Hadeed Mohammad N, Castiglione Carlie L, Saleem Sayf, Chammout Diana H, Muskovac Mariana D, Crile Karen G, Abdulelah Sara A, Maalhagh-Fard Ali, Rampuri Ebrahim Y, Grabowski Gregory M, Belanger Rachelle M
Biology Department, University of Detroit Mercy, Detroit, MI 48221, United States.
Environ Adv. 2022 Dec;10. doi: 10.1016/j.envadv.2022.100320. Epub 2022 Nov 17.
The herbicide atrazine is widely used for controlling broad leaf weeds and increasing crop yields in agricultural areas. Atrazine enters aquatic environments through runoff, ground water discharge and seepage where concentrations have been recorded above 300 ppb. Exposure to the herbicide atrazine at environmentally relevant concentrations has been shown to negatively impact aquatic organisms, including crayfish. Because xenobiotics are concentrated in the crayfish hepatopancreas (digestive gland), we examined changes in morphology and DNA damage in hepatopancreatic tissue structure and cells following a 10-day exposure to atrazine (0, 10, 40, 80, 100 and 300 ppb). We found that there were marked morphological changes, post-exposure, for all atrazine concentrations tested. Hepatopancreatic tissue exhibited degenerated tubule epithelium with necrosis of microvilli, tubule lumen dilation, changes in tubular epithelium height and vacuolization of the epithelium. Likewise, we also performed a terminal deoxynucleotidyl transferase (TdT) mediated dUTP nick-end labeling (TUNEL) assay which showed the percentage of cells with DNA damage increased following atrazine exposure. Crayfish hepatopancreatic tissue displayed significant increases in TUNEL-positive cells following exposure to atrazine at 100 ppb and above. Overall, exposure to atrazine at environmentally relevant concentrations damages hepatopancreatic tissue. This impairment could lead to changes in biotransformation, detoxification, digestion and molting, subsequently reducing crayfish populations and negatively impacting the aquatic ecosystem.
除草剂阿特拉津广泛用于农业地区控制阔叶杂草和提高作物产量。阿特拉津通过径流、地下水排放和渗漏进入水生环境,在这些地方记录到的浓度超过了300 ppb。已表明,在与环境相关的浓度下接触除草剂阿特拉津会对包括小龙虾在内的水生生物产生负面影响。由于异生物质在小龙虾肝胰腺(消化腺)中富集,我们研究了在接触阿特拉津(0、10、40、80、100和300 ppb)10天后,肝胰腺组织结构和细胞的形态变化以及DNA损伤情况。我们发现,在所有测试的阿特拉津浓度下,接触后均出现了明显的形态变化。肝胰腺组织表现出肾小管上皮退化,伴有微绒毛坏死、肾小管腔扩张、肾小管上皮高度变化以及上皮细胞空泡化。同样,我们还进行了末端脱氧核苷酸转移酶(TdT)介导的dUTP缺口末端标记(TUNEL)分析,结果显示阿特拉津暴露后DNA损伤细胞的百分比增加。小龙虾肝胰腺组织在暴露于100 ppb及以上浓度的阿特拉津后,TUNEL阳性细胞显著增加。总体而言,在与环境相关的浓度下接触阿特拉津会损害肝胰腺组织。这种损害可能导致生物转化、解毒、消化和蜕皮的变化,进而减少小龙虾种群数量,并对水生生态系统产生负面影响。