Shopp G M, McCay J A, Holsapple M P
J Toxicol Environ Health. 1985;15(2):293-304. doi: 10.1080/15287398509530655.
These studies investigated the effects of exposure to chlordimeform (CDM), a formamidine pesticide, on selected in vivo immune parameters in the random bred CD-1 mouse. Further studies were done on the effects of this compound on the in vitro PFC response in C57BL/6 mice. Acute and 14-d exposure to CDM via the i.p. route resulted in a decrease in IgM antibody-forming (plaque-forming) cells (PFC) directed at the sheep red blood cell (sRBC) antigen when measured 4 d after i.p. immunization. This suppression was seen at doses as low as 20 mg/kg . d for 14 d. These same doses of CDM did not result in any alteration of cell-mediated immunity as measured by the delayed hypersensitivity response (DHR) to both keyhole limpet hemocyanin (KLH) and sRBC. Lymphocyte blastogenesis was increased in spleen cells from mice exposed to 40 mg/kg . d CDM in response to media alone, concanavalin A (Con A), and lipopolysaccharide (LPS). The in vitro PFC response by C57BL/6 mice was utilized to determine if CDM could suppress the antibody response due to a direct effect on the immune cells. CDM suppressed the in vitro PFC response only at concentrations that were directly cytolytic. A direct cytolytic effect was considered unlikely following exposure in the whole animal, since the suppression of the antibody response occurred in the absence of any effects on spleen cell number or spleen weight. To determine if route of exposure was a factor in the suppressive effects of CDM, 14-d studies were conducted administering CDM orally at doses up to 120 mg/kg . d. Both the CD-1 and C57BL/6 mouse were used to verify that a strain difference was not a factor. There was no effect on either the d 4 or d 5 antibody response, even though 43% of the mice exposed to 120 mg/kg died from the acute toxicity that can characterize this chemical. From an operational standpoint, these results indicate that the route of exposure of a compound relative to the route of administration of an antigen is an important consideration when determining the effects of that compound on an immune response. From an environmental standpoint, these results indicate that relatively high doses of chlordimeform do not result in consistent immunotoxicity as determined by the assays utilized.
这些研究调查了接触杀虫脒(CDM)这种甲脒类农药对随机繁殖的CD-1小鼠体内某些免疫参数的影响。还进一步研究了该化合物对C57BL/6小鼠体外空斑形成细胞(PFC)反应的影响。通过腹腔注射途径急性和14天接触CDM后,在腹腔免疫4天后测量发现,针对绵羊红细胞(sRBC)抗原的IgM抗体形成(空斑形成)细胞(PFC)数量减少。在低至20 mg/kg·d的剂量下持续14天即可观察到这种抑制作用。同样剂量的CDM对通过对钥孔血蓝蛋白(KLH)和sRBC的迟发型超敏反应(DHR)所测得的细胞介导免疫没有任何改变。接触40 mg/kg·d CDM的小鼠脾细胞对单独培养基、伴刀豆球蛋白A(Con A)和脂多糖(LPS)的淋巴细胞增殖反应增强。利用C57BL/6小鼠的体外PFC反应来确定CDM是否因直接作用于免疫细胞而抑制抗体反应。CDM仅在具有直接细胞溶解作用的浓度下才会抑制体外PFC反应。在对整个动物进行接触后,不太可能产生直接的细胞溶解作用,因为在对脾细胞数量或脾重量没有任何影响的情况下,抗体反应受到了抑制。为了确定接触途径是否是CDM抑制作用的一个因素,进行了为期14天的研究,以高达120 mg/kg·d的剂量口服给予CDM。使用CD-1和C57BL/6小鼠来验证品系差异不是一个因素。即使接触120 mg/kg的小鼠中有43%死于该化学物质特有的急性毒性,但对第4天或第5天的抗体反应均没有影响。从操作角度来看,这些结果表明,在确定化合物对免疫反应的影响时,化合物的接触途径相对于抗原的给药途径是一个重要的考虑因素。从环境角度来看,这些结果表明,按照所采用的检测方法,相对高剂量的杀虫脒不会导致一致的免疫毒性。