当前位置: 首页 > 期刊 > 《内分泌学杂志》 > 2006年第2期 > 正文
编号:11416451
Polychlorinated Biphenyls Exert Selective Effects on Cellular Composition of White Matter in a Manner Inconsistent with Thyroid Ho
http://www.100md.com 《内分泌学杂志》
     Molecular and Cellular Biology Program (D.S.S., R.T.Z.) and Department of Biology (R.B., R.T.Z.), University of Massachusetts-Amherst, Morrill Science Center, Amherst, Massachusetts 01003

    Abstract

    Developmental exposure to polychlorinated biphenyls (PCBs) is associated with a variety of cognitive deficits in humans, and recent evidence implicates white matter development as a potential target of PCBs. Because PCBs are suspected of interfering with thyroid hormone (TH) signaling in the developing brain, and because TH is important in oligodendrocyte development, we tested the hypothesis that PCB exposure affects the development of white matter tracts by disrupting TH signaling. Pregnant Sprague Dawley rats were exposed to the PCB mixture Aroclor 1254 (5 mg/kg), with or without cotreatment of goitrogens from gestational d 7 until postnatal d 15. Treatment effects on white matter development were determined by separately measuring the cellular density and proportion of myelin-associated glycoprotein (MAG)-positive, O4-positive, and glial fibrillary acidic protein (GFAP)-positive cells in the genu of the corpus callosum (CC) and in the anterior commissure (AC). Hypothyroidism decreased the total cell density of the CC and AC as measured by 4',6-diamidino-2-phenylindole dihydrochloride (DAPI) staining and produced a disproportionate decrease in MAG-positive oligodendrocyte density with a simultaneous increase in GFAP-positive astrocyte density. These data indicate that hypothyroidism reduces cellular density of CC and AC and fosters astrocyte development at the expense of oligodendrocyte density. In contrast, PCB exposure significantly reduced total cell density but did not disproportionately alter MAG-positive oligodendrocyte density or change the ratio of MAG-positive oligodendrocytes to GFAP-positive astrocytes. Thus, PCB exposure mimicked some, but not all, of the effects of hypothyroidism on white matter composition.

    Introduction

    POLYCHLORINATED BIPHENYLS (PCBs) are ubiquitous environmental contaminants that accumulate in animal tissues because of their lipophilic nature and chemical stability (1). Developmental exposure to PCBs in humans is associated with a variety of neuropsychological deficits such as lower IQ scores, motor impairments, deficits in visual recognition memory, and attention deficits (reviewed in Ref.2). Recently, Stewart et al. (3) reported that the size of the corpus callosum (CC) in children is a strong predictor of the strength of association between PCB body burden and response inhibition. Although the mechanistic relationship between these variables is unknown, PCBs are known to interfere with thyroid function in animals (4, 5), and thyroid hormone (TH) is known to be important in the development of white matter tracts in animals (6, 7, 8) and in humans (9, 10). Thus, it is possible that PCB exposure in humans causes specific cognitive deficits in part by interfering with TH action on the development of major white matter tracts such as the CC.

    Considering this, we sought to test the hypothesis that PCB exposure selectively affects white matter tract development by interfering with TH action, focusing on the anterior commissure (AC) and CC. This hypothesis is based on the observation that TH controls several aspects of white matter tract development, including oligodendrocyte precursor cell proliferation and survival (reviewed in Ref.11), oligodendrocyte number (6), and oligodendrocyte differentiation (12, 13, 14). Moreover, a specific PCB congener, PCB-118, can induce a dose-dependent increase in the number of oligodendrocytes in vitro, an effect that can be blocked with the TH receptor (TR) antagonist NH-3 (15). Thus, TH is important for white matter tract development, and PCB exposure may interfere with TH action in this tissue.

    To test this hypothesis, we focused our experiments on postnatal day 15, a time when both myelination and TH levels are at their peak during development (16, 17), and effects of hypothyroidism on white matter development have been documented (6, 7, 18, 19). We began by evaluating the effect of developmental exposure to the commercial PCB mixture Aroclor 1254 on myelin-associated glycoprotein (MAG) expression in the CC and AC of male pups and comparing the observed effects with those of pups in which thyroid function was experimentally reduced. We further characterized treatment effects on oligodendrocytes by evaluating density and proportion of MAG-positive and O4-positive oligodendrocytes within these white matter tracts and made comparisons with effects of hypothyroidism. Finally, because oligodendrocytes and astrocytes can be derived from a common precursor, we evaluated the effects of PCB exposure and hypothyroidism on glial fibrillary acidic protein (GFAP)-positive astrocyte density and proportion in these white matter tracts. We found that developmental PCB exposure significantly reduces cellular density and density of MAG-positive oligodendrocytes in the AC and CC but does not affect the proportion of MAG-positive oligodendrocytes, GFAP-positive astrocytes, or the density of O4-positive oligodendrocytes within these white matter tracts. These effects of PCB exposure are only partially consistent with the effects of hypothyroidism. Moreover, our findings are consistent with the hypothesis that TH controls the balance of MAG-positive oligodendrocytes to GFAP-astrocytes in these white matter tracts, perhaps by acting on a common precursor.

    Materials and Methods

    Animals

    All animal procedures were performed in accordance with the National Institutes of Health Guide for the Care and Use of Laboratory Animals (20) and were approved by the University of Massachusetts-Amherst Institutional Animal Care and Use Committee. Timed pregnant Sprague Dawley rats (Zivic Miller Inc., Pittsburgh, PA) arrived at our animal facility 2 d after insemination [gestational d 2 (G2)]. Upon arrival, animals were individually housed in plastic cages in a 12-h light, 12-h dark cycle (lights on 0600–1800 h) with food and water provided ad libitum.

    Experimental treatment

    Dams were randomly assigned to one of four treatment groups (n = 7–8 per group): control, hypothyroid (HTx), PCB-treated (PCB), or HTx plus PCB (HTx+PCB). On G3, all animals began receiving a single untreated wafer at 1600–1800 h daily. This initial exposure to untreated wafers trains the animals to consume them completely before PCB administration begins. Beginning on G7, wafers (Keebler Golden Vanilla Wafer-Mini, Kellogg Co., Battle Creek, MI) were dosed with Aroclor 1254 (lot no. A8120256; AccuStandard Inc., New Haven, CT) dissolved in methanol at a concentration of 5 μg/μl. To prepare the wafers daily, a volume equal to 1 μl/g body weight was pipetted onto the wafer each morning and allowed to dry in a fume hood throughout the day. Wafers for animals in the control and HTx groups were dosed with methanol alone. Maternal PCB exposure continued from G7 to postnatal day 15 (P15). Dams in the HTx and HTx+PCB groups were treated with a combination of methimazole (MMI) and potassium perchlorate in the drinking water. This treatment was initiated incrementally as follows: from G7–G9, 0.1% MMI plus 0.5% perchlorate; from G9–G11, 0.1% MMI plus 0.1% perchlorate; and from G11 to P15, 0.02% MMI plus 0.5% perchlorate. On P15, one male pup from each litter was weighed and killed by decapitation after CO2 exposure. Trunk blood was collected to measure total serum T4 levels. The brain was removed, immediately frozen on pulverized dry ice, labeled, and stored at –80 C until sectioning in a cryostat.

    RIA

    Total T4 was measured in 5 μl of rat serum using a barbital buffer system as previously described (21). Each assay tube contained 100 μl barbital buffer [0.11 M barbital (pH 8.6), 0.1% (wt/vol) 8-anilino-1-napthalene-sulfonic acid ammonium salt, 15% bovine -globulin Cohn fraction II, and 0.1% gelatin], 100 μl anti-T4 (rabbit; Sigma Chemical Co., St. Louis, MO) diluted to a final concentration of 1:30,000, and 100 μl 125I-labeled T4 (15,000 cpm; Perkin-Elmer/NEN Life Science Products, Boston, MA). Standards were prepared from T4 (Sigma) measured using a Cahn electrobalance; standards were run in triplicate, whereas samples were run in duplicate. Standards were calibrated to measure serum T4 levels from 0.4–25.6 μg/dl. Tubes were incubated at 37 C for 30 min and then chilled on wet ice for 30 min. Bound counts were precipitated by adding 300 μl ice-cold polyethylene glycol 8000 (20% wt/vol; Sigma). Tubes were centrifuged at 1800 x g for 20 min at 4 C, and the supernatant was aspirated and the pellet counted in a -counter (Packard Cobra II). Pups with T4 levels lower than the lowest standard (0.4 μg/dl) were considered to have undetectable T4 levels and not included in statistical analysis. The assay was run at 40–50% binding; nonspecific binding was generally less than 8%. The assay was validated for rat serum by demonstrating parallelism between the standard curve and a dilution series of rat serum.

    Experimental strategy

    We initially examined the effect of PCB treatment and hypothyroidism on MAG expression because previous studies have shown that MAG mRNA levels are influenced by hypothyroidism (19, 22). Thus, if PCB treatment affects oligodendrocyte development by producing a relative state of hypothyroidism, we predicted that PCB exposure would decrease MAG expression as evaluated by in situ hybridization. However, MAG is also a marker of differentiated oligodendrocytes (23), and the mRNA is localized to the perinuclear region of the soma (24). Therefore, we were able to simultaneously use MAG as a marker of terminally differentiated oligodendrocytes for analysis of oligodendrocyte cell number and density. However, this creates a potential confound in that the expected reduction in cellular levels of MAG mRNA may simultaneously be interpreted as a reduction in number or density of oligodendrocytes. Thus, we also evaluated the number of cells expressing the early marker of oligodendrocyte differentiation, O4. Moreover, because oligodendrocytes and astrocytes can be derived from a common precursor (12, 25), we also evaluated treatment effects on similar characteristics of terminally differentiated astrocytes using GFAP as a marker.

    In situ hybridization

    Tissue.

    Frozen brain tissue was sectioned in a coronal plane at 12 μm using a cryostat (Reichert-JungFrigocut 2800N; Leica Corp., Deerfield, IL). These sections were taken approximately 0.48–1.0 mm caudal to Bregma (corresponding to Figs. 14–16 in Ref.26). Sections were thaw-mounted onto twice-gelatin-coated slides and stored at –80 C until hybridization.

    Oligonucleotide and cRNA probe preparation.

    The probe used for detection of oligodendrocytes was generated by 3'-end labeling a 48-base oligonucleotide (IDT, Coralville, IA) directed against exon 8 of the MAG mRNA (5'-CAG GAT GGA GAC TGT CTC CCC CTC TAC CGC CAC CAC CGT CCC ATT CAC-3'; bp1116–1163). Terminal deoxynucleotidyl transferase (TdT; Roche Applied Sciences, Indianapolis, IN) was used according to the manufacturer’s directions with the following exception: the TdT labeling reaction contained a 10-fold molar excess of [35S]dATP to 3'-ends to create an average tail length of 10 radiolabeled nucleotides per probe. Oligonucleotide probe preparation and specificity have previously been reported (24). For detection of astrocytes, a [33P]cRNA probe for GFAP was generated in vitro from a cDNA fragment (bp 1365–2290, accession no. NM017009). The cDNA fragment was cloned into pCRII-TOPO using TOPO TA Cloning (Invitrogen, Carlsbad, CA) after RT-PCR using P15 cortical RNA as a template for the RT reaction and amplified using the following PCR primers: forward, 5'-AGCTCCCTCCTCAGATAGTCTTGT-3', and reverse, 5'-TGTGACTCTTCCAGGTTGAGAAGC-3'. The authenticity of the PCR-generated fragment was confirmed by sequence analysis. To generate an antisense cRNA probe, pCRII-TOPO-GFAP was linearized with EcoRV and transcribed in the presence of T7 RNA polymerase. To generate a sense cRNA probe, the plasmid was linearized with HindIII and transcribed in the presence of SP6 RNA polymerase. The DNA templates were then removed with deoxyribonuclease digestion, and then the probes were purified by phenol/chloroform extraction followed by two ethanol precipitations. To compensate for differences in signal strength of MAG and GFAP mRNAs, different isotopic nucleotides were used for detection of mRNAs, allowing similar exposure times against x-ray film and photographic emulsion.

    Pre- and posthybridization treatments.

    Prehybridization treatments were performed as previously described (27). Briefly, for each probe, two slides per animal were thawed and immersed in 4% formaldehyde/PBS for 30 min, rinsed in PBS, acetylated in 0.25% acetic anhydride/0.1 M triethanolamine/0.9% NaCl (pH 8.0) for 10 min, and rinsed in 2x standard saline citrate (SSC) (1x SSC contains 0.15 M sodium chloride and 0.015 M sodium citrate, pH 7.4). Slides were then dehydrated through a series of graded alcohols, delipidated in chloroform, rehydrated to 95% ethanol, and dried at room temperature. Fifty microliters of hybridization buffer containing 2 x 106 cpm were applied to each slide, coverslipped, and incubated at 37 C (oligonucleotide) or 52 C (cRNA) for 16 h. Hybridization buffer contained 50% ultrapure formamide (Fisher Scientific, Fairlawn, NJ), 4x SSC (oligonucleotide) or 2x SSC (cRNA), 250 μg/ml tRNA, 1x Denhardt’s, 10% (wt/vol) dextran sulfate, and 500 mM DTT. After the hybridization, coverslips were removed in 1x SSC and washed four times in 1x SSC for 15 min each at room temperature. For the oligonucleotide probe, sections were then washed four times with 2x SSC/50% formamide at 40 C for 15 min each, rinsed two times in 1x SSC for 30 min each, equilibrated to 70% ethanol, and then air dried. Posthybridization for the cRNA-GFAP probe was as follows: sections were washed two times with 2x SSC/50% formamide at 52 C for 15 min each and then rinsed two times in 1x SSC for 10 min each, incubated at 37 C for 30 min in RNase wash buffer (0.5 M NaCl, 0.01 M Tris, 1 mM EDTA) containing 100 μg/ml RNase A, rinsed two times in 2x SSC for 10 min each, followed by two more washes with 2x SSC/50% formamide at 52 C for 15 min each, two more rinses in 1x SSC for 10 min each, equilibrated to 70% ethanol, and then air dried.

    Film autoradiography and signal quantification

    After in situ hybridization, slides were arranged in an x-ray cassette and exposed to BioMax film (Eastman Kodak, Rochester, NY) for 24 h. To control for overexposure, 14C-labeled standards (American Radiolabeled Chemicals Inc., St. Louis, MO) were included in the cassette and simultaneously exposed to the film. Radiographic signal was developed using an automated film processor (Konica SRX-101A; Alliance Imaging Inc., Warham, MA) and analyzed as follows. A magnified image was captured using a Nikon Macro lens mounted on a Dage-MTI-72 camera (Dage-MTI, Michigan City, IN) interfaced to a Macintosh computer operating NIH Image V 1.61 (W. Rashband, National Institute of Mental Health, Bethesda, MD) to control a Scion AG-5 capture board. Density values corresponding to the signal in the AC or CC were generated by encircling the entire AC unilaterally or by encircling the CC at the midline between the lateral margins of the lateral ventricles using the drawing tool in NIH Image (Fig. 1). The resulting density values from each brain region were averaged across all four sections for each animal and statistical analysis performed.

    Single-cell mRNA measurements

    After exposure to film, slides were removed from the x-ray cassette and dipped in NTB-2 photographic emulsion (Eastman Kodak), air dried, boxed in a light-tight container, and stored at 4 C for 72 h. Slides were then developed in Dektol (diluted 1:1 with water) for 2 min, rinsed in water, fixed in Kodak fixer for 5 min, and then rinsed in running cold water for 5 min, counterstained with 0.5% methyl green, and coverslipped in Permount (Sigma-Aldrich, St. Louis, MO). Single-cell levels of MAG mRNA were determined as previously described by Zoeller et al. (28). Briefly, all slides were coded, randomized, and analyzed blindly. Images of the AC and CC were magnified x200 with a Nikon ES-600 microscope equipped with a CCD camera (Dage-MTI) interfaced with a Macintosh G4 computer through an AG-5 frame grabber using NIH Image version 1.61. Images were captured using dark-field optics, and black and white polarization was electronically inverted. Using NIH Image, a threshold was set such that only silver grains were detected, and the area of silver grains associated with each of 10 single cells per brain region was determined by placing a fixed circle with an area of 0.002 mm2 over each cell. The area over each of the 40 cells that was covered by silver grains in the AC and CC of each brain was used an index of single-cell mRNA levels (i.e. proportional to the amount of radioactive probe sequestered in the cell) (29). This method of measuring silver grain area has been demonstrated to closely resemble the results obtained from directly counting silver grains (30). After all brain sections were analyzed, the individual measurements from each slide were averaged for each animal and decoded, and statistical analysis was performed.

    Cell density measurements

    To determine the numerical density of oligodendrocytes or astrocytes present in the AC and CC, methyl green-stained nuclei associated with MAG-positive or GFAP-positive silver grain clusters were counted using a Nikon ES-600 microscope fitted with a 5-mm x 5-mm ocular reticule. The number of MAG-positive nuclei and GFAP-positive nuclei in the CC was counted by randomly placing a reticule adjacent to the midline under x400 magnification. At this magnification, the reticule represents 0.0144 mm2. The number of MAG-positive nuclei in the AC was determined by counting all MAG-positive nuclei within the entire AC in a digitized image captured at x400 magnification using a mounted CCD camera. The total number of MAG-positive nuclei per AC was then normalized to square millimeters by measuring the area of the AC using the morphometric function of NIH Image. GFAP-positive nuclei in the AC were counted using the same strategy.

    To determine the total cellular density in the AC, CC, and cingulate cortex, 4',6-diamidino-2-phenylindole (DAPI)-stained nuclei were enumerated in the same sections as oligodendrocytes were counted. DAPI staining was performed by rinsing slides in PBS containing 1 μg/ml DAPI for 30 min after removing coverslips in xylene and rehydrating through a series of graded alcohol. DAPI fluorescence was visualized using a Nikon Eclipse microscope equipped with a Spot RT Slider CCD camera (Diagnostic Instruments, Sterling Heights, MI) connected to a Windows-based computer. Individual x400 magnified AC, CC, and cortical fields were digitized, and the numbers of DAPI-stained nuclei were counted either within a grid measuring 0.1 mm x 0.11 mm (AC and CC) or 0.27 mm x 0.38 mm at x400 magnification. Two fields were counted in each slide of the CC, AC, and cingulate cortex.

    O4 immunohistochemistry and quantification of O4-positive cells

    To determine the numerical density of O4-positive cells within the AC and CC, adjacent tissue sections to those used in in situ hybridization experiments were fixed in freshly prepared 4% paraformaldehyde in PBS for 15 min followed by three washes of PBS for 5 min each. Slides containing brain sections were then blocked in 10% normal donkey serum in PBS at room temperature for 45 min and then incubated overnight at 4 C with anti-O4 monoclonal antibody (1 μg/ml) (Chemicon, Temecula, CA) in PBS containing 1% normal donkey serum. The next day, sections were washed three times in PBS for 5 min each and then incubated at 37 C for 30 min with donkey antimouse fluorescein isothiocyanate-conjugated secondary antibody. Slides were then washed three times in PBS for 5 min each and then coverslipped in Vectashield mounting medium containing DAPI (Vector Laboratories, Burlingame, CA). Slides immunostained in the absence of primary antibody were used as negative controls. Stained sections were observed using a Nikon Eclipse microscope equipped with a Spot RT Slider CCD camera (Diagnostic Instruments) running MetaVue acquisition and analysis software (Molecular Devices, Sunnyvale, CA). The x400 magnified images were analyzed for immunopositive cells by hand using the cell count feature in MetaVue. A total of six to eight brain sections (n = 3–4 per group) were analyzed per treatment group.

    Statistical analysis

    Results were analyzed using a two-way ANOVA with PCB exposure and HTx treatment as the main effects unless otherwise stated. Post hoc tests, where appropriate, were performed by Bonferroni’s t test. Bonferroni’s t test uses the mean square error from the ANOVA table as a point estimate of the pooled variance [Graphpad Prism (ANOVA), San Diego, CA; http://www.graphpad.com/quickcalcs/ (Bonferroni’s post hoc and Grubb’s test, respectively)]. The Grubb’s test was used on all data to identify statistical outliers. Statistical outliers were identified in some data sets, but the overall results were not altered by omission. A few samples were lost during processes; therefore, there are some unequal cell sizes.

    Results

    Animals and T4

    Two-way ANOVA with repeated measures revealed a significant effect on maternal body weight of gestational day (F8,248 = 76.14; P < 0.001) but not of treatment (F3,248 = 1.463; P > 0.05) (Fig. 2A). However, there was a significant interaction among these two effects (F21,248 = 10.79; P < 0.0001), indicating that the effect of treatments were dependent upon gestational day. During lactation, both lactation day (F4,124 = 21.07; P < 0.0001) and treatment (F3,124 = 3.751; P < 0.05) affected maternal weight, but there was no interaction among these two main effects (F12,124 = 0.0623; P > 0.05) (Fig. 2A).

    In contrast, there was a significant effect of treatment on maternal body weight gain during gestation (F1,31 = 41.18; P < 0.0001) (Fig. 2B) but not during lactation. Post hoc analysis of body weight gain revealed that HTx dams gained less weight during gestation, and this was unaffected by exposure to PCBs (Fig. 2B).

    Treatment effects on maternal body weight gain was reflected in pup body weight on P15 (Fig. 2C). Two-way analysis of P15 pup body weight demonstrated an effect of HTx treatment (F1,28 = 79.64; P < 0.0001), but not of PCB exposure (F1,28 = 1.525; P > 0.05); there was no significant interaction between the two main effects (F1,28 = 0.037; P > 0.05). HTx and HTx+PCB treatment groups exhibited lower body weights compared with controls (Fig. 2C).

    Circulating levels of total T4 were lower in pups derived from dams exposed to HTx and/or PCB; in fact, HTx animals had T4 levels below the lowest standard of our assay (0.4 μg/dl). Therefore, HTx and HTx+PCB treatment groups were not included in the unpaired two-tailed t test used to demonstrate a significant difference between control animals and PCB-exposed animals (t = 7.476; P < 0.0001) (Fig. 2D).

    Treatment effects on MAG expression

    Figure 3 shows the effects of HTx treatment and PCB exposure on MAG mRNA expression in the AC and CC (Fig. 3, A and B). Both HTx (F1,24 = 180; P < 0.001) and PCB exposure (F1,24 = 12.654; P < 0.001) significantly affected MAG expression in the AC; there was no significant interaction between these two main effects (F1,24 = 0.615; P > 0.05). Post hoc analysis revealed that the abundance of MAG mRNA was significantly lower in the AC of HTx animals compared with that of control animals. In addition, MAG mRNA levels were significantly lower in the AC of PCB-exposed animals compared with controls, but not to the extent observed in HTx or HTx+PCB animals (Fig. 3B, left). Likewise in the CC, two-way ANOVA revealed a significant effect of HTx (F1,24 = 1083; P < 0.0001) and PCB (F1,24 = 27.185; P < 0.001) and a significant interaction between these two main effects (F1,24 = 24.06; P < 0.0001). Post hoc analysis revealed that MAG mRNA levels in HTx or PCB-treated animals were significantly lower than in control animals (Fig. 3B, right).

    Treatment effects on cellular levels of MAG mRNA

    To determine whether the observed treatment effects on MAG expression identified by film autoradiography were a result of effects on cellular levels of MAG mRNA, we evaluated single-cell levels of MAG mRNA using liquid emulsion autoradiography (Fig. 4A). Cellular levels of MAG mRNA were significantly affected by HTx in both the AC (F1,26 = 352; P < 0.0001) and CC (F1,26 = 464; P < 0.0001) but not by PCB exposure (AC: F1,26 = 2.578; P > 0.05; CC: F1,26 = 0.015; P > 0.05), and there was no significant interaction between the two main effects (Fig. 4B). Cellular levels of MAG mRNA in both AC and CC were significantly reduced in HTx animals but were not affected by PCB exposure either in the presence or absence of HTx (Fig. 4B).

    Treatment effects on MAG-positive oligodendrocyte density

    Our finding that PCB exposure reduced the expression of MAG mRNA on film, but did not alter cellular levels of MAG mRNA, indicated that PCB exposure reduced the number of oligodendrocytes or their packing density in the AC and CC; therefore, we counted MAG-positive oligodendrocytes in the AC and CC to test this hypothesis. Figure 4C illustrates the effects of HTx treatment and PCB exposure on MAG-positive oligodendrocyte density. Both PCB exposure (F1,25 = 9.926; P = 0.05) and HTx treatment (F1,25 = 151.4; P < 0.0001) significantly affected MAG-positive oligodendrocyte density in the AC, and there was a significant interaction between the two main effects (F1,25 = 7.707; P < 0.01) (Fig. 4C). In the CC, there was a significant affect of PCB exposure (F1,25 = 11.26; P = 0.0025) and HTx treatment (F1,25 = 101.0; P < 0.0001) but no significant interaction (F1,25 = 3.270; P > 0.05) (Fig. 4C). In both the AC and CC, treatments reduced the density of MAG-positive oligodendrocytes.

    Treatment effects on O4-positive oligodendrocyte density

    To determine whether the effects of HTx treatment and PCB exposure on the density of MAG-positive cells in the AC and CC is selective to mature oligodendrocytes, we investigated oligodendrocyte precursor cells by counting O4-positive cells in the AC and CC. Figure 5 shows the effects of HTx treatment and PCB exposure on O4-positive cells. Two-way ANOVA demonstrated an effect of HTx treatment on the density of O4-positive cells in the AC (F1,11 = 39.44; P < 0.0001) and CC (F1,10 = 16.60; P < 0.001). Despite these findings, post hoc analysis demonstrated a significant reduction between control animals and HTx animals in the AC only (Fig. 5, B and D). There was a trend for an effect of PCB exposure in AC (F1,11 = 3.92; P = 0.07) but not in the CC (F1,10 = 0.056; P = 0.8174). Lastly, there was no interaction between the two main factors in the AC (F1,11 = 1.8; P > 0.05) or CC (F1,10 = 0.0008; P > 0.05).

    Treatment effects on total cellular packing density

    To test whether treatments selectively affected oligodendrocytes, we evaluated total cellular density in the AC and CC by counting DAPI-stained nuclei contained within a fixed area. Measuring total cell density verifies changes in marker-specific cell densities and provides a baseline in which to compare the changes in marker-specific cell densities. To determine whether treatment selectively targets white matter, we also measured cellular density in an area of gray matter, the cingulate cortex. Figure 6 demonstrates the effects of treatment on cellular packing density in the AC and CC. Two-way ANOVA demonstrated that PCB exposure produced a significant effect on cell density in the CC (F1,26 = 16.51; P < 0.001) but not in the AC (F1,26 =2.101; P > 0.05). In contrast, HTx exerted a significant effect on cell density in both the CC (F1,26 = 40.05; P < 0.0001) and AC (F1,26 = 36.37; P < 0.0001). There was no significant interaction between the two main effects in either the CC (F1,26 = 0.7142; P > 0.05) or AC (F1,26 = 2.844; P > 0.05) (Fig. 6, A and B). Post hoc analysis revealed that cell density in the CC and AC was significantly reduced in HTx and HTx+PCB animals, but PCB-exposed animals exhibited a significant reduction in cell density in the CC only (Fig. 6, A and B). Cell density measurements in the cortex revealed no effect of HTx treatment (F1,25 = 0.751; P > 0.05) or PCB exposure (F1,25 = 0.966; P > 0.05) or a significant interaction between the two main effects (F1,25 = 1.732; P > 0.05) (Fig. 6C).

    Treatment effects on GFAP expression

    Considering that TH plays a role in oligodendrocyte differentiation from precursors that also give rise to astrocytes, it is important to determine whether treatments exerted specific effects on oligodendrocyte differentiation or whether astrocyte differentiation is also affected. Therefore, we examined the effect of treatment on GFAP-positive astrocytes, and these data are illustrated in Fig. 7. Both HTx (F1,25 = 20.79; P < 0.001) and PCB exposure (F1,25 = 8.974; P < 0.01) significantly affected GFAP expression, but there was no significant interaction between these two main effects (F1,25 = 0.41; P > 0.05). However, post hoc analyses showed that individual treatment groups were not significantly different from control but are different between PCB-exposed and HTx-treated animals (Fig. 7B, left). In the CC, HTx (F1,25 = 30.01; P < 0.001) exerted a significant effect, but there was no effect of PCB exposure (F1,25 = 1.1; P > 0.05) or of the interaction (F1,25 = 0.0001; P > 0.05). Both HTx and HTx+PCB treatments significantly increased GFAP mRNA expression in the CC (Fig. 7, A and B, right).

    Treatment effects on cellular levels of GFAP mRNA

    Figure 7C illustrates the effects of treatment on cellular GFAP mRNA levels in the AC and CC. HTx treatment exerted a significant effect on cellular levels of GFAP mRNA in the AC (F1,24 = 15.49; P < 0.001) but not in response to PCB exposure (F1,25 = 0.147; P > 0.05), and there was no significant interaction between these two main effects (F1,25 = 0.412; P > 0.05). Post hoc analysis revealed that cellular levels of GFAP mRNA were significantly elevated in HTx-treated animals only (Fig. 7C, left). Similarly in the CC, there was a significant effect of HTx on cellular levels of GFAP mRNA (F1,26 = 68.72; P < 0.001) but no effect of PCB exposure (F1,26 = 1.317; P > 0.05) or the interaction (F1,26 = 0.84; P > 0.05). Cellular levels of GFAP mRNA were significantly higher in HTx and HTx+PCB-treated animals compared with controls (Fig. 7C, right).

    Treatment effects on GFAP-positive astrocyte packing density

    Figure 7D illustrates the effects of treatment on the density of GFAP-positive cells in the AC and CC. Treatment effects on GFAP-positive astrocyte cell density paralleled the effect of HTx treatment on cellular levels of GFAP mRNA in AC and CC. GFAP-positive cell packing density in the AC and CC was significantly affected by HTx (AC: F1,25 = 20.02; P < 0.001; CC: F1,25 = 50.27; P < 0.001), but no effect of PCB exposure (AC: F1,25 = 2.832; P > 0.05; CC: F1,25 = 0.981; P > 0.05) or a significant interaction between the two main factors (AC: F1,25 = 0.5; P > 0.05; CC: F1,25 = 0.919; P > 0.05) (Fig. 7D). GFAP-positive astrocyte density in the AC and CC was significantly increased in HTx animals; however, HTx+PCB cotreatment significantly increased the density of GFAP-positive astrocytes only in the CC (Fig. 7D).

    Treatment effects on the sum of oligodendrocyte and astrocyte packing density

    If HTx and/or PCB exposure act on the common precursor giving rise to oligodendrocytes and astrocytes, then the sum of MAG- and GFAP-positive cells would not be altered by treatments. Figure 8 demonstrates that the sum of MAG-positive and GFAP-positive cell densities was affected by HTx treatment in the AC (F1,24 = 21.09; P < 0.001) but the not in the CC (F1,26 = 0.00001; P > 0.05). On the contrary, PCB exposure affected the sum of the densities for both the AC (F1,24 = 6.02; P < 0.05) and CC (F1,26 = 8.22; P < 0.01). There was no interaction among these main effects (AC: F1,24 = 0.419; P > 0.05; CC: F1,26 = 0.007; P > 0.05). However, post hoc tests demonstrated that the sum of MAG-positive and GFAP-positive cell densities was significantly reduced compared with controls only in the AC of HTx and HTx+PCB (Fig. 8, A and B).

    Treatment effects on the proportion of oligodendrocytes and astrocytes in the AC and CC

    We used our oligodendrocyte and cell density data to determine treatment effects on the proportion of oligodendrocytes in the AC and CC (Fig. 8, C and D). PCB exposure did not alter the proportion of oligodendrocytes occupying the AC (F1,25 = 1.983; P > 0.05) or CC (F1,25 = 0.550; P > 0.05). In contrast, HTx exerted a significant effect on the proportion of oligodendrocytes in both the AC (F1,25 = 66.33; P < 0.0001) and CC (F1,25 = 33.09; P < 0.0001) (Fig. 8C). Post hoc analysis demonstrated that HTx animals had a significantly lower proportion of MAG-positive oligodendrocytes in the AC and CC than control animals (Fig. 8C). Similarly, the proportion of GFAP-positive astrocytes in the AC and CC was significantly affected by HTx treatment (AC: F1,27 =39.74; P < 0.001; CC: F1,27 = 94.75; P < 0.001). HTx animals exhibited significantly greater proportions of GFAP-positive astrocytes in both the AC and CC compared with controls (Fig. 8D). No effect of PCB exposure on the proportion of GFAP-positive cells in the AC or CC was measured.

    Discussion

    Experimental studies indicate that PCB exposure may exert adverse effects on the developing brain by reducing circulating levels of TH, causing a state of relative hypothyroidism (31, 32). This hypothesis is supported by the observation in animals that PCB exposure reduces serum TH (21, 28, 33, 34, 35) and by the observation in some epidemiological studies that PCB body burden is negatively associated with measures of thyroid function (36, 37, 38, 39). In contrast, PCBs may also exert direct actions on the TR, independent of effects on serum TH levels (40, 41). This hypothesis is based in part on the observation that PCBs can directly inhibit or enhance TR activity in vitro (42, 43, 44, 45, 46, 47). Moreover, several reports indicate that PCB exposure can exert TH-like actions in the developing brain (15, 21, 28, 48). In the present studies, we tested the hypothesis that PCB exposure affects white matter tract development by interfering with TH action. Our results clearly demonstrate that developmental PCB exposure does not recapitulate the full effect of hypothyroidism on the cellular composition of white matter.

    In the present study, developmental exposure to hypothyroidism produced an overall reduction in cell density (number of cells per unit area) in the genu of the CC and in the AC. In addition, hypothyroidism produced a disproportionately greater decrease in the density of MAG-positive oligodendrocytes in these tracts with a simultaneous increase in the density of GFAP-positive astrocytes. Furthermore, hypothyroidism reduced the density of O4-positive oligodendrocytes in the AC and CC. These effects were specific to white matter inasmuch as the cellular density of a single region of gray matter (cingulate cortex) was unaffected by hypothyroidism. Similarly, developmental exposure to PCBs produced an overall reduction in the total cell density of these white matter tracts, and this effect was selective inasmuch as the total cell density of cingulate cortex was unaffected by PCB exposure. However, PCB exposure did not affect the relative proportion of MAG-positive or GFAP-positive cells. Thus, PCB exposure mimicked some, but not all, of the effects of hypothyroidism on white matter development.

    The finding that hypothyroidism induced a disproportionate decrease in the density of MAG-positive oligodendrocytes and a simultaneous and proportional increase in GFAP-positive astrocytes (Fig. 8) is consistent with the hypothesis that these two cell types are derived from a common precursor in the AC and CC (49, 50, 51, 52) and that TH acts on these precursor cells to trigger oligodendrocyte differentiation at the expense of astrocyte differentiation (12, 14, 53, 54). Moreover, our finding that the sum of the densities of astrocytes and oligodendrocytes in the CC was not altered by hypothyroidism (Fig. 8) further supports this interpretation. These findings are consistent with previous work showing that TH insufficiency decreases oligodendrocyte numbers in vivo (6, 55) and increases astrocyte numbers in white matter of the cerebellum (56, 57). Our present data indicate that a potentially important role of TH in white matter tract development is to control the ratio of MAG-positive oligodendrocytes to GFAP-positive astrocytes in two major white matter tracts.

    We observed that the effects of HTx treatment on single-cell levels of both MAG and GFAP mRNAs are mirrored in our MAG-positive and GFAP-positive cell density measurements. Specifically, HTx treatment reduced cellular levels of MAG mRNA and concomitantly the density of MAG-positive cells. Likewise, cellular levels of GFAP mRNA increased in HTx-treated animals as did the density of GFAP-positive cells. Thus, it is possible that our cell density measurements reflect the number of cells that reach a threshold level of detection for each marker rather than accurate MAG-positive and GFAP-positive cell density measurements. Although this interpretation is plausible, there are two elements of the current study that suggest the effects of TH on cellular levels of MAG and GFAP mRNAs are not a confounding variable. First, MAG mRNA levels are quite abundant on P15, and even the least intensely labeled cell is far above the threshold of detection. Second, we found that the density of cells positive for a second, independent marker of oligodendrocytes, the O4 antigen, was simultaneously reduced in the AC and CC of HTx animals. These findings are more consistent with the interpretation that oligodendrocyte differentiation was reduced in these HTx animals.

    In contrast, we found that PCB exposure had no effect on the density of O4-positive cells in the AC or CC. The finding that PCB exposure did not reduce O4-positive cells is contrary to the finding that PCB exposure did reduce MAG-positive oligodendrocytes in the AC and CC. Oligodendrocyte differentiation proceeds through a defined series of antigen acquisition that characterizes various stages of the oligodendrocyte lineage, with the O4 antigen being expressed in the oligodendrocyte lineage at an earlier stage than MAG (58). Thus, our observation that PCB exposure reduced the density of MAG-positive cells, but not O4-positive cells, suggests that PCB exposure may selectively affect oligodendrocyte differentiation at a stage that differs from that of hypothyroidism , specifically between acquisition of O4 and MAG expression.

    We were somewhat surprised that the effects hypothyroidism on packing density were selective to the AC and CC and unaffected in the cingulate cortex, because early reports indicated that cortical packing density was increased in HTx animals (59). This discrepancy may be attributable to technical differences in animal treatment or to technical differences in the method of analysis. Specifically, earlier reports used the DNA content of wet tissue as a measure of cell packing density; in contrast, we physically counted DAPI-stained nuclei in the cingulate cortex. It is likely that our method of physically counting nuclei is a more accurate measurement. However, it is premature to assume that cell density in all gray matter regions remain unaffected in HTx or PCB-exposed animals.

    Previous studies have clearly demonstrated the necessity of sufficient TH for proper myelination of white matter tracts (6, 19, 60). In the present study, we used a dose of PCB exposure that reduced circulating levels of TH by about 80% (from 5.85 ± 0.38 to 1.37 ± 0.42) in P15 pups. Crofton has reported that a 60% reduction in serum total T4 is associated with a PCB-induced hearing loss in rats (31); thus, our procedure produced a reduction in serum T4 that was greater than that associated with other adverse effects in the developing nervous system. However, we found that PCB exposure caused a reduction in total cell density of the CC and reduced MAG-positive cells in AC and CC, similar to that of hypothyroidism, but it did not alter the ratio of MAG-positive oligodendrocytes to GFAP-positive astrocytes or disproportionately reduce the density of MAG-positive oligodendrocytes in either white matter tract investigated. Thus, the PCB-induced reduction in circulating levels of T4 did not fully recapitulate the effects of goitrogen-induced hypothyroidism, indicating that developmental exposure to PCBs did not affect developing white matter by causing a state of relative hypothyroidism.

    It should be noted that in the present study, our goitrogen treatment reduced T4 levels below the lowest standard of our assay. Thus, because of the severely depressed T4 levels, synergistic or additive effects of PCBs and hypothyroidism may not be detectable. Consequently, we may not have been able to differentiate effects resulting from hypothyroidism from those that may result from the addition of PCBs.

    Developmental exposure to PCBs can increase the expression of TH-responsive genes in the developing brain despite significantly reducing circulating T4 (21, 28, 48). In addition, Fritsche et al. (15) have shown that PCB-118, a congener known to rapidly accumulate in brain tissue (61), can induce oligodendrocyte differentiation in a human neural progenitor cell line by acting on the TR. Interestingly, sustained neonatal hyperthyroidism leads to a reduction in the expression of myelin-associated genes (62), although it is not clear whether this observation is linked to changes in oligodendrocyte number or proportion relative to astrocytes or total numbers of cells. Considering these findings, it is possible that PCB exposure can act as an inappropriate TH-like signal during early development, ultimately causing a reduction in the numbers of cells present in these white matter tracts. However, in our current experiments, we failed to observe that PCB exposure could ameliorate the effects of hypothyroidism. Therefore, these observations are inconsistent with the hypothesis that PCBs act as TR agonists on white matter. However, it should be noted that our ability to detect TH-like effects of PCBs in hypothyroid animals may have been compromised by the severity of TH insufficiency induced in HTx-treated animals.

    It is important to recognize that PCBs may be acting on white matter development by a mechanism that does not include TH signaling. In fact, the findings reported here are largely consistent with the idea that the effects of PCBs on white matter composition are not the result of altered TH action. Some PCB congeners can bind to the ryanodine receptor, affecting calcium signaling (63, 64, 65), and calcium signaling may be important in oligodendrocyte precursor cell differentiation (66). In addition, PCBs can induce reactive oxygen species in neuronal cultures that ultimately leads to cell death (67), and oligodendrocytes are sensitive to elevated levels of reactive oxygen species (68). Regardless of the mechanism by which PCB exposure selectively reduces the cellular density of these white matter tracts that we have observed in the present experiments, it is a potentially important observation. Because the proportion of oligodendrocytes is reduced relative to gray matter, it is possible that fewer axon fibers are myelinated in these white matter tracts, and this may be true in humans as well as in animals. The size of the CC is reported to be altered in magnetic resonance imaging studies on children diagnosed with disorders associated with impulse behaviors and cognitive deficits including attention deficit hyperactivity disorder, Tourette’s, and autism (69, 70, 71, 72, 73, 74). Moreover, exposure to environmental chemicals has been linked to these disorders (75, 76). Finally, a recent report has documented that the size of the CC is a strong predictor for the association between cord blood levels of PCBs and response inhibition (3). Thus, it is possible that effects of PCB exposure on the cellular composition of white matter tracts may underlie some neurological deficits detected in children exposed to PCBs.

    Acknowledgments

    We thank K. Gauger and S. Giera for comments on early versions of this manuscript.

    Footnotes

    This work was supported in part by STAR (Science to Achieve Results) Environmental Protection Agency Fellowship FP916424 (to D.S.S), National Institutes of Health Grant ES10026 (to R.T.Z.), and Environmental Protection Agency Grant RD-3213701-0 (to R.T.Z.).

    First Published Online November 10, 2005

    Abbreviations: AC, Anterior commissure; CC, corpus callosum; DAPI, 4',6-diamidino-2-phenylindole; G2, gestational d 2; GFAP, glial fibrillary acidic protein; HTx, hypothyroid; MAG, myelin-associated glycoprotein; MMI, methimazole; P15, postnatal d 15; PCB, polychlorinated biphenyl; SSC, standard saline citrate; TH, thyroid hormone; TR, TH receptor.

    Accepted for publication October 28, 2005.

    References

    Fisher BE 1999 Most unwanted. Environ Health Perspect 107:A18–A23

    Schantz SL, Widholm JJ, Rice DC 2003 Effects of PCB exposure on neuropsychological function in children. Environ Health Perspect 111:357–576

    Stewart P, Fitzgerald S, Reihman J, Gump B, Lonky E, Darvill T, Pagano J, Hauser P 2003 Prenatal PCB exposure, the corpus callosum, and response inhibition. Environ Health Perspect 111:1670–1677

    Colborn T 2004 Neurodevelopment and endocrine disruption. Environ Health Perspect 112:944–949

    Zoeller RT 2005 Thyroid hormone and brain development: environmental influences. Curr Opin Endocrinol Diabetes 12:31–35

    Schoonover CM, Seibel MM, Jolson DM, Stack MJ, Rahman RJ, Jones SA, Mariash CN, Anderson GW 2004 Thyroid hormone regulates oligodendrocyte accumulation in developing rat brain white matter tracts. Endocrinology 145:5013–5020

    Berbel P, Guadano-Ferraz A, Angulo A, Ramon Cerezo J 1994 Role of thyroid hormones in the maturation of interhemispheric connections in rats. Behav Brain Res 64:9–14

    Gravel C, Hawkes R 1990 Maturation of the corpus callosum of the rat. I. Influence of thyroid hormones on the topography of callosal projections. J Comp Neurol 291:128–146

    Annunziata P, Federico A, D’Amore I, Corona RM, Guazzi GC 1983 Impairment of human brain development: glycoconjugate and lipid changes in congenital athyroidism. Early Hum Dev 8:269–278

    Shenkman L, Mitsuma T, Suphavai A, Hollander CS 1972 Hypothalamic hypothyroidism. JAMA 222:480–481

    Bernal J 2002 Action of thyroid hormone in brain. J Endocrinol Invest 25:268–288

    Chojnacki A, Weiss S 2004 Isolation of a novel platelet-derived growth factor-responsive precursor from the embryonic ventral forebrain. J Neurosci 24:10888–10899

    Murray K, Dubois-Dalcq M 1997 Emergence of oligodendrocytes from human neural spheres. J Neurosci Res 50:146–156

    Johe KK, Hazel TG, Muller T, Dugich-Djordjevic MM, McKay RD 1996 Single factors direct the differentiation of stem cells from the fetal and adult central nervous system. Genes Dev 10:3129–3140

    Fritsche E, Cline JE, Nguyen NH, Scanlan TS, Abel J 2005 Polychlorinated biphenyls disturb differentiation of normal human neural progenitor cells: clue for involvement of thyroid hormone receptors. Environ Health Perspect 113:871–876

    Kanfer J, Parenty M, Goujet-Zalc C, Monge M, Bernier L, Campagnoni AT, Dautigny A, Zalc B 1989 Developmental expression of myelin proteolipid, basic protein, and 2',3'-cyclic nucleotide 3'-phosphodiesterase transcripts in different rat brain regions. J Mol Neurosci 1:39–46

    Walker P, Dubois JD, Dussault JH 1980 Free thyroid hormone concentrations during postnatal development in the rat. Pediatr Res 14:247–249

    Gravel C, Sasseville R, Hawkes R 1990 Maturation of the corpus callosum of the rat. II. Influence of thyroid hormones on the number and maturation of axons. J Comp Neurol 291:147–161

    Ibarrola N, Rodriguez-Pena A 1997 Hypothyroidism coordinately and transiently affects myelin protein gene expression in most rat brain regions during postnatal development. Brain Res 752:285–293

    Institute of Laboratory Animal Resources (U.S.) 1996 Guide for the care and use of laboratory animals. 7th ed. Washington, DC: National Academy Press

    Gauger KJ, Kato Y, Haraguchi K, Lehmler HJ, Robertson LW, Bansal R, Zoeller RT 2004 Polychlorinated biphenyls (PCBs) exert thyroid hormone-like effects in the fetal rat brain but do not bind to thyroid hormone receptors. Environ Health Perspect 112:516–523

    Rodriguez-Pena A, Ibarrola N, Iniguez MA, Munoz A, Bernal J 1993 Neonatal hypothyroidism affects the timely expression of myelin-associated glycoprotein in the rat brain. J Clin Invest 91:812–818

    See J, Zhang X, Eraydin N, Mun SB, Mamontov P, Golden JA, Grinspan JB 2004 Oligodendrocyte maturation is inhibited by bone morphogenetic protein. Mol Cell Neurosci 26:481–492

    Zoeller RT, Butnariu OV, Fletcher DL, Riley EP 1994 Limited postnatal ethanol exposure permanently alters the expression of mRNAs encoding myelin basic protein and myelin-associated glycoprotein in cerebellum. Alcohol Clin Exp Res 18:909–916

    Levison SW, Druckman SK, Young GM, Basu A 2003 Neural stem cells in the subventricular zone are a source of astrocytes and oligodendrocytes, but not microglia. Dev Neurosci 25:184–196

    Paxinos G, Watson C 1986 The rat brain in stereotaxic coordinates. 2nd ed. San Diego: Academic Press

    Zoeller RT, Fletcher DL, Butnariu O, Lowry C, Moore FL 1997 N-Ethylmaleimide (NEM) can significantly improve in situ hybridization results using 35S-labeled oligodeoxynucleotide or complementary RNA probes. J Histochem Cytochem 45:1035–1041

    Zoeller RT, Dowling AL, Vas AA 2000 Developmental exposure to polychlorinated biphenyls exerts thyroid hormone-like effects on the expression of RC3/neurogranin and myelin basic protein messenger ribonucleic acids in the developing rat brain. Endocrinology 141:181–189

    Rogers AW 1979 Techniques of autoradiography. Amsterdam: Elsevier/North Holland

    Petersen SL, McCrone S, Keller M, Shores S 1995 Effects of estrogen and progesterone on luteinizing hormone-releasing hormone messenger ribonucleic acid levels: consideration of temporal and neuroanatomical variables. Endocrinology 136:3604–3610

    Crofton KM 2004 Developmental disruption of thyroid hormone: correlations with hearing dysfunction in rats. Risk Anal 24:1665–1671

    Brouwer A, Morse DC, Lans MC, Schuur AG, Murk AJ, Klasson-Wehler E, Bergman A, Visser TJ 1998 Interactions of persistent environmental organohalogens with the thyroid hormone system: mechanisms and possible consequences for animal and human health. Toxicol Ind Health 14:59–84

    Bastomsky CH 1977 Enhanced thyroxine metabolism and high uptake goiters in rats after a single dose of 2,3,7,8-tetrachlorodibenzo-p-dioxin. Endocrinology 101:292–296

    Bastomsky CH, Murthy PVN, Banovac K 1976 Alterations in thyroxine metabolism produced by cutaneous application of microscope immersion oil: effects due to polychlorinated biphenyls. Endocrinology 98:1309–1314

    Kato Y, Ikushiro S, Haraguchi K, Yamazaki T, Ito Y, Suzuki H, Kimura R, Yamada S, Inoue T, Degawa M 2004 A possible mechanism for decrease in serum thyroxine level by polychlorinated biphenyls in Wistar and Gunn rats. Toxicol Sci 81:309–315

    Hagmar L 2003 Polychlorinated biphenyls and thyroid status in humans: a review. Thyroid 13:1021–1028

    Sala M, Sunyer J, Herrero C, To-Figueras J, Grimalt J 2001 Association between serum concentrations of hexachlorobenzene and polychlorobiphenyls with thyroid hormone and liver enzymes in a sample of the general population. Occup Environ Med 58:172–177

    Persky V, Turyk M, Anderson HA, Hanrahan LP, Falk C, Steenport DN, Chatterton Jr R, Freels S 2001 The effects of PCB exposure and fish consumption on endogenous hormones. Environ Health Perspect 109:1275–1283

    Koopman-Esseboom C, Morse DC, Weisglas-Kuperus N, Lutkeschiphost IJ, van der Paauw CB, Tuinstra LGMT, Brouwer A, Sauer PJJ 1994 Effects of dioxins and polychlorinated biphenyls on thyroid hormone status of pregnant women and their infants. Pediatr Res 36:468–473

    Zoeller RT, Dowling ALS, Herzig CTA, Iannacone EA, Gauger KJ, Bansal R 2002 Thyroid hormone, brain development, and the environment. Environ Health Perspect 110(Suppl 3):355–361

    Zoeller RT 2003 Thyroid toxicology and brain development: should we think differently Environ Health Perspect 111:A628

    Miyazaki W, Iwasaki T, Takeshita A, Kuroda Y, Koibuchi N 2004 Polychlorinated biphenyls suppress thyroid hormone receptor-mediated transcription through a novel mechanism. J Biol Chem 279:18195–18202

    Bogazzi F, Raggi F, Ultimieri F, Russo D, Campomori A, McKinney JD, Pinchera A, Bartalena L, Martino E 2003 Effects of a mixture of polychlorinated biphenyls (Aroclor 1254) on the transcriptional activity of thyroid hormone receptor. J Endocrinol Invest 26:972–978

    Iwasaki T, Miyazaki W, Takeshita A, Kuroda Y, Koibuchi N 2002 Polychlorinated biphenyls suppress thyroid hormone-induced transactivation. Biochem Biophys Res Commun 299:384–388

    Kitamura S, Jinno N, Suzuki T, Sugihara K, Ohta S, Kuroki H, Fujimoto N 2005 Thyroid hormone-like and estrogenic activity of hydroxylated PCBs in cell culture. Toxicology 208:377–387

    Arulmozhiraja S, Shiraishi F, Okumura T, Iida M, Takigami H, Edmonds JS, Morita M 2005 Structural requirements for the interaction of 91 hydroxylated polychlorinated biphenyls with estrogen and thyroid hormone receptors. Toxicol Sci 84:49–62

    Yamada-Okabe T, Aono T, Sakai H, Kashima Y, Yamada-Okabe H 2004 2,3,7,8-Tetrachlorodibenzo-p-dioxin augments the modulation of gene expression mediated by the thyroid hormone receptor. Toxicol Appl Pharmacol 194:201–210

    Bansal R, You SH, Herzig CT, Zoeller RT 2005 Maternal thyroid hormone increases HES expression in the fetal rat brain: an effect mimicked by exposure to a mixture of polychlorinated biphenyls (PCBs). Brain Res Dev Brain Res 156:13–22

    Grinspan JB, Stern JL, Pustilnik SM, Pleasure D 1990 Cerebral white matter contains PDGF-responsive precursors to O2A cells. J Neurosci 10:1866–1873

    Liu Y, Rao MS 2004 Olig genes are expressed in a heterogeneous population of precursor cells in the developing spinal cord. Glia 45:67–74

    Noble M, Murray K, Stroobant P, Waterfield MD, Riddle P 1988 Platelet-derived growth factor promotes division and motility and inhibits premature differentiation of the oligodendrocyte/type-2 astrocyte progenitor cell. Nature 333:560–562

    Raff MC, Miller RH, Noble M 1983 A glial progenitor cell that develops in vitro into an astrocyte or an oligodendrocyte depending on culture medium. Nature 303:390–396

    Baas D, Bourbeau D, Sarlieve LL, Ittel ME, Dussault JH, Puymirat J 1997 Oligodendrocyte maturation and progenitor cell proliferation are independently regulated by thyroid hormone. Glia 19:324–332

    Grinspan JB, Edell E, Carpio DF, Beesley JS, Lavy L, Pleasure D, Golden JA 2000 Stage-specific effects of bone morphogenetic proteins on the oligodendrocyte lineage. J Neurobiol 43:1–17

    Ahlgren SC, Wallace H, Bishop J, Neophytou C, Raff MC 1997 Effects of thyroid hormone on embryonic oligodendrocyte precursor cell development in vivo and in vitro. Mol Cell Neurosci 9:420–432

    Faivre-Sarrailh C, Rami A, Fages C, Tardy M 1991 Effect of thyroid deficiency on glial fibrillary acidic protein (GFAP) and GFAP-mRNA in the cerebellum and hippocampal formation of the developing rat. Glia 4:276–284

    Granholm AC 1985 Effects of thyroid hormone deficiency on glial constituents in developing cerebellum of the rat. Exp Brain Res 59:451–456

    Rowitch DH, Lu QR, Kessaris N, Richardson WD 2002 An ‘oligarchy’ rules neural development. Trends Neurosci 25:417–422

    Eayrs JT, Horn G 1955 The development of cerebral cortex in hypothyroid and starved rats. Anat Rec 121:53–61

    Ferreira AA, Nazario JC, Pereira MJ, Azevedo NL, Barradas PC 2004 Effects of experimental hypothyroidism on myelin sheath structural organization. J Neurocytol 33:225–231

    Kodavanti PRS, Ward TR, Derr-Yellin EC, Mundy WR, Casey AC, Bush B, Tilson HA 1998 Congener-specific distribution of polychlorinated biphenyls in brain regions, blood, liver, and fat of adult rats following repeated exposure to Aroclor 1254. Toxicol Appl Pharmacol 153:199–210

    Marta CB, Adamo AM, Soto EF, Pasquini JM 1998 Sustained neonatal hyperthyroidism in the rat affects myelination in the central nervous system. J Neurosci Res 53:251–259

    Wong PW, Joy RM, Albertson TE, Schantz SL, Pessah IN 1997 Ortho-substituted 2,2',3,5',6-pentachlorobiphenyl (PCB 95) alters rat hippocampal ryanodine receptors and neuroplasticity in vitro: evidence for altered hippocampal function. Neurotoxicology 18:443–456

    Wong PW, Garcia EF, Pessah IN 2001 ortho-Substituted PCB95 alters intracellular calcium signaling and causes cellular acidification in PC12 cells by an immunophilin-dependent mechanism. J Neurochem 76:450–463

    Gafni J, Wong PW, Pessah IN 2004 Non-coplanar 2,2',3,5',6-pentachlorobiphenyl (PCB 95) amplifies ionotropic glutamate receptor signaling in embryonic cerebellar granule neurons by a mechanism involving ryanodine receptors. Toxicol Sci 77:72–82

    Haak LL, Song LS, Molinski TF, Pessah IN, Cheng H, Russell JT 2001 Sparks and puffs in oligodendrocyte progenitors: cross talk between ryanodine receptors and inositol trisphosphate receptors. J Neurosci 21:3860–3870

    Lee DW, Opanashuk LA 2004 Polychlorinated biphenyl mixture aroclor 1254-induced oxidative stress plays a role in dopaminergic cell injury. Neurotoxicology 25:925–939

    Griot C, Vandevelde M, Richard A, Peterhans E, Stocker R 1990 Selective degeneration of oligodendrocytes mediated by reactive oxygen species. Free Radic Res Commun 11:181–193

    Egaas B, Courchesne E, Saitoh O 1995 Reduced size of corpus callosum in autism. Arch Neurol 52:794–801

    Giedd JN, Castellanos FX, Casey BJ, Kozuch P, King AC, Hamburger SD, Rapoport JL 1994 Quantitative morphology of the corpus callosum in attention deficit hyperactivity disorder. Am J Psychiatry 151:665–669

    Hardan AY, Minshew NJ, Keshavan MS 2000 Corpus callosum size in autism. Neurology 55:1033–1036

    Hynd GW, Semrud-Clikeman M, Lorys AR, Novey ES, Eliopulos D, Lyytinen H 1991 Corpus callosum morphology in attention deficit-hyperactivity disorder: morphometric analysis of MRI. J Learn Disabil 24:141–146

    Piven J, Bailey J, Ranson BJ, Arndt S 1997 An MRI study of the corpus callosum in autism. Am J Psychiatry 154:1051–1056

    Plessen KJ, Wentzel-Larsen T, Hugdahl K, Feineigle P, Klein J, Staib LH, Leckman JF, Bansal R, Peterson BS 2004 Altered interhemispheric connectivity in individuals with Tourette’s disorder. Am J Psychiatry 161:2028–2037

    London EA 2000 The environment as an etiologic factor in autism: a new direction for research. Environ Health Perspect 108(Suppl 3):401–404

    Rice DC 2000 Parallels between attention deficit hyperactivity disorder and behavioral deficits produced by neurotoxic exposure in monkeys. Environ Health Perspect 108(Suppl 3):405–408(David S. Sharlin, Ruby Bansal and R. Tho)