Arfsten D P, Still K R, Wilfong E R, Johnson E W, McInturf S M, Eggers J S, Schaeffer D J, Bekkedal M Y-V
Navy Drug Screening Laboratory, Naval Air Station Jacksonville, Florida 32212-0113, USA.
J Toxicol Environ Health A. 2009;72(6):410-27. doi: 10.1080/15287390802647344.
Depleted uranium (DU) munitions and armor plating have been used in several conflicts over the last 17 yr, including the Persian Gulf War and the Iraq War. Because of its effectiveness and availability, DU will continue to be used in military applications into the foreseeable future. There is much controversy over the use of DU in weapons and equipment because of its potential radiological and toxic hazards, and there is concern over the chronic adverse health effects of embedded DU shrapnel in war veterans and bystanders. This study evaluated the effects of long-term implantation of DU on the reproductive success of F0 generation adults and development and survival of subsequent F1 and F2 generations in a two-generation reproductive toxicity study. F0 generation Sprague-Dawley rats, 8 wk of age, were surgically implanted with 0, 4, 8, 12, or 20 DU pellets (1 x 2 mm). Inert implant control animals were implanted with 12 or 20 tantallum (Ta) pellets. The F0 generation was then mated at 120 d post DU implantation. In the F0 generation, when measured on postimplantation d 27 and 117, uranium was present in the urine of DU-implanted animals in a dose-dependent manner. F0 reproductive success was similar across treatment groups and the maternal retrieval test revealed no changes in maternal behavior. DU implantation exerted no effect on the survival, health, or well-being of the F0 generation. Necropsy results of F0 animals were negative with the exception of a marked inflammatory response surrounding the implanted DU pellets. For the F1 generation, measures of F1 development through postnatal day (PND) 20 were unremarkable and no gross abnormalities were observed in F1 offspring. No uranium was detected in whole-body homogenates of PND 4 or PND 20 pups. Necropsy findings of F1 PND 20 pups were negative and no instances of ribcage malformation were observed in F1 PND 20 pups. Body weight and body weight gain of F1 rats through PND 120 were similar across treatment groups. Eight of 414 F1 animals observed from PND 20 to 120 died of unknown causes; 7 were from litters of DU-implanted F0 mating pairs. F1 mating success at 10 wk of age was an overall 70% compared with 91% for F0 mating pairs. Mating success was similar between F1 animals derived from DU-implanted F0 adults and those derived from F0 implant control adults suggesting that the comparatively low mating success was not due to F1 DU exposure. The gestational index of F1 animals derived from mid-dose F0 mating pairs was found to be lower compared with F1 controls. The average gestation duration of F1 animals derived from high-dose F0 mating pairs was found to be significantly longer than F1 controls. F1 sperm motility analyses did not differ among experimental groups and no gross abnormalities were identified at necropsy among surviving F1 animals at PND 120. Histopathology of kidneys, spleen, thymus, bone marrow, ovaries, and testes of F1 high-dose animals did not differ from F1 controls. F1 high-dose females had significantly higher mean relative liver and heart weights compared with F1 controls; the biological relevance of this finding could not be determined. For the F2 generation, measures of F2 development through PND 20 were unremarkable and no gross abnormalities were observed in F2 offspring. Necropsy findings of F2 PND 20 pups were negative and no instances of ribcage malformation were observed in F2 PND 20 pups. Body weight and body weight gain of F2 rats through PND 90 were similar across treatment groups. Mean relative heart weights of males derived from high-dose F0 parents were significantly lower compared with F2 controls. Sperm motility and concentration analysis of F2 males at PND 90 were similar across F2 groups. Overall, the consistent absence of positive findings in this study seems to suggest that DU is not a significant reproductive or developmental hazard, particularly when one considers that mid- and high-dose rats were implanted with the equivalent of 0.3 and 0.5 lb of DU in a 70-kg human, respectively. However, the findings that seven of eight F1 adults that died postweaning were from DU-implanted F0 mating pairs, and that mean relative heart weights were elevated in high-dose F1 and F2 pups, suggest conservatism is warranted in characterizing the reproductive and teratogenic hazards of embedded DU until further studies are completed.
在过去17年的几场冲突中,包括海湾战争和伊拉克战争,贫铀弹药和装甲板都有使用。由于其有效性和可得性,在可预见的未来,贫铀仍将用于军事用途。由于贫铀潜在的放射性和毒性危害,其在武器和装备中的使用存在诸多争议,人们还担心战争退伍军人和旁观者体内嵌入的贫铀弹片会对健康产生长期不良影响。本研究在一项两代生殖毒性研究中,评估了长期植入贫铀对F0代成年动物生殖成功率以及后续F1和F2代发育和存活的影响。8周龄的F0代斯普拉格-道利大鼠通过手术植入含0、4、8、12或20颗贫铀丸(1×2毫米)。惰性植入物对照动物植入12或20颗钽丸。贫铀植入后120天,F0代动物进行交配。在F0代中,植入后第27天和第117天测量时,植入贫铀的动物尿液中铀的含量呈剂量依赖性。各治疗组的F0代生殖成功率相似,母性检索试验显示母性行为无变化。植入贫铀对F0代动物的存活、健康或福祉没有影响。F0代动物尸检结果均为阴性,但植入的贫铀丸周围有明显的炎症反应。对于F1代,出生后第20天(PND 20)前的F1代发育指标无异常,F1代后代未观察到明显的异常。在PND 4或PND 20幼崽的全身匀浆中未检测到铀。F1代PND 20幼崽的尸检结果为阴性,F1代PND 20幼崽未观察到胸廓畸形的情况。各治疗组F1代大鼠在PND 120前的体重和体重增加情况相似。从PND 20到120观察的414只F1代动物中有8只死于不明原因;其中7只来自植入贫铀的F0代交配组。F1代10周龄时的交配成功率总体为70% , 而F0代交配组为91%。来自植入贫铀的F0代成年动物的F1代动物与来自F0代植入物对照成年动物的F1代动物交配成功率相似,这表明相对较低的交配成功率不是由于F1代接触贫铀所致。发现来自中剂量F0代交配组的F1代动物的妊娠指数低于F1代对照组。发现来自高剂量F0代交配组的F1代动物的平均妊娠期明显长于FIP对照组。F1代精子活力分析在各实验组之间无差异,在PND 120存活的F1代动物尸检中未发现明显异常。F1代高剂量动物的肾脏、脾脏、胸腺、骨髓、卵巢和睾丸的组织病理学与F1代对照组无差异。F1代高剂量雌性动物的肝脏和心脏平均相对重量明显高于F1代对照组;这一发现的生物学相关性尚无法确定。对于F2代,出生后第20天(PND 20)前的F2代发育指标无异常,F2代后代未观察到明显的异常。F2代PND 20幼崽的尸检结果为阴性,F2代PND 20幼崽未观察到胸廓畸形的情况。各治疗组F2代大鼠在PND 90前的体重和体重增加情况相似。来自高剂量F0代亲本的雄性F2代动物的心脏平均相对重量明显低于F2代对照组。F2代雄性动物在PND 90时的精子活力和浓度分析在各F2组之间相似。总体而言,本研究中始终未发现阳性结果,这似乎表明贫铀不是重大的生殖或发育危害,特别是考虑到中剂量和高剂量大鼠植入的贫铀量分别相当于70千克人体中的0.3磅和0.5磅。然而,断奶后死亡的8只F1代成年动物中有7只来自植入贫铀的F0代交配组,以及高剂量F1代和F2代幼崽的心脏平均相对重量升高,这表明在完成进一步研究之前,在确定嵌入贫铀的生殖和致畸危害时应持谨慎态度。