0001).
|
Results of dual-label ISHH studies (Figure 5) demonstrated that all GABAergic
neurons detected in the POA contained AhR mRNA, regardless of region. Despite
the uniform co-localization of GAD and AhR mRNAs, effects of TCDD on GAD
67 gene expression differed among regions and also between sexes. Figure
6 shows examples of autoradiographic ISHH signals for GAD 67 mRNA in the rPOA/AVPV
region (Figure 6A), the rostral MPN (Figure 6B), and the caudal MPN (Figure
6C). In the rPOA/AVPV region, GAD 67 mRNA levels were significantly higher in
females than in males; this difference was abolished by a TCDD-induced decrease
in levels detected only in females (Figure 7A). Although GAD 67 mRNA levels
in the rostral MPN region were also significantly higher in females than in
males, we saw no effects of TCDD (Figure 7B). Finally, in the caudal MPN (Figure
7C), we found no sex differences in GAD 67 mRNA levels in vehicle-treated pups.
However, in this region TCDD decreased levels specifically in males.
 |
Figure 5. (A) Low-magnification (10
objective) photomicrograph showing emulsion autoradiogram resulting from
hybridization of MPN tissue sections to digoxigenin-labeled cRNA probes
for GAD mRNA (GAD 65 and GAD 67; brown stain over cytoplasm) and 33P-labeled
probes for AhR mRNA (black silver grains). 3V, third ventricle. (B)
Higher magnification (40
objective) of same section shown in (A). |
 |
Figure 6. Photographs of
autoradiograms resulting from hybridization of tissue sections from
the (A) rPOA/AVPV region, (B) the rostral MPN, and (C)
the caudal MPN to 35S-labeled cRNA probes for GAD 67 mRNA.
|
 |
Figure 7. Effects of developmental
exposure to TCDD (1 µg/kg po to dams on GD 15; n = 5) or
vehicle (n = 7) on GAD 67 mRNA levels in male and female rats
examined on PND 3. Bars represent mean (±SE) autoradiographic signals
corrected for background differences. *Significantly different between
sexes (p < 0.05). **Significantly different between sexes
(p < 0.005). +Significantly different from vehicle-treated
counterpart of same sex (p < 0.05).
|
Discussion
The results of these studies show that although virtually all GABAergic neurons
in the developing POA contained AhR mRNA, TCDD altered GAD 67 gene expression
in a region-specific manner that differed between sexes. These effects do not
appear to be secondary to suppression of testosterone levels, because androgen-dependent
sex differences in PR gene expression in the MPN were not altered by TCDD. Furthermore,
considering that TCDD decreased GAD 67 levels in both males and females, and
that effects varied among regions, these changes are probably not attributable
solely either to antiestrogenic effects of TCDD or to AhR activation of xenobiotic
response elements in the promoter region of the GAD 67 gene. These findings
suggest that AhR activation in the brain may affect multiple signaling pathways,
some of which are sex- and region-specific. Although the mechanisms responsible
for disruption of GAD 67 gene expression remain to be determined, our
results clearly show that GABAergic neurons in POA regions important for gonadotropin
release and male sexual behavior are targets of TCDD during development.
The present findings are the first to show that females have higher levels
of GAD 67 mRNA levels than males in both the rPOA/AVPV and the caudal MPN regions
but not in the more rostral MPN region. These regional differences may have
important physiological implications and emphasize the importance of considering
subdivisions of the POA as functionally distinct groups of neurons. Previous
work did not detect consistent sex differences in GAD 67 gene expression
in the POA of Sprague-Dawley rats on either PND 1 or 15 using ISHH or ribonuclease
protection assays (60). In their ISHH studies, these researchers did
not examine the rPOA/AVPV region and only compared single sections at the level
of the sexually dimorphic nucleus of the POA, a region in which others also
failed to detect sex differences in GAD 67 gene expression (61).
Furthermore, in the ribonuclease protection assays, they used tissue punches
of the mPOA that included regions we analyzed separately in the present study
(subdivisions we termed rostral and caudal MPN). It seems likely that pooling
tissues could mask the region-specific sex differences we detected in GAD 67
mRNA levels in the caudal MPN region. Thus, methodological differences likely
explain apparent discrepancies between results; nevertheless, differences in
rat strain or the age at which pups were examined could also contribute to these
divergent results.
GAD 67 gene expression in the rPOA/AVPV was higher in untreated females
than in male counterparts because the AVPV plays a key role in the elicitation
of LH-releasing hormone and LH surge release by ovarian steroids in females.
For example, microimplants of antiestrogen block the surge in E2-treated
ovariectomized animals (33,34). Likewise, lesions of this region block
the ability of progesterone to elicit LH surge release in estrogen-treated rats
(62). Finally, specifically in the rPOA/AVPV, E2 elicits temporal
changes in GAD 67 mRNA levels that mark events required for the induction of
LH surge release (44). Further studies are required to determine the
mechanisms responsible for the observed sex differences and to determine whether
differences in GABAergic activity during development are responsible for the
sexually dimorphic structural features and functions of the AVPV in adulthood.
We found that TCDD exposure abolished sex differences in GAD 67 gene
expression in the rPOA/AVPV by specifically decreasing expression in females.
Previous work shows that female rats exposed to this dose of TCDD during development
show delayed onset of puberty and increased time required to achieve pregnancy
in a continuous mating situation (17,18). In concert with the present
findings, GABAergic neurons in the POA have been implicated previously in the
onset of puberty. Together with the compelling evidence that GABAergic neurons
of the AVPV play a role in E2-dependent LH surge release and ovulation,
it is reasonable to speculate that the underlying cause of disruptions in female
reproductive functions is a TCDD-induced suppression of GABA synthesis during
development. Nonetheless, TCDD exposure did not affect rPOA/AVPV levels of GAD
67 mRNA in males, despite previous evidence that exposure to a maternal dose
of 1 µg/kg TCDD on GD 15 feminizes gonadotropin release patterns in Holtzman
male rats (13).
Although we found no sex differences in GAD 67 gene expression in the
caudal MPN, TCDD decreased expression in this region specifically in males.
This finding is intriguing in view of previous work showing that the caudal
MPN is important for the expression of male sexual behaviors (35,36)
that are altered by developmental exposure to TCDD (13). Unlike other
regions of the POA, the caudal MPN of males has approximately 5 times as many
androgen receptors as does that of females (45) and therefore may be
the primary target for androgen action during sexual differentiation of the
substrates important for masculine behaviors in adulthood. Whether TCDD-induced
reduction in the activity of GABAergic neurons in the caudal MPN could interfere
with behavioral masculinization is not clear, especially considering that we
found no sex differences in GAD 67 gene expression in untreated animals.
However, previous work shows that perinatal treatment with the GABAA
receptor antagonist picrotoxin permanently decreases male sexual behavior in
adulthood (63). In light of this information and our finding that nearly
all AhR mRNA signal is accounted for by co-localization with GAD mRNA, TCDD-induced
decreases in GAD 67 gene expression in the caudal MPN of males could
have permanent consequences, including deficits in masculine sexual behaviors.
The mechanisms underlying the variable effects of TCDD on GAD 67 gene
expression in males and females will require further research, but our present
findings provide important new insights. First, we found that sex differences
in PR mRNA levels in the MPN were not affected by TCDD administration. Because
this sex difference depends on androgen action (46,47), presumably through
aromatization to E2, it seems unlikely that TCDD disrupted GAD
67 gene expression by interfering with testosterone production in males.
Second, we found that TCDD decreased GAD 67 mRNA levels, but it did so in both
males (caudal MPN region) and females (AVPV region). Thus, effects of TCDD are
probably not attributable to interference with estrogen action in the developing
brain, because only males are exposed to relatively high levels of E2
through local aromatization of circulating androgens. Finally, TCDD did not
have the same effect on GAD 67 gene expression in all regions, even though
we found no regional differences in the percentage of co-localization of GAD
and AhR mRNAs. This finding suggests that effects of TCDD do not result solely
from a genomic action of the AhR on GAD 67 gene expression. On the basis
of this evidence, it seems likely that TCDD effects on GAD 67 gene expression
may involve a complex interaction among genomic effects of AhR activation, disruption
of sex-specific genomic effects of steroids, and alterations in region-specific
signal transduction pathways.
In summary, we found that GABAergic neurons in the POA express the AhR
gene and that TCDD exposure during development alters GAD 67 gene expression
in a region- and sex-specific manner. Of particular importance is the finding
of disruptive effects of TCDD in the rPOA/AVPV and caudal MPN. These regions
play a key role in female fertility and regulation of male sexual behaviors,
functions that previous work found to be disrupted when developing animals are
exposed to the same dose of TCDD and the same time of administration used in
the present studies. Although the mechanisms underlying TCDD disruptions of
GAD 67 gene expression are not readily apparent, they are likely to involve
complex interactions of genomic and nongenomic AhR and ER pathways in GABA neurons,
as well as modulation of region-specific afferent signals to GABAergic neurons.
References and Notes
1. Birnbaum LS. The mechanism of dioxin toxicity: relationship
to risk assessment. Environ Health Perspect 102(suppl 9):157-167 (1994).
2. DeVito MJ, Birnbaum LS. Toxicology of dioxins and related
chemicals. In: Dioxins and Health (Schecter A, ed). New York:Plenum Press, 1994;139-162.
3. Bertazzi PA, Bernucci I, Brambilla G, Consonni D, Pesatori
AC. The Seveso studies on early and long-term effects of dioxin exposure: a
review. Environ Health Perspect 106(suppl 2):625-633 (1998).
4. Safe S, Wang F, Porter W, Duan R, McDougal A. Ah receptor
agonists as endocrine disruptors: antiestrogenic activity and mechanisms. Toxicol
Lett 102-103:343-347 (1998).
5. Poland A, Knutson JC. 2,3,7,8-Tetrachlorodibenzo-p-dioxin
and related aromatic hydrocarbons: examination of the mechanisms of toxicity.
Annu Rev Pharmacol Toxicol 22:517-554 (1982).
6. Safe SH. Comparative toxicology and mechanism of action
of polychlorinated dibenzo-p-dioxins and dibenzofurans. Annu Rev Pharmacol
Toxicol 26:371-399 (1986).
7. Burbach KM, Poland A, Bradfield CA. Cloning of the
Ah-receptor cDNA reveals a distinctive ligand-activated transcription factor.
Proc Natl Acad Sci U S A 89:8185-8189 (1992).
8. Ema M, Sogawa K, Watanabe Y, Chujoh Y, Matsushita N,
Gotoh O, Funae Y, Fujii-Kuriyama Y. cDNA cloning and structure of mouse putative
Ah receptor. Biochem Biophys Res Commun 184:246-253 (1992).
9. Dolwick KM, Schmidt JV, Carver LA, Swanson HI, Bradfield
CA. Cloning and expression of a human Ah receptor cDNA. Mol Pharmacol 44:911-917
(1993).
10. Whitlock JP Jr. Induction of cytochrome P4501A1. Annu
Rev Pharmacol Toxicol 39:103-125 (1999).
11. Gu Y-Z, Hogenesch JB, Bradfield CA. The PAS superfamily:
sensors of environmental and developmental signals. Annu Rev Pharmacol Toxicol
40:519-561 (2000).
12. Matsumura F. How important is the protein phosphorylation
pathway in the toxic expression of dioxin-type chemicals? Biochem Pharmacol
48(2):215-224 (1994).
13. Mably TA, Moore RW, Goy RW, Petersen RE. In utero
and lactational exposure of male rats to 2,3,7,8-tetrachlorodibenzo-p-dioxin.
2: Effects on sexual behavior and the regulation of luteinizing hormone secretion
in adulthood. Toxicol Appl Pharmacol 114:108-117 (1992).
14. Bjerke DL, Peterson RE. Reproductive toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin
in male rats: different effects of in utero versus lactational exposure.
Toxicol Appl Pharmacol 127:241-249 (1994).
15. Bjerke DL, Brown TJ, MacLusky NJ, Hochberg RB, Peterson
RE. Partial demasculinization and feminization of sex behavior in male rats
by in utero and lactational exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin
is not associated with alterations in estrogen receptor binding or volumes of
sexually differentiated brain nuclei. Toxicol Appl Pharmacol 127:258-267
(1994).
16. Gray LE Jr, Ostby J, Wolf C, Miller DB, Kelce WR,
Gordon CJ, Birnbaum L. Functional developmental toxicity of low doses of 2,3,7,8-tetrachlorodibenzo-p-dioxin
and a dioxin-like PCB (169) in Long Evans rats and Syrian hamsters: reproductive,
behavioral and thermoregulatory alterations. Organohalogen Compounds 25: 33-38
(1995).
17. Gray LE Jr, Ostby JS. In utero 2,3,7,8-tetrachlorodibenzo-p-dioxin
(TCDD) alters reproductive morphology and function in female rat offspring.
Toxicol Appl Pharmacol 133:285-294 (1995).
18. Gray LE Jr, Wolf C, Mann P, Ostby JS. In utero
exposure to low doses of 2,3,7,8-tetrachlorodibenzo-p-dioxin alters reproductive
development of female Long Evans hooded rat offspring. Toxicol Appl Pharmacol
146:237-244 (1997).
19. Barraclough CA. Modifications in the CNS regulation
of reproduction after exposure of prepubertal rats to steroid hormones. Recent
Prog Horm Res 22:503-539 (1966).
20. Flerko B, Petrusz P, Tima L. On the mechanisms of
sexual differentiation of the hypothalamus. Factors influencing the "critical
period" of the rat. Acta Biol 18(1):27-36 (1967).
21. Barraclough CA, Turgeon JL. Ontogeny of development
of the hypothalamic regulation of gonadotropin secretion: effects of perinatal
sex steroid exposure. Symp Soc Dev Biol 33:255-273 (1975).
22. MacLusky NJ, Naftolin F. Sexual differentiation of
the central nervous system. Science 211:1294-1303 (1981).
23. Jacobson C, Davis F, Gorski R. Formation of sexually
dimorphic nucleus of the preoptic area: neuronal growth, migration, and changes
in cell number. Dev Brain Res 21:7-18 (1985).
24. vom Saal FS, Montano MM, Wang MS, Sexual differentiation
in mammals. In Chemically Induced Alterations in Sexual and Functional Development:
The Wildlife-Human Connection (Colborn T, Clement C, eds). Princeton, NJ:Princeton
Scientific Publications, 1992;17-83.
25. McEwen BS, Lieberburg I, Chaptal C, Krey L. Aromatization:
important for sexual differentiation of neonatal rat brain. Horm Behav
9:249-263 (1977).
26. McDonald PG, Doughty C. Androgen sterilization in
the neonatal female rat and its inhibition by an estrogen antagonist. Neuroendocrinology
13:182-188 (1973).
27. MacLusky NJ, Philip A, Hurlburt C, Naftolin F. Estrogen
formation in the developing rat brain: sex differences in aromatase activity
during early post-natal life. Psychoneuroendocrinology 10(3):355-361 (1985).
28. Petersen SL, Curran MA, Marconi SA, Carpenter CD,
Lubbers LS, McAbee MD. Distribution of mRNAs encoding the arylhydrocarbon receptor
(AhR), arylhydrocarbon receptor nuclear translocator (ARNT) and ARNT2 in the
rat brain and brain stem. J Comp Neurol 427:428-439 (2000).
29. Gorski RA, Gordon JH, Shryne JE, Southam AE. Evidence
for a morphological sex difference within the medial preoptic area of the rat
brain. Brain Res 148:333-346 (1978).
30. Simerly RB, Swanson LW, Gorski RA. The distribution
of monoaminergic cells and fibers in a periventricular preoptic nucleus involved
in the control of gonadotropin release: immunohistochemical evidence for a dopaminergic
sexual dimorphism. Brain Res 330(1):55-64 (1985).
31. Simerly RB, Swanson LW, Gorski RA. Reversal of the
sexually dimorphic distribution of serotonin-immunoreactive fibers in the medial
preoptic nucleus by treatment with perinatal androgen. Brain Res 340(1):91-98
(1985).
32. Simerly RB, Swanson LW, Handa RJ, Gorski RA. Influence
of perinatal androgen on the sexually dimorphic distribution of tyrosine hydroxylase-immunoreactive
cells and fibers in the anteroventral periventricular nucleus of the rat. Neuroendocrinology
40(6):501-510 (1985).
33. Petersen SL, Barraclough CA. Suppression of spontaneous
LH surges in estrogen-treated ovariectomized rats by microimplants of antiestrogen
into the preoptic brain. Brain Res 484:279-289 (1989).
34. Petersen SL, Cheuk C, Hartman RD, Barraclough CA.
Medial preoptic microimplants of the antiestrogen, keoxifene, affect luteinizing
hormone-releasing hormone mRNA levels, median eminence luteinizing hormone-releasing
hormone concentrations and luteinizing hormone release in ovariectomized, estrogen-treated
rats. J Neuroendocrinology 1:279-289 (1989).
35. Gray P, Brooks PJ. The effect of lesion location within
the medial preoptic-anterior hypothalamic continuum on maternal and male sexual
behaviors in female rats. Behav Neurosci 98:703-711 (1984).
36. Sachs BD, Meisel RL. The physiology of male sexual
behavior. In: The Physiology of Reproduction (Knobil E, Neill JD, eds).
New York:Raven Press, 1988;1393-1485.
37. Laroche JaSP. Unpublished data.
38. Erlander MG, Tillakaratne NJ, Feldblum S, Patel N,
Tobin AJ. Two genes encode distinct glutamate decarboxylases. Neuron 7(1):91-100
(1991).
39. Pinal CS, Cortessis V, Tobin AJ. Multiple elements
regulate GAD65 transcription. Dev Neurosci 19(6):465-475 (1997).
40. Flugge G, Oertel WH, Wuttke W. Evidence for estrogen-receptive
GABAergic neurones in the preoptic/anterior hypothalamic area of the rat brain.
Neuroendocrinology 43:1-5 (1985).
41. McIntyre T, Hrabovszky E, Petersen SL. Unpublished
data.
42. Varju P, Katarova Z, Madarasz E, Szabo G. GABA signalling
during development: new data and old questions. Cell Tissue Res 305:239-246
(2001).
43. Tobet SA, Hanna IK. Ontogeny of sex differences in
the mammalian hypothalamus and preoptic area. Cell Mol Neurobiol 17(6):565-601
(1997).
44. Curran-Rauhut MA, Petersen SL. Regulation of glutamic
acid decarboxylase 65 and 67 gene expression by ovarian steroids: identification
of two functionally distinct populations of GABA neurons in the preoptic area.
J Neuroendocrinol 14(4):310-317 (2002).
45. Lisciotto CA, Morrell JI. Sex differences in the distribution
and projections of testosterone target neurons in the medial preoptic area and
the bed nucleus of the stria terminalis of rats. Horm Behav 28:492-502
(1994).
46. Wagner CK, Nakayama AY, DeVries GJ. Role of testosterone,
estrogen and progesterone in the sexual differentiation of the rat medial preoptic
nucleus. Soc Neurosci Abstr 24:550 (1998).
47. Wagner CK, Nakayama AY, De Vries GJ. Potential role
of maternal progesterone in the sexual differentiation of the brain. Endocrinology
139(8):3658-3661 (1998).
48. Sutter TR, Tang YM, Hayes CL, Wo YY, Jabs EW, Li X,
Yin H, Cody CW, Greenlee WF. Complete cDNA sequence of a human dioxin-inducible
mRNA identifies a new gene subfamily of cytochrome P450 that maps to chromosome
2. J Biol Chem 269(18):13092-13099 (1994).
49. Hays L, Petersen SL. Unpublished observations.
50. Guide for the Care and Use of Laboratory Animals.
Washington, DC:National Academy Press, 1996.
51. Swanson LW. Brain Maps: Structure of the Rat Brain,
2nd ed. Amsterdam:Elsevier, 1998;267.
52. Park O-K, Mayo KE. Transient expression of progesterone
receptor messenger RNA in ovarian granulosa cells after the preovulatory luteinizing
hormone surge. Mol Endocrinol 5:967-978 (1991).
53. Petersen SL, Keller ML, Carder SA, McCrone S. Differential
effects of estrogen and progesterone on levels of POMC mRNA levels in the arcuate
nucleus: relationship to the timing of LH surge release. J Neuroendocrinol 5:643-648
(1993).
54. Petersen SL, McCrone S. Use of dual-label in situ
hybridization histochemistry to determine the receptor complement of specific
neurons. In: In Situ Hybridization Applications to Neurobiology (Valentino
KL, Eberwine JJ, Barchas JD, eds). New York:Oxford University Press, 1993;78.
55. Petersen SL, Gardner E, Adelman J, McCrone S. Examination
of steroid-induced changes in LHRH gene transcription using 33P-
and 35S-labeled probes specific for intron 2. Endocrinology 137:234-239
(1996).
56. Carver LA, Hogenesch JB, Bradfield CA. Tissue specific
expression of the rat Ah-receptor and ARNT mRNAs. Nucleic Acids Res 22(15):3038-3044
(1994).
57. Petersen SL, McCrone S, Coy D, Adelman JP, Mahan LC.
GABAA receptor subunit mRNAs in cells of the preoptic area: colocalization
with LHRH mRNA using dual-label in situ hybridization histochemistry.
Endocr J 1:29-34 (1993).
58. Petersen SL, LaFlamme K. Progesterone increases levels
of mu opioid receptor mRNA in the preoptic region and arcuate nucleus of ovariectomized,
estradiol-treated female rats. Mol Brain Res 52:32-37 (1997).
59. Vizi S, Palfi A, Hatvani L, Gulya K. Methods for quantification
of in situ hybridization signals obtained by film autoradiography and
phosphorimaging applied for estimation of regional levels of calmodulin mRNA
classes in the rat brain. Brain Res Protocols 8:32-44 (2001).
60. Davis AM, Grattan DR, Selmanoff M, McCarthy MM. Sex
differences in glutamic acid decarboxylase mRNA in neonatal rat brain: implications
for sexual differentiation. Horm Behav 30:538-552 (1996).
61. Gao B, Moore RY. The sexually dimorphic nucleus of
the hypothalamus contains GABA neurons in rat and man. Brain Res 742:163-171
(1996).
62. Wiegand SJ, Terasawa E. Discrete lesions reveal functional
heterogeneity of suprachiasmatic structures in regulation of gonadotropin secretion
in the female rat. Neuroendocrinology 34:395-404 (1982).
63. Silva MR, Oliveira CA, Felicio LF, Nasello AG, Bernardi
MM. Perinatal treatment with picrotoxin induces sexual, behavioral, and neuroendocrine
changes in male rats. Pharmacol Biochem Behav 60(1):203-208 (1998).
Last Updated: May 27, 2002