Brain asymmetry as a potential biomarker for developmental TCDD intoxication: a dose-response study

Brain Asymmetry as a Potential Biomarker for Developmental TCDD Intoxication: A Dose-Response Study Diane S. Henshel, J. William Martin, and Jamie C. DeWitt School of Public and Environmental Affairs, Indiana University, Bloomington, Indiana 47405 USA

Previous studies have indicated tit in evo exposure to 2,3,78 ra ddiio: (TCDD) and related compounds is correlated with the development of o mmetic bra ce betwn the two hals of the foreb an dite This asmmetry is m Isted as a d on, co tecta. Previosy, onlildli s eagle) hadbe s of id response_ nh ferences ha bee creaewihteldsopoyhoiatddbnopdontoceqvAlec . We dt of in + facors (fs ine im h s nes (hen t mod (chickrerposure to TCDD on the brai toout delm et in a sensitive en). Embryos from chickn egg (Gan galw) injected with one of sevral doses of TCDD or vehicle control wre sacrificed afer 9, 11, 13, 15, 17, or 20 days of incion, or cubaed to 24 hr or att;3 we pos h M of botihi; ha and d either

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both the and severity of brain aymmetr ob d at all agesmeasured; and 4) the asymmetry was easuble in embryonic brains at an age when the braincase was a thin, flexible ida9), implying -tht the effect of TCDD was direct on .the developing brain Layer (embry-o Case. Key aymet, brindvpment di and not i diect Rssn , embryo, T 105:718-725 (1997)

Polychlorinated dibenzo-p-dioxins (PCDDs), polychlorinated dibenzofurans (PCDFs) and polychlorinated biphenyls (PCBs) are virtually ubiquitous environmental pollutants that are known to bioconcentrate in animal tissue, biomagnify up the food chain, cross the placenta into mammalian embryos, and be deposited into the eggs of egg-laying animals (1-3). These compounds are part of the broader class of compounds known as polyhalogenated polycyclic aromatic hydrocarbons (PHAHs), the most acutely toxic of which is 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) (3). TCDD in particular, and PCDDs, PCDFs, and PCBs in general, are known to be embryotoxic and teratogenic,

causing abnormalities in the palate or beak, heart, and kidney, as well as causing general depression of embryonic growth (1,4,5). In addition, these compounds are linked to abnormalities in the development of the nervous system. PCBs, for example, have been linked to changes in the biochemical development of parts of the nervous system and nervous system-related tissue (6). PCBs, PCDFs, and PCDDs, as well as other organochlorines, have all been linked to behavioral changes in a wide variety of animals (2,6-8). Indications from the biochemical studies, however, are that some of the nervous system effects of these compounds may not be mediated by the laterally

substituted, coplanar compounds prototypically represented by TCDD (6). Previous studies from our laboratory have indicated that in ovo exposure to TCDD and related compounds is also correlated with the development of brains that are grossly asymmetric (9-12. This asymmetry is manifested as differences in several parameters between the left and right halves of the forebrain and is also evident in the tecta, again as a left-right difference. Previously, only wildlife species (heron, cormorant, eagle) have been shown to manifest this response (9-12). In the wildlife studies, the frequency and degree of left-right interhemispheric differences had been correlated with the levels of PCDDs and/or TCDD toxic equivalents in eggs from the same nest (heron, cormorant) or in the blood (eagle). As environmentally exposed wildlife species are virtually always exposed to a mixture of compounds, the question remained whether the asymmetry was being induced by the TCDD-like compounds or by some other compounds that coexisted Address correspondence to D.S. Henshel, School of Public and Environmental Affairs, 10,h and Fee Lane, Room 340 SPEA Building, Indiana University, Bloomington, IN 47405 USA. This work was supported by the Wildlife Toxicology Fund (World Wildlife Fund, Canada), the Sustainable Development Research Initiative of British Columbia, NSERC (Canada), the British Columbia Ministry (Environment), the Arde Bulova Foundation, and a Biological Research Support Grant. J.W.M. and J.C.D. were supported by research assistantships from the School of Public and Environmental Affairs, Indiana University. Received 16 October 1996; accepted 3 March 1997.

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Figure 1. Drawings of the chicken brain from the (A) dorsal and (B) lateral aspects illustrating the major brain regions and the individual measurements made. Abbreviations: A, angle, D, depth; H, height; TD, tectal depth (tectal width not shown); C, cerebrum (telencephalon); T, tectum; Cb, cerebellum; SC, spinal cord; B, brain stem; OB, olfactory bulb; W, width; Hy, hypothalanus.

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Volume 105, Number 7, July 1997 * Environmental Health Perspectives

Articles * Brain asymmetry as a biomarker of TCDD exposure

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Environmental Health Perspectives * Volume 105, Number 7, July 1997

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720

Volume 105, Number 7, July 1997 * Environmental Health Perspectives

Articles * Brain asymmetry as a biomarker of TCDD exposure

with the TCDD-like compounds in the environment. In addition, there was a question ofwhen during embryonic development the asymmetry began to develop and whether, once developed, the asymmetry remained evident. Finally, it was not clear whether TCDD affected the brain directly or whether the gross brain malformation was induced indirectly via an effect on the braincase. Therefore, we initiated this developmental, dose-response, controlled laboratory study to determine whether TCDD alone could induce brain asymmetries similar to those observed in wildlife species contaminated in the wild with TCDD and TCDDlike compounds.

Methods Fertile white leghorn chicken (Gallus gallus) eggs were injected before the start of incubation with one of several doses of TCDD [10, 100, 300, or 1000 pg TCDD/g egg (= parts per trillion or ppt) for the embryos sacrificed before hatching and 10, 30, 60, 100, 300, or 1000 ppt for the embryos allowed to hatch] or with vehicle control

(safflower oil). TCDD was obtained from Ultra Scientific (Providence, RI) predissolved to a known concentration in safflower oil. Injection volumes were normalized to the weight of the individual eggs: 0.1 p1 of TCDD or oil per gram of egg was injected through a hole in the shell above the air sac using a Hamilton syringe. The hole in the shell was subsequently sealed with paraffin. The eggs were incubated at 37.5°C dry bulb and 300C wet bulb (approximately 56% humidity) until sacrifice or hatch. Embryos were sacrificed at embryonic days (E; incubation days) E9, E11, E13, E15, E17, and E20. All eggs were removed from the incubator at the same time of day that they had initially been placed in the incubator. All embryos were sacrificed in random order. Other injected eggs were incubated until hatching, and the hatchlings were sacrificed either within 24 hr of hatching or at 3 weeks post-hatch. Hatchlings raised to 3 weeks were raised in groups including one of each dose, housed by group in 1 1/2 ft (W) x 2 ft (D) x 1 1/2 ft (H) plastic cages, warmed with a 100 (week 1) or 60 watt

(weeks 2-3) light bulb. Food and water provided ad libitum. The birds were individually coded with permanent marker

were

on their feathers.

At sacrifice, the older embryos (E13, E1 5, E17, E20), hatchlings, and 3-week-old

birds were all anesthetized with phenobarbital and either perfused through the heart with phosphate buffered saline (PBS, pH 7.4) followed by 4% paraformaldehyde made in PBS (PARA, pH 7.4) or were sacrificed with phenobarbital and then dissected rapidly to remove the brains. The dissected brains were then immersion-fixed in 4°C PARA. Sacrifice method was by injection set across all doses and controls, with injection sets of three birds each per dose and by age of sacrifice. The younger embryos were sacrificed by immersion in cold PARA (40C). All embryos were stored in PARA at 40C until shortly before necropsy, when they were transferred to PBS (4°C) with 0.625% sodium azide added to prevent mold growth. All animals were handled following protocols approved by the University of British Columbia (UBC) Animal Care

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Figure 4. Mean symmetry differences in brain of post-hatch chicks averaged by age and dose of 2,3,7,8-tetrachlorodibenzo-p-dioxin. P21, postnatal day 21. Measurements include width, angle, depth, and height of the forebrain and width and depth of the tectum (see Fig.1 ).

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Articles Henshel et al. -

Committee, and handling of hazardous materials was approved by the UBC Occupational Safety and Health office. Six measurements were made on each brain, four on the forebrain region and two on the tecta. The tectal depth and forebrain depth were measured from the lateral aspect of the brain, while the tectal width was measured from the ventral aspect of the brain. The other three measurements (height, width, angle) were all made from the dorsal aspect of the forebrain. The four forebrain measurements (illustrated in Fig. 1) were mediolateral width just rostral to the pineal (width), mediolateral measurement from the same central point just rostral to the pineal and out to the lateral edge at a 350 angle from the horizontal defined by the width measurement (angle), rostral-caudal length from mid-wulst (the dorsorostral forebrain protrusion) to the caudal-most part of the forebrain on that rostrocaudal axis (height), and the dorsoventral depth of the brain at the point where the hypothalamus meets the telencephalon (at the level of the pre-optic area, depth). Brains were measured as described previously (7,8), except that the tecta were also measured for this study. Briefly, each measurement was made using a ruler propped parallel to the surface of the brain. The eye was centered over the center of the brain for the width and angle measurements and over the center of the area being measured for the other measurements. All measurements were made two times. If the measurements did not agree, each measurement was made an additional three times and the results were averaged. The measurements reported here represent the difference between left and right halves of the brain and are all presented as measurements from the left side of the brain minus measurements from the right side of the brain. We regressed each measurement on TCDD concentration and on age using the Regression and General Linear Models procedures in SAS (PROC REG, PROC GLM, SAS Institute, Cary, NC). Significance was determined using a p-value of 0.05. Probit analysis was also performed using SAS (PROC PROBIT) to estimate the ED10s (the dose at which a 10% population response is elicited) and the median effective doses (ED50s) for the observed asymmetry. The standard deviation (SD) reported for the ED50 is the standard deviation (a) reported by SAS for the average (the p or the ED50). No such values were given for the EDlos by SAS; therefore, no SDs were reported for the ED10s. Further, 95% fiducial limits are not incuded in this paper as they were inconsistently reported by SAS, depending on the sample sizes for each age and dose.

722

Results

all of the measurements, in general. The R2 values for the two tectal measurements tended to be intermediate between the width, angle, and depth measurements and the height measurement, although the R2 for tectal depth was similar to the R2- for the width, angle, and depth measurements. When evaluated by age and TCDD concentration, all six measurements were significant at the 0.0001 level. The regression equations (Eq. 1-6) in the shaded box describe the relationships between each measurement, TCDD, and age; p-values for the individual parameters within each equation are listed below each parameter.

TCDD clearly affected both the frequency and the degree of brain symmetry in a dosedependent manner (Fig. 2-5). To give an indication of relative variability in the data, the sample size and standard error of the means are listed in Table 1 for the angle measurement (Fig. 2 and 4). Noticeably, the TCDD-induced forebrain asymmetry was only evident at the lowest dose (10 ppt) in the E13 and older animals. However, the tectal asymmetry was already present in the brains exposed to the lowest dose of TCDD at E9. It is also clear from these data that the asymmetry persisted to at least 3 weeks post-hatch, through a period of rapid posthatching growth. Similarly, although the forebrain measurements were only made from the dorsal aspect, the brain asymmetry was noticeable from both the dorsal and the ventral aspects of the brain (Fig. 6). Table 2 lists the PROBIT determined EDlos and ED50s by age and measurement. Of the four forebrain measurements, width, angle, depth and height, the first three had the highest R2 values when regressed against age and TCDD concentration (see equations below). The height measurements had the lowest R2 values of

Discussion TCDD injected at the start of incubation clearly induces brain asymmetry in chicken embryos in a dose-dependent manner. The asymmetry is manifested as a consistent left-right hemispheric difference in both the forebrain and the tectum and is present after the initial formation of these brain regions. Chickens have a 21-day incubation period. Chicken brains (and avian brains in general) do not develop evenly throughout development (Fig. 7). During early incubation (organogenesis), the chicken

Table 1. Standard error of the mean and sample size for angle difference measurementsa Dose (ppt) 1000 10 30 60 100 300 0 Age ND ND 0.13 (8) 0 (9) 0 (8) 0.11(3) E9 0.11(5) 0.14 (4) 0 (10) ND ND 0 (3) Eli 0.07 (14) 0.13 (10) ND ND 0.12 (8) 0.12 (10) 0.14 (4) 0 (13) 0.1 (12) E13 0.1 (11) ND ND 0.18(8) 0.2(9) 0.14(4) E15 0(15) ND ND 0.18 (2) E17 0 (13) 0.13 (6) 0.18 (9) 0.35 (7) ND ND 0.2 (7) NS (1) E20 0 (8) 0.1 (6) P0 0 (22) 0.07 (22) 0.13 (7) 0.13 (8) 0.13 (18) 0.11 (5) NS 0.24 (4) 0 (2) NS P21 0.06 (4) 0.13 (7) 0 (5) 0 (5) Abbreviations: E, embryonic day or incubation day; P, postnatal day; ND, not done; NS, no survivors. aValues in parentheses are sample size.

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Volume 105, Number 7, July 1997 * Environmental Health Perspectives

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Articles Brain asymmetry as a biomarker of TCDD exposure -

brain first segments into the prosencephal_ 0ppt _ ic, diencephalic, mesencephalic, and lnOppt _30Oppt rhombencephalic regions (listed from rostral to caudal). By E3-E4, the two forebrain L_ 300ppt hemispheres (the telencephalon) bubble out in the prosencephalic region of the neural tube. By E4, the mesencephalon begins to develop as an enlarging central 0.909 0.8 _ 5 structure. The partitioning of the mesen0 > 0.7 cephalon into two (left and right) tectal 0.60 prominances begins about E5. By E7 or 0 06 c!i 0. O5i|I|| E8, the dominant outgrowths of the brain 0C 0.5 0.4 LO.110.4 IlI!lIi are the tecta, caudal to the telencephalic 0.3 0.3 I _ outgrowths. The telencephalic hemispheres 0' 0. begin to appear more prominent around E9 or E10 so that, by E12, the forebrain P21 P21 Hatchling HIatchling hemispheres are almost equal in size to the Age (days) Age (days) tectal outgrowths. By E16 or E18, the forebrain hemispheres have begun to dwarf the more caudal tecta (13,14). Given the difficulty of dissecting out early embryonic brains, we only made asymmetry measurements on brains from E9 embryos and older. By this age, even though the telencephalic hemispheres are still very small and undeveloped, there is clear 0.9 fore~~~~~~~~~~~~~~~~~~0.9 brain asymmetry induced by the higher 0.8 0.8 ~.0.7 0.7 doses of TCDD used and tectal asymmetry 0.8 0.8 at all doses of TCDD used. Once the fore0.5 -r =ra 0.5 i brain hemispheres begin to develop again, in 0.4 e 0.4 0.4 the latter half of the 21-day incubation periU~~~~~~~~~~~~~~~~~.3 0.303 od, the brain asymmetry is also manifested 0.2 0.2 0.1 0.1 at even the lower doses of TCDD. Once the 0 0 brain has started to develop asymmetrically, P21 H P2 Hatchling evidence from the brains of the hatchling Age (days) Age (days) and 3-week-old birds indicates that the brains remain asymmetrical. Thus, the asymmetry endpoint appears to be increased in sensitivity following and during periods of rapid development of the brain regions affected (forebrain and tecta). Once the asymmetry is present, the brain appears to continue to grow such that the asymmetry 0.9 0.9 remains. This implies that TCDD may be 0.8 0.8 affecting the brain during periods of high * 0.1 0 mitogenic activity and may be differentially = 0.5 inducing increased mitogenesis on the two * 0.5 0.5 -r sides of the brain. The ED1Os (Table 2) con0.4 E 0.4 U. U. 0.3 03 firm this increase in sensitivity in the fore0.2 0.2 brain measurements at the time of the fore0.1 0.1 brain expansion and indicate that the sensi0 0 tivity of the tectal measurements are already P21 P21 Hatchling Hatchling Age (days) Age (days) maximal by E9 (posttectal expansion). These results also suggest that TCDD Figure 5. Proportion of asymmetric brains in post-hatch chicks graphed by age and dose of 2,3,7,8-tetraaffects primarily the brain and not primarily chlorodibenzo-p-dioxin. P21, postnatal day 21. Measurements include width, angle, depth, and height of the forebrain and width and depth of the tectum (see Fig.1 ). the braincase, with a secondary effect on the brain. At E9, the earliest that we have attempted to measure the brain asymmetry, direct effect of TCDD on braincase develpreviously made on several wildlife species the braincase is a very thin, almost memopment (which we have not in any way (great blue herons, double-crested corbrane-like covering over the brain. At this attempted to assess), our results indicate morants, and bald eagles) exposed in ovo in point in development, the braincase is very that there is a direct effect of TCDD on the the wild to a mixture of TCDD-related flexible and appears to present little or no brain as it undergoes rapid development, chemicals, including (depending on the resistance to the brain developing underThese results in TCDD-injected chickstudy) PCDDs, PCDFs, and PCBs neath. Thus, while there may also be a ens are consistent with observations we have (10-12). In each of these studies, the brain lb.

P21

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Articles * Henshel et al.

asymmetry was highly and significantly correlated to either TCDD levels, TCDDtoxic equivalents (TEQs), or some other measure that generally indicates exposure to TCDD-like compounds ethoxyresorufin 0deethylase, an enzyme induced by TCDD exposure and a variety of other environmental contaminants) (15). The present

results in chickens confirm that although other non-TCDD-like congeners may have had an effect on the measured brain asymmetry in the wildlife studies, TCDD alone can induce a developmentally linked gross brain asymmetry in avian brains. Ibis important to correlate this gross brain asymmetry with functional changes in

~B

brain-controlled activity. At this time we do not know specifically which brain-mediated functions (if any) may be affected by this gross dysmorphism, although behavioral studies are ongoing. From previous histological studies we know that the pyriform cortex of the heron hatchlings from a PCDD- and PCDF-contaminated colony was increased in both mediolateral width and cell density (9). The pyriform cortex is associated with the limbic system, a series of structures in the brain that affect emotion and instinctive behavior. In addition, the pyriform cortex is the main cortical area involved in olfactory discrimination and is believed to receive indirect input from the olfactory bulb (16). Olfaction is also generally believed to affect instinctive behaviors. We did not, however, track sidedness in the brains for the initial heron studies and, given how the brains were processed, we can not determine sidedness after the fact. In addition, the pyriform cortex is a thin strip on the outside of the forebrain. The relatively large differences in the left-right hemispheres seen in this study could not be totally attributed to changes in such a thin strip of tissue, nor could any changes in the tecta be directly attributed to changes in the thickness of the pyriform cortex. Future studies are needed to determine which nuclei (an amalgamation of functionally and/or anatomically related neurons) and biochemical markers in the brain are specifically affected by TCDD. REFERENCES

Figure 6. Photographs of embryonic day 13 chicken brains from the ventral (A, B) and dorsal (C, D) aspects illustrating the flattened arc on the left side of the brain (B. D; indicated by arrows) due to in ovo (TCDD) exposure. The TCDD injected chicken brain (300 ppt) is shown in B and D. The noninjected control brain is shown in A and C.

1. Couture LA, Abbott BD, Birnbaum LS. A critical review of the developmental toxicity and teratogenicity of 2,3,7,8-tetrachlorodibenzo-pdioxin: recent advances toward understanding the mechanism. Teratology 42:619-627 (1990). 2. Dahlgren RB, Linder RL. Effects of polychlorinated biphenyls on pheasant reproduction, behavior and survival. J Wildl Manage 35:315-319 (1971). 3. Safe S. Polychlorinated biphenyls (PCBs),

dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), and related compounds: environmental and mechanistic considerations which sup-

Table 2. Probit (log10) determined ED10s and ED50s by age and measurement Tectal Depth Tectal Width Angle Depth Width Height ED50 EDs EDs ED10 ED10 ED10 ED10 EDs ED10 ED b EDs Age ED10a 8.75 127.32 ± 8.08 8.75 127.32 ± 8.08 22.77 107.09 ± 3.35 24.85 89.32 ± 2.71 21.00 168.68 ± 5.08 E9 832.52 1046.20 ± 1.2 58.26 ± 3.51 14.62 87.53 ± 4.04 77.56 95.89 ± 1.18 53.96 164.73 ± 2.39 11.64 Eli 803.38 1000.00 ± 1.19 85.36 103.98 ± 1.17 79 ± 4.24 93.13 ± 4.98 12.39 32.27 131.63 ± 2.99 11.91 82.07 ± 8.92 4.83 56.38 ± 6.8 477.26 ± 33.23 4.97 E13 5.35 2.71 85.15 ± 14.73 10.02 90.93 ± 5.59 6.41 110.25 ± 9.21 6.12 4.72 67.77 ± 8.0 67.83 ± 6.54 806.74 1000.00 ± 1.18 E15 58.9 ± 7.12 62.51 ± 38.52 6.37 0.58 34.91 ± 16.3 1.20 47.93 ± 17.78 15.34 106.38 ± 4.53 496.50 ± 6.62 0.98 E17 44.07 6.44 0.58 90.65 ± 51.3 4.76 111.17 ± 9.31 7.21 241.29 ±15.47 6.44 42.3 ± 4.34 42.3 ± 4.34 6.37 111.17 ± 9.31 E20 9.12 78.78 ± 5.38 4.93 58.71 ± 6.91 7.16 62.28 ± 5.41 247.17 ± 6.44 6.85 79.03 ± 6.74 86.83 ± 5.54 P0 22.70 9.67 2.16 206.97 ± 35.14 18.35 199.72 ± 6.44 1.23 195.93 ± 52.18 P21 0.029 33.75 ± 250.16 16.05 70.69 ± 3.18 196.33 ± 7.14 15.80 Abbreviations: E, embryonic day or incubation day; P, postnatal day; ED10, effective dose eliciting a 10% response; ED50, median effective dose. aNo standard deviation (SD) is given by SAS (SAS Institute, Cary, NC) for the ED10s, therefore no SD is listed.

bp (ED50 a(SD). 724

Volume 105, Number 7, July 1997 * Environmental Health Perspectives

Articles * Brain asymmetry as a biomarker of TCDD exposure

"ig Figure 7. Drawings of the chicken brain from the dorsal aspect between embryonic days 10 and 20, just prior to hatching. Abbreviations: C, cerebrum; T, tectum; Cb, cerebellum; SC, spinal cord. Modified from Romanoff (14). port the development of toxic equivalency factors (TEFs). Crit Rev Toxicol 21:51-88 (1990). 4. Henshel DS, Hehn BM, Vo MT, Steeves JD. A short-term test for dioxin teratogenicity using chicken embryos. In: Environmental Toxicology and Risk Assessment ASTM STP 1216, vol 2 (Gorsuch JW, Dwyer FJ, Ingersoll CG, La Point TW, eds). Philidelphia:American Society of Testing and Materials, 1993;159-174. 5. Henshel DS, Hehn B, Wagey R, Vo M, Steeves JD. Relative sensitivity of chicken embryos to yolk or aircell-injected 2,3,7,8-tetrachlorodibenzo-p-dioxin. Environ Toxicol Chem 16(4):725-732 (1997). 6. Seegal RF, Schantz SL. Neurochemical and behavioral sequelae of exposure to dioxins and PCBs. In: Dioxins and Health (Schecter A, ed). New York:Plenum Press, 1995;409-447.

7. Fox GA, Gilman AP, Peakall DB, Anderka FW. Behavioral abnormalities of nesting Lake Ontario herring gulls. J Wildl Manage 42:477-483 (1978). 8. Moul I. Environmental contaminants, disturbance and breeding failure at a great blue heron colony on Vancouver Island [MSc Thesis]. University of British Columbia, Vancouver, British Columbia, 1990. 9. Henshel DS, ChengKM, Norstrom R, Whitehead P, SteevesJD. Morphometric and histological changes in brains of great blue heron hatchlings exposed to PCDDs: preliminary analyses. In: Environmental Toxicology and Risk Assessment, ASI-M STP 1179 (Landis W, Hughes JS, Lewis MA, eds). Philadelphia:American Society for Testing and Matials 1993;262-277. 10. Henshel DS, Martin JW, Norstrom R,

Whitehead P, Steeves JD, Cheng KM. Morphometric abnormalities in brains of great blue heron hatchlings exposed to PCDDs. Environ Health Perspect 103:61-66 (1995). 11. Henshel DS, Martin JW, Best D, Cheng KM, Elliot JE, Rosentein D, Sikarskie J. Evaluating gross brain asymmetry a potential biomarker for 2,3,7,8-tetrachlorodibenzo-p-dioxin-related neurotoxicity. In: Environmental Toxicology and Risk Assessment: Biomarkers and Risk Assessment, ASTM STP 1306, vol 5 (Bengtson DA, Henshel DS, eds). Philadelphia:American Society for Testing and Materials; 1996;230-238. 12. Henshel DS, Martin JW, Norstrom RJ, Elliott J, Cheng KM, DeWitt JC. Morphometric brain abnormalities in double-crested cormorant chicks exposed to polychlorinated dibenzo-pdioxins, dibenzofurans, and biphenyls. J Great Lakes Res 24(1):11-26 (1997). 13. Hamburger V, Hamilton HL. A series of normal stages in the development of the chick embryo. J Morphology 88:49-92 (1951). 14. Romanoff AL. The Avian Embryo: Stuctural and Functional Development. New York:The Macmillan Company, 1960. 15. Custer TW, Hines RK, Melancon MJ, Hoffman DJ, Wickliffe JK, Bickham JW, Martin JW, Henshel DS. Contaminant concentrations and biomarker response in great blue heron eggs from 10 colonies on the upper Mississippi River, USA. Environ Toxicol Chem 16(2):260-271 (1997). 16. Shepherd, G. Neurobiology. New York.Oxford University Press, 1983.

ANNOUNCING THE

EIGHTH NORTH AMERICAN ISSX MEETING OCTOBER 26-30 1997

A/fEil

HILTON HEAD, SOUTH CAROLINA

SHORT COURSES

ADDITIONAL TOPICS INCLUDE:

Four half-day short courses will be offered, two in the morning and two in the afternoon.

* Susceptibility factors for disease * Chemistry and enzymology of biotransformation * Drug interactions * Alternatives to animal models * Computational models * Transgenic models * Physiological barriers * New technologies for analytical methods

SCIENTIFIC PROGRAM FOCUSING ON Two CENTRAL THEMES

(1) Disposition of Biotechnology Compounds * Peptides, Proteins, Oligomers * Uptake, Clearance, Metabolism * Methods to Evaluate Combinational Libraries (2) Risk Assessment and Safety Evaluation * Chemicals in the Environment * Pharmaceuticals and Foods * Risk Management and Regulation

Environmental Health Perspectives . Volume 105, Number 7, July 1997

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