Reproductive, neuroendocrine, and immune consequences of acute exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin in the Siberian hamster

被引:11
作者
Yellon, SM [1 ]
Singh, D
Garrett, TM
Fagoaga, OR
Nehlsen-Cannarella, SL
机构
[1] Loma Linda Univ, Sch Med, Ctr Perinatal Biol, Loma Linda, CA 92350 USA
[2] Loma Linda Univ, Sch Med, Dept Physiol, Loma Linda, CA 92350 USA
[3] Loma Linda Univ, Sch Med, Dept Pathol, Loma Linda, CA 92350 USA
[4] Loma Linda Univ, Med Ctr, Ctr Immunol, Loma Linda, CA 92350 USA
[5] MCP Ind Inc, Corona, CA 91718 USA
关键词
circadian rhythm; melatonin; pregnancy; reproductive immunology;
D O I
10.1095/biolreprod63.2.538
中图分类号
Q [生物科学];
学科分类号
07 ; 0710 ; 09 ;
摘要
The present study tested the hypothesis that acute treatment with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) impairs fertility, disrupts the nocturnal melatonin rhythm, and suppresses lymphocyte function. Adult Siberian hamsters administered 2 or 100 mu g TCDD/kg body weight/0.2 ml sesame oil had a delayed latency to first litter and an increased adult mortality compared to hamsters given 0.1 mu g/kg or vehicle. Within 75 days of TCDD treatment, full reproductive capabilities were achieved. Moreover, the nocturnal melatonin rhythm was not disrupted in adults administered TCDD or in their progeny. Lymphocyte activity varied with respect to time of day and treatment. Lymphocyte proliferation was enhanced at night irrespective of TCDD treatment; during the day, 2 wk after the 2-mu g/kg treatment, blastogenesis was reduced compared to that in the 0.1-mu g/kg group or in vehicle-treated controls. In contrast, TCDD did not affect the mixed lymphocyte reaction in response to allogeneic antigen when assessed at 2 and 20 wk post-treatment. Thus, findings indicate that TCDD produced acute effects on fertility, mortality, and systemic lymphocyte proliferation, but long-lasting effects on specific aspects of reproductive, neuroendocrine, and immune cell functions were not observed.
引用
收藏
页码:538 / 543
页数:6
相关论文
共 34 条
[1]  
Arendt J, 1995, MELATONIN MAMMALIAN, P110
[2]  
BARTNESS TJ, 1993, J PINEAL RES, V15, P161
[3]   LEVELS OF PCDDS AND PCDFS IN ADIPOSE-TISSUE OF OCCUPATIONALLY EXPOSED WORKERS [J].
BECK, H ;
ECKART, K ;
MATHAR, W ;
WITTKOWSKI, R .
CHEMOSPHERE, 1989, 18 (1-6) :507-516
[4]   THE MECHANISM OF DIOXIN TOXICITY - RELATIONSHIP TO RISK ASSESSMENT [J].
BIRNBAUM, LS .
ENVIRONMENTAL HEALTH PERSPECTIVES, 1994, 102 :157-167
[5]  
BOYUM A, 1977, LYMPHOLOGY, V10, P71
[6]  
BRADLEY LM, 1980, SELECTED METHODS CEL, P162
[7]   REPRODUCTIVE TOXICITY AND TOXICOKINETICS OF 2,3,7,8-TETRACHLORODIBENZO-PARA-DIOXIN .2. PROBLEM OF PATERNALLY-MEDIATED ABNORMALITIES IN THE PROGENY OF RAT [J].
CHAHOUD, I ;
KROWKE, R ;
BOCHERT, G ;
BURKLE, B ;
NEUBERT, D .
ARCHIVES OF TOXICOLOGY, 1991, 65 (01) :27-31
[8]   Treatment of rats during pubertal development with 2,3,7,8-tetrachlorodibenzo-p-dioxin alters both signaling kinase activities and epidermal growth factor receptor binding in the testis and the motility and acrosomal reaction of sperm [J].
El-Sabeawy, F ;
Wang, SY ;
Overstreet, J ;
Miller, M ;
Lasley, B ;
Enan, E .
TOXICOLOGY AND APPLIED PHARMACOLOGY, 1998, 150 (02) :427-442
[9]   EMBRYOTOXIC EFFECTS OF 2,3,7,8 TETRACHLORODIBENZO-PARA-DIOXIN ADMINISTERED TO FEMALE RATS BEFORE MATING [J].
GIAVINI, E ;
PRATI, M ;
VISMARA, C .
ENVIRONMENTAL RESEARCH, 1983, 31 (01) :105-110
[10]   CONTAMINANTS IN FISHES FROM GREAT LAKES-INFLUENCED SECTIONS AND ABOVE DAMS OF 3 MICHIGAN RIVERS .3. IMPLICATIONS FOR HEALTH OF BALD EAGLES [J].
GIESY, JP ;
BOWERMAN, WW ;
MORA, MA ;
VERBRUGGE, DA ;
OTHOUDT, RA ;
NEWSTED, JL ;
SUMMER, CL ;
AULERICH, RJ ;
BURSIAN, SJ ;
LUDWIG, JP ;
DAWSON, GA ;
KUBIAK, TJ ;
BEST, DA ;
TILLITT, DE .
ARCHIVES OF ENVIRONMENTAL CONTAMINATION AND TOXICOLOGY, 1995, 29 (03) :309-321