Laboratorio de Ecotoxicología Acuática, INIBIOMA-(CONICET-UNCo), CEAN-Ruta 61 km 3, Paraje San Cabao, 8371 Junín de los Andes, Neuquén, Argentina.
Laboratorio de Ecotoxicología Acuática, INIBIOMA-(CONICET-UNCo), CEAN-Ruta 61 km 3, Paraje San Cabao, 8371 Junín de los Andes, Neuquén, Argentina.
Aquat Toxicol. 2014 Sep;154:97-106. doi: 10.1016/j.aquatox.2014.05.003. Epub 2014 May 12.
We studied Abcc mediated-transport in middle and posterior intestine of the rainbow trout, Oncorhynchus mykiss. Luminal and serosal transport were evaluated in everted and non-everted intestinal sacs, respectively, incubated with 1-chloro-2,4-dinitrobenzene (CDNB; 200 μM). CDNB enters the cells and is conjugated with glutathione via glutathione S-transferase (GST) to form 2,4-dinitrophenyl-S-glutathione (DNP-SG), a known Abcc substrate. DNP-SG concentration in the bath was recorded every 10 min, in order to calculate the mass-specific transport rate. For evaluating the possible involvement of Abcc proteins in microcystin-LR (MCLR) transport, 1.135 μM MCLR was added to the bath or inside the sacs, in everted or non-everted preparations, respectively. Both luminal and serosal DNP-SG efflux were significantly inhibited by MCLR. A concentration-response curve obtained using strips from middle intestine yielded an IC50 value of 1.33 μM MCLR. The Abcc inhibitor, MK571 produced concentration-dependent inhibition of DNP-SG similar to that produced by MCLR. Since competition of MCLR and CDNB as GST substrates could bias the DNP-SG transport results, we evaluated the effects of MCLR on calcein efflux, which does not depend on GST activity. We applied the non-fluorescent, cell-permeant compound calcein-AM (0.25 μM) to middle intestinal strips and recorded the efflux of its hydrolysis product, the fluorescent Abcc substrate calcein. 2.27 μM MCLR and 3 μM MK571 inhibited calcein efflux (17.39 and 20.2%, respectively). Finally, MCLR interaction with Abcc transporters was evaluated by measuring its toxic intracellular effects. Middle intestinal segments were incubated in saline solution with 1.135 μM MCLR (MC1), 2.27 μM MCLR (MC2), 3 μM MK571 (MK) or 1.135 μM MCLR+3 μM MK571 (MC1/MK). After 1h, GSH concentration, protein phosphatase 1 and 2A (PP1, PP2A) and GST activities were measured in each segment. MC1did not produce significant effect while MC1/MK and MC2 significantly inhibited PP1and PP2A in similar proportions (34-49%). MK alone significantly increased PP2A activity (40%) with no effect in any other variable. GST activity and GSH concentration were not affected by any treatment. Concentration-response curves for MCLR (1.135 to 13.62 μM) alone or plus 3 or 6 μM MK571 were obtained using PP1 activity as response variable. The IC50 values were 1.0, 0.52, and 0.37 μM, respectively. Our results suggest that O. mykiss enterocytes are capable of eliminating MCLR by GST-mediated conjugation and luminal excretion through an Abcc-like apical transporter. This mechanism would prevent toxic effects and reduce the toxin uptake into the blood, which is likely mediated by basolateral Abccs.
我们研究了虹鳟鱼中肠和后肠的 Abcc 介导的转运。分别用 1-氯-2,4-二硝基苯(CDNB;200μM)孵育外翻和非外翻肠囊,评估腔侧和基底外侧转运。CDNB 进入细胞并通过谷胱甘肽 S-转移酶(GST)与谷胱甘肽结合形成 2,4-二硝基苯-S-谷胱甘肽(DNP-SG),这是一种已知的 Abcc 底物。每隔 10 分钟记录浴中 DNP-SG 的浓度,以计算质量特异性转运速率。为了评估 Abcc 蛋白在微囊藻毒素-LR(MCLR)转运中的可能作用,将 1.135μM MCLR 加入浴中或外翻肠囊内。腔侧和基底外侧 DNP-SG 外排均被 MCLR 显著抑制。从中肠获得的条带的浓度-反应曲线得到的 MCLR 的 IC50 值为 1.33μM。Abcc 抑制剂 MK571 对 DNP-SG 的抑制作用呈浓度依赖性,类似于 MCLR 产生的抑制作用。由于 MCLR 和 CDNB 作为 GST 底物的竞争可能会影响 DNP-SG 转运结果,我们评估了 MCLR 对 calcein 外排的影响,calcein 外排不依赖于 GST 活性。我们将非荧光、细胞可渗透的 calcein-AM 化合物(0.25μM)应用于中肠条带,并记录其水解产物荧光 Abcc 底物 calcein 的外排。2.27μM MCLR 和 3μM MK571 分别抑制 calcein 外排(17.39%和 20.2%)。最后,通过测量 MCLR 对 Abcc 转运蛋白的毒性细胞内作用来评估 MCLR 与 Abcc 转运蛋白的相互作用。将中肠段在含有 1.135μM MCLR(MC1)、2.27μM MCLR(MC2)、3μM MK571(MK)或 1.135μM MCLR+3μM MK571(MC1/MK)的盐溶液中孵育 1 小时。孵育后,在每个肠段中测量 GSH 浓度、蛋白磷酸酶 1 和 2A(PP1、PP2A)和 GST 活性。MC1 没有产生显著影响,而 MC1/MK 和 MC2 以相似的比例(34-49%)显著抑制 PP1 和 PP2A。MK 单独使用可显著增加 PP2A 活性(40%),而对其他任何变量均无影响。GST 活性和 GSH 浓度不受任何处理影响。使用 PP1 活性作为反应变量,获得了单独的 MCLR(1.135 至 13.62μM)或加 3 或 6μM MK571 的 MCLR 浓度-反应曲线。IC50 值分别为 1.0、0.52 和 0.37μM。我们的结果表明,虹鳟鱼肠细胞能够通过 GST 介导的结合和通过 Abcc 样顶端转运蛋白的腔侧排泄来消除 MCLR。这种机制可以防止毒性作用并减少毒素进入血液的摄取,这可能是由基底外侧 Abcc 介导的。