U.S. Fish and Wildlife Service, Chesapeake Bay Field Office, 177 Admiral Cochrane Drive, Annapolis, MD 21401, USA.
Myers Ecotoxicology Services, LLC, 19604 12th Ave NW, Shoreline, WA 98177, USA.
Sci Total Environ. 2017 Jan 1;575:1325-1338. doi: 10.1016/j.scitotenv.2016.09.209. Epub 2016 Oct 15.
From the 1940s through 1977, at least 590,000kg of polychlorinated biphenyls (PCBs) were released into the Hudson River from General Electric manufacturing plants located in Hudson Falls and Fort Edward, New York. In 1984, the U.S. Environmental Protection Agency designated a nearly 322km reach as the Hudson River PCBs Superfund Site. Here we describe a Fish Health Assessment study, part of a Natural Resource Damage Assessment, that evaluated the prevalence of toxicopathic lesions in adult brown bullhead (Ameiurus nebulosus), smallmouth bass (Micropterus dolomieu), and yellow perch (Perca flavescens). In fall 2001, 29-51 fish of each species were collected in fall 2001 from highly contaminated areas below the plants (Thompson Island Pool (TIP) and Stillwater Dam Pool (STW)), an upriver reference area (Feeder Dam Pool (FDP)), and a reference lake, Oneida Lake (ODA). The focus was on histopathologic lesions and observations associated with contaminant exposure: liver-neoplasms, foci of cellular alteration, bile duct hyperplasia; testes-ovotestis (testicular oocytes), germ cell degeneration, altered developmental stage; ovaries-atresia and altered developmental stage. Lesions associated with PCB exposure were defined as those with significantly greater prevalence and/or severity in TIP and STW compared with ODA and FDP. For brown bullhead and smallmouth bass, no lesions or changes in gonadal development met those criteria. In yellow perch, ovarian atresia was the only lesion associated with PCB exposure. Prevalence was 53% in FDP, 75% in ODA, and 100% in both STW and TIP; severity increased from mostly minimal to mild-moderate. Because of the high prevalence of atresia in reference collections, it is likely that factors other than PCBs are also involved. As part of a post-dredging monitoring plan, we recommend assessing gonad structure and function in yellow perch collected at the time of spawning in locations with a range of PCB contamination.
从 20 世纪 40 年代到 1977 年,至少有 59 万公斤多氯联苯(PCBs)从通用电气位于纽约哈德逊福尔斯和爱德华堡的制造厂释放到哈德逊河中。1984 年,美国环境保护署将近 322 公里的河段指定为哈德逊河 PCB 超级基金遗址。在这里,我们描述了一项鱼类健康评估研究,该研究是自然资源损害评估的一部分,评估了成年褐鳜(Ameiurus nebulosus)、小口黑鲈(Micropterus dolomieu)和黄鲈(Perca flavescens)中有毒病变的流行程度。2001 年秋季,从工厂下方的高度污染区域(汤普森岛池(TIP)和斯蒂尔沃特坝池(STW))、上游参考区域(饲料坝池(FDP))和一个参考湖奥奈达湖(ODA)采集了 29-51 条每种鱼类。重点是与污染物暴露相关的组织病理学病变和观察:肝脏-肿瘤、细胞改变焦点、胆管增生;睾丸-卵睾(睾丸卵母细胞)、生殖细胞退化、发育阶段改变;卵巢-闭锁和发育阶段改变。与 PCB 暴露相关的病变被定义为与 ODA 和 FDP 相比,在 TIP 和 STW 中具有更高的流行率和/或严重程度的病变。对于褐鳜和小口黑鲈,没有病变或性腺发育变化符合这些标准。在黄鲈中,卵巢闭锁是唯一与 PCB 暴露相关的病变。在 FDP 中的流行率为 53%,在 ODA 中的流行率为 75%,在 STW 和 TIP 中的流行率均为 100%;严重程度从轻微到中度逐渐增加。由于参考采集中闭锁的高流行率,除了 PCBs 之外,其他因素也可能参与其中。作为疏浚后监测计划的一部分,我们建议在 PCB 污染程度不同的产卵地点采集黄鲈时,评估其性腺结构和功能。