Altered operant responding for motor reinforcement and the determination of benchmark doses following perinatal exposure to low-level 2,3,7,8-tetrachlorodibenzo-p-dioxin

被引:43
作者
Markowski, VP
Zareba, G
Stern, S
Cox, C
Weiss, B
机构
[1] Univ Rochester, Sch Med & Dent, Dept Environm Med, Rochester, NY 14642 USA
[2] Univ Rochester, Sch Med & Dent, Dept Biostat, Rochester, NY 14642 USA
[3] Univ So Maine, Dept Psychol, Portland, ME 04103 USA
关键词
benchmark dose; estrous cycle; operant behavior; prenatal exposure; TCDD; wheel running;
D O I
10.2307/3455037
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Pregnant Holtzman rats were exposed to a single oral dose of 0, 20, 10, or 180 ng/kg 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on the 18th day of gestation. Their adult female offspring were trained to respond on a lever for brief opportunities to run in specially designed running wheels. Once they had begun responding on a fixed-ratio 1 (FR1) schedule of reinforcement, the fixed-ratio requirement for lever pressing was increased at five-session intervals to values of FR2, FR5, FR10, FR20, and FR30. We examined vaginal cytology after each behavior session to track estrous cyclicity. Under each of the FR values, perinatal TCDD exposure produced a significant dose-related reduction in the number of earned opportunities to run, the lever response rate, and the total number of revolutions in the wheel. Estrous cyclicity was not affected. Because of the consistent dose-response relationship at all FR values, we used the behavioral data to calculate benchmark doses based on displacements from modeled zero-dose performance of 1% (ED01) and 10% (ED10), as determined by a quadratic fit to the dose-response function. The mean ED10 benchmark dose for earned run opportunities was 10.13 ng/kg with a 95% lower bound of 5.77 ng/kg. The corresponding ED01 was 0.98 ng/kg with a 95% lower bound of 0.83 ng/kg. The mean ED10 for total wheel revolutions was calculated as 7.32 ng/kg with a 95% lower bound of 5.41 ng/kg. The corresponding ED01 was 0.71 ng/kg with a 35% lower bound of 0.60. These values should be viewed from the perspective of current human body burdens, whose average value, based on TCDD toxic equivalents, has been calculated as 13 ng/kg.
引用
收藏
页码:621 / 627
页数:7
相关论文
共 55 条
[1]   DEVELOPMENTAL EXPRESSION OF 2 MEMBERS OF A NEW CLASS OF TRANSCRIPTION FACTORS .1. EXPRESSION OF ARYL-HYDROCARBON RECEPTOR IN THE C57BL/6N MOUSE EMBRYO [J].
ABBOTT, BD ;
BIRNBAUM, LS ;
PERDEW, GH .
DEVELOPMENTAL DYNAMICS, 1995, 204 (02) :133-143
[2]  
Altman J, 1995, ATLAS PRENATAL RAT B
[3]  
[Anonymous], 1985, INTRO GRAPHICAL METH
[4]  
Barnett S., 1975, The rat
[5]  
BEACH FA, 1956, NEBRASKA S MOTIVATIO, V4, P1
[6]   THE INFLUENCE OF ESTROUS-CYCLE AND INTRASTRIATAL ESTRADIOL ON SENSORIMOTOR PERFORMANCE IN THE FEMALE RAT [J].
BECKER, JB ;
SNYDER, PJ ;
MILLER, MM ;
WESTGATE, SA ;
JENUWINE, MJ .
PHARMACOLOGY BIOCHEMISTRY AND BEHAVIOR, 1987, 27 (01) :53-59
[7]   REPRODUCTIVE TOXICITY OF 2,3,7,8-TETRACHLORODIBENZO-P-DIOXIN IN MALE-RATS - DIFFERENT EFFECTS OF IN-UTERO VERSUS LACTATIONAL EXPOSURE [J].
BJERKE, DL ;
PETERSON, RE .
TOXICOLOGY AND APPLIED PHARMACOLOGY, 1994, 127 (02) :241-249
[8]   DOPAMINE FUNCTIONS IN APPETITIVE AND DEFENSIVE BEHAVIORS [J].
BLACKBURN, JR ;
PFAUS, JG ;
PHILLIPS, AG .
PROGRESS IN NEUROBIOLOGY, 1992, 39 (03) :247-279
[9]  
Crowder MJ, 1990, ANAL REPEATED MEASUR
[10]   COMPARISONS OF ESTIMATED HUMAN-BODY BURDENS OF DIOXINLIKE CHEMICALS AND TCDD BODY BURDENS IN EXPERIMENTALLY EXPOSED ANIMALS [J].
DEVITO, MJ ;
BIRNBAUM, LS ;
FARLAND, WH ;
GASIEWICZ, TA .
ENVIRONMENTAL HEALTH PERSPECTIVES, 1995, 103 (09) :820-831