Zaldibar B, Cancio I, Marigómez I
Cell Biology & Histology Laboratory, Zoology & Animal Cell Biology Department, School of Science & Technology, University of the Basque Country, PO Box 644, E-48080 Bilbo, Basque Country, Spain.
Aquat Toxicol. 2007 Feb 28;81(2):183-96. doi: 10.1016/j.aquatox.2006.12.007. Epub 2006 Dec 17.
In marine molluscs, the epithelium of the digestive gland is composed of two cell types, namely, digestive and basophilic cells. Under normal physiological conditions digestive cells outnumber basophilic cells, but under different stress situations the composition of the epithelium changes, basophilic cells apparently replace digestive cell. Winkles, Littorina littorea, were exposed to 1.25mg/l Cd for 20 days to provoke cell type replacement. Then, animals were depurated in clean seawater for 10 days to determine whether cell type replacement was reversible. Digestive glands were fixed in Carnoy and paraffin embedded for histological analysis. The volume densities of basophilic cells (Vv(BAS)) and digestive cells (Vv(DIG)) were calculated by stereology on hematoxylin-eosin stained sections. Vv(BAS) increased and Vv(DIG) decreased in Cd-exposed animals. After estimation of cell size and absolute cell numbers, these changes were attributed to digestive cell loss and concomitant basophilic cell hypertrophy but not to increased numbers of basophilic cells. Cell type composition and cell size almost fully returned to normal values after 10-day depuration. Accordingly, PCNA immunohistochemistry demonstrated that proliferating digestive cells were more abundant in winkles exposed to Cd and after 10-day depuration than in control specimens, suggesting that net digestive cell loss was accompanied by increased digestive cell proliferation. Thus, Cd-exposure seems to provoke an enhanced digestive cell turnover in order to cope with Cd detoxification. Intralysosomal accumulation of metals (autometallographied black silver deposits; BSD) was used as a biomarker of exposure to Cd and lysosomal structural changes as an effect biomarker to see whether cell type composition might have any effect on these endpoints. BSD formed around Cd ions, in digestive cell lysosomes of Cd-exposed winkles whereas basophilic cells appeared devoid of them. After depuration, BSD were less conspicuous. Enlarged lysosomes were observed in Cd-exposed winkles, lysosome size returning to control levels after 10-day depuration. Changes in digestive cell proliferation, digestive cell loss and basophilic cell hypertrophy did not apparently affect the biomarkers investigated herein.
在海洋软体动物中,消化腺上皮由两种细胞类型组成,即消化细胞和嗜碱性细胞。在正常生理条件下,消化细胞的数量超过嗜碱性细胞,但在不同的应激情况下,上皮细胞的组成会发生变化,嗜碱性细胞明显取代消化细胞。将滨螺(Littorina littorea)暴露于1.25mg/l的镉中20天,以引发细胞类型的替代。然后,将动物置于清洁海水中净化10天,以确定细胞类型的替代是否可逆。将消化腺用卡诺固定液固定,石蜡包埋,用于组织学分析。通过体视学方法在苏木精-伊红染色切片上计算嗜碱性细胞(Vv(BAS))和消化细胞(Vv(DIG))的体积密度。在暴露于镉的动物中,Vv(BAS)增加,Vv(DIG)减少。在估计细胞大小和绝对细胞数量后,这些变化归因于消化细胞的损失和伴随的嗜碱性细胞肥大,而不是嗜碱性细胞数量的增加。经过10天的净化后,细胞类型组成和细胞大小几乎完全恢复到正常值。因此,增殖细胞核抗原免疫组织化学显示,暴露于镉的滨螺以及经过10天净化后的滨螺中,增殖的消化细胞比对照标本中更丰富,这表明消化细胞的净损失伴随着消化细胞增殖的增加。因此,镉暴露似乎会引发消化细胞更新增强,以应对镉的解毒。溶酶体内金属的积累(自动金属显影黑色银沉积物;BSD)被用作镉暴露的生物标志物,溶酶体结构变化作为效应生物标志物,以观察细胞类型组成是否可能对这些终点产生任何影响。在暴露于镉的滨螺的消化细胞溶酶体中,BSD围绕镉离子形成,而嗜碱性细胞似乎没有。净化后,BSD不那么明显。在暴露于镉的滨螺中观察到溶酶体增大,经过10天净化后,溶酶体大小恢复到对照水平。消化细胞增殖、消化细胞损失和嗜碱性细胞肥大的变化显然没有影响本文研究的生物标志物。