首页> 外文期刊>The Journal of Experimental Biology >CA2+ VERSUS ZN2+ TRANSPORT IN THE GILLS OF FRESHWATER RAINBOW TROUT AND THE COST OF ADAPTATION TO WATERBORNE ZN2+
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CA2+ VERSUS ZN2+ TRANSPORT IN THE GILLS OF FRESHWATER RAINBOW TROUT AND THE COST OF ADAPTATION TO WATERBORNE ZN2+

机译:Ca2 +与ZN2 +在淡水虹鳟2中的运输及适应水生ZN2 +的成本

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摘要

Previous work suggested that Ca2+ and Zn2+ share a common uptake pathway in rainbow trout gills, We here report on relationships between the kinetic variables for unidirectional Ca2+ influx and unidirectional Zn2+ influx during a 1 month exposure of freshwater rainbow trout to Zn2+ (150 mu g l(-1)=2.3 mu mol l(-1) as total zinc, Zn), Initial exposure to Zn2+ caused a large competitive inhibition of Ca2+ influx, as indicated by a threefold increase in apparent K-m for Ca2+ (measured in the presence of Zn2+), There was also a smaller non-competitive inhibition (50% decrease in J(max)) of the Ca2+ transport system, which was abolished after 1-2 weeks of exposure, The K-m, measured in the absence of Zn2+, decreased dramatically (i.e. elevated affinity) on days 1-4 but increased thereafter; both true and apparent K-m finally stabilized significantly above control levels, However, the K-m values for Ca2+ (<200 mu mol l(-1)) were low relative to the Ca2+ level in the water (1000 mu mol l(-1)), and therefore the changes did not influence the actual Ca2+ influx of the fish, which tracked J(max), In contrast, water [Zn2+] (2.3 mu mol l(-1) as total Zn) was close to the reported apparent K-m (3.71 mu mol l(-1)) for Zn2+ influx in the presence of 1000 mu mol l(-1) Ca2+, Unidirectional Zn2+ influx increased during the first week of exposure to waterborne Zn2+, followed by a persistent reduction to about 50% of control levels, effects that may be largely explained by the observed changes in true K-m for Ca2+, We speculate that the initial response of the fish to elevated [Zn2+] is to compensate for a reduced availability of Ca2+ by markedly increasing the affinity of a dual Ca2+/Zn2+ transporter, Once the Ca2+ influx is 'corrected' by restoration of functional transport sites (J(max)), the system is tuned to limit the influx of Zn2+ by a persistent reduction in the affinities for both ions. The changes in influx characteristics for Ca2+ and Zn2+ were correlated with internal physiological alterations indicative of adaptation to Zn2+ and increased metabolic cost, Depressed plasma [Ca] was corrected within 1 week, and there were no effects on whole-body [Ca] or [Zn]. A slight accumulation of Zn in the gills was associated with increased branchial metallothionein levels, Rates of protein synthesis and degradation in the gills were initially increased and whole-body growth was transiently impaired, effects which were reversed after 18 days of exposure, Sublethal challenge with Zn2+ (at 450 mu g l(-1)=6.9 mu mol l(-1) as total Zn) always depressed plasma [Ca] in control fish, but by 1 month of exposure to Zn2+ at 150 mu g l(-1) (as total Zn), experimental fish were resistant to challenge, However, the fish did not acquire increased survival tolerance (LT(50)) to a lethal concentration of Zn2+ (4 mg l(-1)=61 mu mol l(-1) as total Zn). [References: 39]
机译:先前的工作表明,Ca2 +和Zn2 +在虹鳟g中有一个共同的摄取途径,我们在此报告了在淡水虹鳟暴露于Zn2 +(150μgl( -1)= 2.3μmol l(-1)作为总锌(Zn),最初暴露于Zn2 +导致对Ca2 +流入的竞争性抑制作用很大,这表明Ca2 +的表观Km增加了三倍(在存在Zn2 +的情况下测量),对Ca2 +转运系统的非竞争性抑制作用较小(J(max)降低50%),在暴露1-2周后被取消,在没有Zn2 +的情况下测得的Km急剧下降(即亲和力增加)在1-4天,但随后增加;真实和表观Km都最终稳定在控制水平以上,但是,Ca2 +(<200μmoll(-1))的Km值相对于水中的Ca2 +水平(1000μmoll(-1))较低。 ,因此这些变化不会影响实际的Ca2 +流入量(跟踪J(max))。相反,水[Zn2 +](2.3 mol mol(-1)作为总Zn)接近报道的表观Km在存在1000μmol l(-1)Ca2 +的情况下(3.71μmol l(-1))的Zn2 +流入量,在暴露于水性Zn2 +的第一周内单向Zn2 +流入量增加,随后持续减少至约50%的控制水平,其影响很大程度上可以通过观察到的Ca2 +的真实Km变化来解释。我们推测,鱼类对[Zn2 +]升高的初始反应是通过显着提高a2的亲和力来补偿Ca2 +的减少。 Ca2 + / Zn2 +双重转运蛋白,一旦通过功能性转运位点的恢复“校正”了Ca2 +内流(J(m ax)),调整系统以通过持续降低两种离子的亲和力来限制Zn2 +的流入。 Ca2 +和Zn2 +的流入特征的变化与内部生理变化相关,表明对Zn2 +的适应性和代谢成本的增加,血浆[Ca]的降低在1周内得到纠正,对全身[Ca]或[Ca]均无影响。锌]。 g中锌的少量积累与分支金属硫蛋白水平的升高有关,initially中蛋白质合成和降解的速率最初提高,全身生长暂时受到损害,接触18天后,这种作用被逆转,亚致死Zn2 +(在总浓度为450 mu gl(-1)= 6.9 mu mol l(-1)时)在对照鱼中总是抑制血浆[Ca],但是在150 mu gl(-1)暴露于Zn2 + 1个月(作为总锌),实验鱼对攻击具有抵抗力,但是,对于致命浓度的Zn2 +(4 mg l(-1)= 61μmol l(-1),鱼没有获得更高的生存耐受性(LT(50)) )作为总Zn)。 [参考:39]

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