![]() |
|
|
| |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
McArdle Laboratory for Cancer Research, University of Wisconsin Medical School, Madison, Wisconsin
Received October 10, 2005; accepted December 14, 2005
| Abstract |
|---|
|
|
|---|
The compound 2,3,7,8-tetrachlorodibenzo-p-dioxin (dioxin) is a prototype for the study of gene-environment interactions. Dioxin is an ubiquitous environmental pollutant that is known to cause toxicity (Poland and Glover, 1973
; Poland and Knutson, 1982
; Anderson et al., 1993
), cancer (Pitot et al., 1980
; Becher and Flesch-Janys, 1998
), and terata in experimental animals (Couture et al., 1990
; Abbott and Birnbaum, 1991
; Hamm et al., 2000
; Loertscher et al., 2002
). Moreover, this compound has been associated with a spectrum of adverse health outcomes in human populations (Mastroiacovo et al., 1988
; Rogan et al., 1988
; Stockbauer et al., 1988
; Wolfe et al., 1995
). The most well characterized genetic modifier of dioxin signaling is the Ahr locus. The Ahr locus encodes the aryl hydrocarbon receptor (AHR), a ligand-activated transcription factor that transduces the dioxin signal to the nucleus (Bank et al., 1992
; Harper et al., 1992
; Dolwick et al., 1993
). In the mouse, the Ahr locus exists as four alleles, denoted Ahrb1, Ahrb2, Ahrb3, and Ahrd. The b alleles encode receptors with a high binding affinity for dioxin, and the d allele encodes a receptor with a lower affinity (Poland et al., 1994
). C57BL/6 mice that express the Ahrb1 allele are highly sensitive to the toxic and teratogenic effects of dioxin, whereas DBA/2 mice with the Ahrd allele are less sensitive (Poland and Glover, 1980
).
Genetic analyses in the mouse have provided evidence that polymorphisms at loci other than Ahr may have a significant impact on dioxin sensitivity. In an early screen of mouse strains for their sensitivity to dioxin-induced cleft palate, it was observed that the CBA/J mouse strain was relatively resistant to dioxin-induced cleft palate compared with other strains that also harbored Ahr b alleles (Poland and Glover, 1980
). In this regard, exposure of pregnant CBA/J dams to 30 µg/kg dioxin did not induce cleft palate in any of 61 scored offspring. In contrast, other Ahr b allele strains, C57BL6/J and BALB/c, displayed a cleft palate incidence ranging from 54 to 95%. These data support the idea that the mammalian genome harbors additional genetic loci, other than Ahr, that significantly influence the teratogenic sensitivity to dioxin.
|
| Materials and Methods |
|---|
|
|
|---|
Assessment of Terata. At E17, the dam was sacrificed by cervical dislocation, and the uterus was dissected from the dam and placed into ice-cold phosphate-buffered saline. A 3-mm section of each embryo tail was taken for DNA isolation and later genotyping. Fusion of the hard palate was scored by gross examination of the oral cavity (Fig. 1A). Palatal shelves that failed to fuse were recorded as "cleft palate" (Fig. 1B). The cleft palate phenotype occurred as a binary event, in that all of the shelves that failed to fuse exhibited an identical cleft of the secondary palate. The urogenital tract was dissected and macroscopically assessed for swelling of the kidneys and ureters (Fig. 1C). If such swelling was observed, it was scored as "hydronephrosis" (Fig. 1D). The sex of each embryo was scored according to its internal anatomy (Fig. 1, C and D). Comparisons of the incidence of terata between groups were made using the Fisher's exact test.
Genotype Analysis. The DNA was isolated from the tail of the embryo via standard proteinase K-phenol extraction protocol (Sambrook et al., 1989
). The polymerase chain reaction (PCR) was used to amplify informative SSLP microsatellites in the embryo DNA (Bilger et al., 2004
). Ninety-six B6CBAF2 embryos from a B6CBAF1 (the dam is listed first and the sire second) intercross were scored and genotyped at 58 SSLP loci, and 100 embryos from a CBAxB6CBAF1 backcross were scored and genotyped by PCR at 60 SSLP loci (Table 1). The PCR was performed using 100 ng of genomic DNA at an initial denaturing step of 95°C for 5 min. After denaturation, 30 cycles were performed at 95°C for 1 min, 54°C for 45 s, and 72°C for 1 min. A final extension step was carried out at 72°C for 5 min. The specific annealing temperatures were optimized for each primer set (Table 1). The PCR products were resolved on 4% (w/v) NuSieve 3:1 agarose gels (Cambrex Bio Science Rockland, Inc., Rockland ME).
|
Linkage Analysis. For each SSLP microsatellite marker, a likelihood ratio test was used to test for linkage to a quantitative trait locus influencing the incidence of cleft palate. The LOD score for each marker was computed by dividing the value for the likelihood ratio test statistic by 2 ln(10). The genome-wide significance level (P value) at each marker within a cross was determined by a permutation test (Churchill and Doerge, 1994
) in which 100,000 random permutations of the phenotypes (cleft palate or normal) were performed. For each permutation, the largest likelihood ratio statistic across the set of markers was recorded, and this null distribution was used to determine the genome-wide significance (two-sided) for linkage to each marker (Lystig, 2003
). This approach has been used previously by our group (Lee et al., 1997
; software is available at http://www.mcardle.wisc.edu/qlink).
|
| Results |
|---|
|
|
|---|
Incidence of Dioxin-Induced Cleft Palate. The cleft palate incidence in the progeny exposed to dioxin is presented in Fig. 2A. The incidence of dioxin-induced cleft palate was significantly higher in progeny of the B6 parental strain (97%) compared with the CBA parental strain (8%) (p < 10-6). There was also a significantly greater induction of cleft palate in the B6CBAF1 embryos (44%) compared with the CBAB6F1 embryos (15%) (p
0.002). The progeny from the B6CBAF1 x CBA backcross exhibited a cleft palate incidence of 72%. The progeny of the B6CBAF1 intercross had a cleft palate incidence of 70%, which was significantly different from both of the parental strains, B6 (97%) and CBA (8%) (p < 0.001). The CBAxB6CBAF1 backcross gave rise to progeny with a cleft palate incidence of 38%, which was significantly different from the parental strain, CBA (8%; p < 0.01), but not different from B6CBAF1 (44%). The cleft palate sensitivities of male and female CBAxB6CBAF1 backcross progeny did not differ significantly and were found to be 21 and 17%, respectively.
Incidence of Dioxin-Induced Hydronephrosis. The hydronephrosis incidences in the progeny exposed to dioxin are presented in Fig. 2B. The incidence of hydronephrosis is nearly 100% for most of the progeny. However, the incidences of hydronephrosis in both CBA and CBAxB6CBAF1 progeny were significantly less than in B6 progeny (69 and 67%, respectively; p < 0.001). The hydronephrosis sensitivity of male versus female progeny of the CBAxB6CBAF1 backcross was found to be 72% versus 62%, respectively, which was not statistically significant. Given the high incidence of hydronephrosis in the backcross and intercross progeny under these treatment conditions, we were unable to identify loci that influenced this phenotype by linkage analysis in our screen.
Linkage Analysis of Cleft Palate in B6CBAF1 Intercross and CBAxB6CBAF1 Backcross Mice. We observed that the incidence of cleft palate in mice exposed to dioxin in utero was highly dependent on the genotype of the mice for the marker D3Mit62 on proximal chromosome 3 (Table 2). In the intercross, the incidence of cleft palate in mice homozygous for the CBA allele at D3Mit62 was 57%, whereas those for heterozygous or homozygous B6 mice were 67% and 100%, respectively. The LOD score for D3Mit62 was 4.01 (genome-wide P = 0.009). The same trend was observed in the backcross, with a 27% incidence of cleft palate in the animals homozygous for the CBA allele at D3Mit62 and a 48% incidence in the heterozygotes. Although significant linkage was not observed for the backcross (LOD = 1.06), combining the results of the two crosses (LOD = 5.07) demonstrated significant linkage between dioxin-induced cleft palate and D3Mit62 (genome-wide P = 0.046, by permutation test). We have designated the locus on proximal chromosome 3 that modulates cleft palate incidence as Cmt1, indicating its role in chemically mediated teratogenesis.
|
The marker D12Mit12 on proximal chromosome 12 had the second highest LOD score (3.15) for the combined crosses. Although linkage of cleft palate to D12Mit12 was not statistically significant, this result is of interest in that D12Mit12 is within 12 cM of Ahr. In contrast to Cmt1, the CBA allele conferred an increased sensitivity of cleft palate. In the intercross, the incidence of cleft palate in D12Mit12 homozygous CBA, heterozygous, and homozygous B6 mice was 85, 78, and 48%, respectively. Logistic regression analysis indicated that the effects of Cmt1 and the chromosome 12 locus were additive.
| Discussion |
|---|
|
|
|---|
Given the multiple steps in AHR signal transduction and the complexities of mammalian development, we predicted that additional genetic modifiers would exist for dioxin-induced teratogenesis. To gain support for the idea that genes other than the Ahr might influence the teratogenic response to dioxin, we first examined the literature and found that there was evidence for unidentified loci that have a significant impact on AHR biology (Poland and Glover, 1980
; Robinson et al., 2002
). In particular, data from a screen of inbred mouse strains demonstrated significant variation in their sensitivity to dioxin-induced cleft palate. The observation that two Ahr b allele strains, B6 and CBA, displayed significantly different sensitivities led us to use crosses of these inbred strains to identify loci that modify the teratogenic sensitivity to dioxin.
To identify modifier loci, we employed a classic linkage-analysis approach, where polymorphic SSLP microsatellite markers were analyzed for their segregation with sensitivity to dioxin-induced terata in crosses between B6 and CBA strains. To this end, we genotyped the progeny from the B6CBAF1 intercross and the CBAxB6CBAF1 backcross and followed cosegregation of the markers with sensitivity to dioxin-induced cleft palate. A backcross analysis is more efficient than an intercross because each backcross animal will have one of only two genotypes at each locus compared with three genotypes in intercross progeny. This allows for the analysis of fewer mice. On the other hand, the intercross is able to map recessive alleles. We also uncovered a potential maternal effect in our initial crosses. That is, there was an increased incidence of cleft palate among F1 embryos born to B6 dams (44%) compared with those born to CBA dams (15%; Fig. 2A; P < 0.002). Therefore, in our case, it was important to employ both strategies to detect genetic modifiers in the progeny that might be masked by the maternal environment.
With respect to phenotype, we scored for cleft palate and hydronephrosis, two well characterized terata that are induced by dioxin exposure. Given that dioxin-induced hydronephrosis occurs at a dose approximately 10-fold lower than the dose that produces cleft palate, the screen was less sensitive for detecting loci influencing dioxin-induced hydronephrosis (Thomae et al., 2004
). Although our linkage analysis suggested the potential for numerous modifiers of dioxin-induced hydronephrosis, the relatively low LOD scores led us to focus on modifiers of dioxin-induced cleft palate where our screen was more sensitive. We identified two loci that modify sensitivity to dioxin-induced cleft palate. The most potent modifier maps to chromosome 3 and has been designated Cmt1, for "chemically mediated teratogenesis." A weaker modifier maps to chromosome 12 and has been tentatively designated Cmt2.
The Cmt1 Locus and Candidate Genes on Chromosome 3. A number of genes map within the Cmt1 region: Fgf, Il7, Glrb, Fgg, Tshb, Amy1, Egf, Adh7, Car1, and Ptger3. The Fgf locus is the closest to Cmt1 and has been implicated in normal palatogenesis. The Fgf locus encodes the fibroblast growth factor which is highly expressed in the developing mammalian palate and has been suggested to play an important role in epithelial-mesenchymal interactions that dictate fusion and maturation of the developing palate (Lee et al., 2001
). In particular, the fibroblast growth factors have been shown to influence the activity of transforming growth factor
-3 (TGF
3), a regulator of apoptosis and epithelial-to-mesenchymal transdifferentiation at the medial edge of the developing palatal epithelium (Britto et al., 2002
). An interaction between Fgf and Tgf
3 has been suggested to explain a unique pathological mechanism for the cleft palate phenotype exhibited in human Apert syndrome (Britto et al., 2002
). We find the link to the TGF
3 signaling to be interesting, given our recent observation that dioxin's effects on the medial epithelial edge of the palate are remarkably similar to those observed in mice null for TGF
3 expression (Thomae et al., 2005
).
The Cmt2 Locus on Chromosome 12. Although the identification of the Cmt2 locus is only tentative, it is worth noting that it is near the Ahr locus. It is also noteworthy that the B6 and CBA mouse strains are polymorphic at Ahr, harboring distinct Ahrb1 and Ahrb2 alleles, respectively (Poland et al., 1994
). Cloning studies have revealed three b alleles of the murine Ahr, differing by eight point mutations in the common open reading frame and by additional sequences at the carboxyl end (Ema et al., 1994
; Poland et al., 1994
). The alleles, Ahrb1 (
95 kDa), Ahrb2 (
104 kDa), and Ahrb3 (
105 kDa), encode proteins of slightly different size (Poland et al., 1994
). Thus, although the receptors have been reported to bind dioxin with similar affinity, these proteins are of slightly different molecular mass and may display differential expression levels, stability, or transcriptional potency (Ema et al., 1994
; Poland and Glover, 1994
). Although very preliminary, these data suggest the possibility that subtle differences in Ahr alleles could play a role in differential sensitivity to cleft palate.
Comparison with Other Genome-Scans for Clefting Modifiers. Before this work, two genome-wide scans have been performed using mouse models to identify genes and loci that play a role in cleft lip and cleft palate formation. One screen used a spontaneous cleft lip phenotype in the sensitive A/WySnJ and resistant B6 mouse strains (Juriloff et al., 2001
). This screen identified two loci on chromosome 13, designated Clf1 and Clf2, that segregated with spontaneous cleft lip susceptibility. A second genome scan used phenytoin and 6-aminonicotinamide to induce cleft lip and cleft palate, respectively, in the AXB and BXA set of recombinant inbred mouse strains (Diehl and Erickson, 1997
). This screen identified 16 susceptibility regions. It is noteworthy that the region on chromosome 12 identified in our screen comaps to a region identified in a screen for modifier loci of 6-aminonicotinamide induced cleft palate. This result may implicate the locus on chromosome 12 as an important modifier of sensitivity to a broad spectrum of teratogenic chemicals.
| Conclusion |
|---|
|
|
|---|
| Acknowledgements |
|---|
| Footnotes |
|---|
Article, publication date, and citation information can be found at http://molpharm.aspetjournals.org.
ABBREVIATIONS: dioxin, 2,3,7,8-tetrachlorodibenzo-p-dioxin; B6, C57BL/6J; CBA, CBA/J; PCR, polymerase chain reaction; SSLP, simple sequence length polymorphism; LOD, logarithm of the odds (to the base 10); TGF, transforming growth factor.
Address correspondence to: Christopher A. Bradfield, McArdle Laboratory for Cancer Research, 1400 University Avenue, Madison, WI 53706-1599. E-mail: bradfield{at}oncology.wisc.edu
| References |
|---|
|
|
|---|
Abbott BD and Birnbaum LS (1991) TCDD exposure of human embryonic palatal shelves in organ culture alters the differentiation of medial epithelial cells. Teratology 43: 119-132.[CrossRef][Medline]
Anderson YB, Jackson JA, and Birnbaum LS (1993) Maturational changes in dermal absorption of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in Fischer 344 rats. Toxicol Appl Pharmacol 119: 214-220.[CrossRef][Medline]
Bank PA, Yao EF, Phelps CL, Harper PA, and Denison MS (1992) Species-specific binding of transformed Ah receptor to a dioxin responsive transcriptional enhancer. Eur J Pharmacol 228: 85-94.[Medline]
Becher H and Flesch-Janys D (1998) Dioxins and furans: epidemiologic assessment of cancer risks and other human health effects. Environ Health Perspect 106: 623-624.
Bilger A, Bennett LM, Carabeo RA, Chiaverotti TA, Dvorak C, Liss KM, Schadewald SA, Pitot HC, and Drinkwater NR (2004) A potent modifier of liver cancer risk on distal mouse chromosome 1: linkage analysis and characterization of congenic lines. Genetics 167: 859-866.
Botto LD and Khoury MJ (2001) Commentary: facing the challenge of gene-environment interaction: the two-by-four table and beyond. Am J Epidemiol 153: 1016-1020.
Brennan P (2002) Gene-environment interaction and aetiology of cancer: what does it mean and how can we measure it? Carcinogenesis 23: 381-387.
Britto JA, Evans RD, Hayward RD, and Jones BM (2002) Toward pathogenesis of Apert cleft palate: FGF, FGFR and TGF beta genes are differentially expressed in sequential stages of human palatal shelf fusion. Cleft Palate Craniofac J 39: 332-340.[CrossRef][Medline]
Bunger MK, Moran SM, Glover E, Thomae TL, Lahvis GP, Lin BC, and Bradfield CA (2003) Resistance to 2,3,7,8-tetrachlorodibenzo-p-dioxin toxicity and abnormal liver development in mice carrying a mutation in the nuclear localization sequence of the aryl hydrocarbon receptor. J Biol Chem 278: 17767-17774.
Churchill GA and Doerge RW (1994) Empirical threshold values for quantitative trait mapping. Genetics 138: 963-971.[Abstract]
Cooper RS (2003) Gene-environment interactions and the etiology of common complex disease. Ann Intern Med 139: 437-440.
Couture LA, Harris MW, and Birnbaum LS (1990) Characterization of the peak period of sensitivity for the induction of hydronephrosis in C57BL/6N mice following exposure to 2,3,7, 8-tetrachlorodibenzo-p-dioxin. Fundam Appl Toxicol 15: 142-150.[CrossRef][Medline]
Diehl SR and Erickson RP (1997) Genome scan for teratogen-induced clefting susceptibility loci in the mouse: evidence of both allelic and locus heterogeneity distinguishing cleft lip and cleft palate. Proc Natl Acad Sci USA 94: 5231-5236.
Dolwick KM, Swanson HI, and Bradfield CA (1993) In vitro analysis of Ah receptor domains involved in ligand-activated DNA recognition. Proc Natl Acad Sci USA 90: 8566-8570.
Ema M, Ohe N, Suzuki M, Mimura J, Sogawa K, Ikawa I, and Fujii-Kuriyama Y (1994) Dioxin binding activities of polymorphic forms of mouse and human aryl hydrocarbon receptors. J Biol Chem 269: 27337-27343.
Hamm JT, Sparrow BR, Wolf D, and Birnbaum LS (2000) In utero and lactational exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin alters postnatal development of seminal vesicle epithelium. Toxicol Sci 54: 424-430.
Harper PA, Giannone JV, Okey AB, and Denison MS (1992) In vitro transformation of the human Ah receptor and its binding to a dioxin response element. Mol Pharmacol 42: 603-612.[Abstract]
Jain S, Maltepe E, Lu MM, Simon C, and Bradfield CA (1998) Expression of ARNT, ARNT2, HIF1 alpha, HIF2 alpha and Ah receptor mRNAs in the developing mouse. Mech Dev 73: 117-123.[CrossRef][Medline]
Juriloff DM, Harris MJ, and Brown CJ (2001) Unravelling the complex genetics of cleft lip in the mouse model. Mammalian Genome 12: 426-435.
Lee GH, Bugni JM, Obata M, Nishimori H, Ogawa K, and Drinkwater NR (1997) Genetic dissection of susceptibility to murine ovarian teratomas that originate from parthenogenetic oocytes. Cancer Res 57: 590-593.
Lee S, Crisera CA, Erfani S, Maldonado TS, Lee JJ, Alkasab SL, and Longaker MT (2001) Immunolocalization of fibroblast growth factor receptors 1 and 2 in mouse palate development. Plast Reconstr Surg 107: 1776-1784.[CrossRef][Medline]
Loertscher JA, Lin TM, Peterson RE, and Allen-Hoffmann BL (2002) In utero exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin causes accelerated terminal differentiation in fetal mouse skin. Toxicol Sci 68: 465-472.
Lystig TC (2003) Adjusted P values for genome-wide scans. Genetics 164: 1683-1687.
Mastroiacovo P, Spagnolo A, Marni E, Meazza L, Bertollini R, Segni G, and Borgna-Pignatti C (1988) Birth defects in the Seveso area after TCDD contamination. J Am Med Assoc 259: 1668-1672.[Abstract]
Mimura J, Yamashita K, Nakamura K, Morita M, Takagi TN, Nakao K, Ema M, Sogawa K, Yasuda M, Katsuki M, et al. (1997) Loss of teratogenic response to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in mice lacking the Ah (dioxin) receptor. Genes Cells 2: 645-654.[Abstract]
Murray JC (2002) Gene/environment causes of cleft lip and/or palate. Clin Genet 61: 248-256.[CrossRef][Medline]
Pitot HC, Goldsworthy T, Campbell HA, and Poland A (1980) Quantitative evaluation of the promotion by 2,3,7,8-tetrachlorodibenzo-p-dioxin of hepatocarcinogenesis from diethylnitrosamine. Cancer Res 40: 3616-3620.
Poland A and Glover E (1973) Studies on the mechanism of toxicity of the chlorinated dibenzo-p-dioxins. Environ Health Perspect 5: 245-251.[Medline]
Poland A and Glover E (1980) 2,3,7,8,-Tetrachlorodibenzo-p-dioxin: segregation of toxicity with the Ah locus. Mol Pharmacol 17: 86-94.
Poland A and Knutson JC (1982) 2,3,7,8-Tetrachlorodibenzo-p-dioxin and related halogenated aromatic hydrocarbons: examination of the mechanism of toxicity. Annu Rev Pharmacol Toxicol 22: 517-554.[CrossRef][Medline]
Poland A, Palen D, and Glover E (1994) Analysis of the four alleles of the murine aryl hydrocarbon receptor. Mol Pharmacol 46: 915-921.[Abstract]
Robinson S, Clothier B, Akhtar R, Yang A, Latour I, Van Ijperen C, Festing M, and Smith A (2002) Non-AhR gene susceptibility loci for porphyria and liver injury induced by the interaction of dioxin with iron overload in mice. Mol Pharmacol 61: 674-681.
Rogan WJ, Gladen BC, Hung K-L, Koong S-L, Shih L-Y, Taylor JS, Wu Y-C, Yang D, Ragan NB, and Hsu C-C (1988) Congenital poisoning by polychlorinated biphenyls and their contaminants in Taiwan. Science (Wash DC) 241: 334-336.
Sambrook J, Fritsch EF, and Maniatis T (1989) Molecular Cloning: A Laboratory Manual, pp 916, Cold Spring Harbor Laboratory Press, Woodbury, NY.
Stockbauer JW, Hoffman RE, Schramm WF, and Edmonds LD (1988) Reproductive outcomes of mothers with potential exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin. Am J Epidemiol 128: 410-419.
Thomae TL, Glover E, and Bradfield CA (2004) A maternal Ahr null genotype sensitizes embryos to chemical teratogenesis. J Biol Chem 279: 30189-30194.
Thomae TL, Stevens EA, and Bradfield CA (2005) Transforming growth factor-
3 restores fusion in palatal shelves exposed to 2,3,7,8-tetrachlorodibenzo-p-dioxin. J Biol Chem 280: 12742-12746.
Wolfe WH, Michalek JE, Miner JC, Rahe AJ, Moore CA, Needham LL, and Patterson DG Jr (1995) Paternal serum dioxin and reproductive outcomes among veterans of Operation Ranch Hand. Epidemiology 6: 17-22.[Medline]
| |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||