MECHANISMS OF VANCOMYCIN-INDUCED NEPHROTOXICITY
MECHANISMS OF VANCOMYCIN-INDUCED NEPHROTOXICITY
批准号:
2185023
负责人:
Mary A Smith
金额:
$12.03万
依托单位国家:
美国
项目类别:
财政年份:
1993
资助国家:
美国
项目状态:
已结题
起止时间:
1993-01-01 至 1997-12-31
关键词:
adenylate kinase apical membrane basolateral membrane cell cell interaction cell membrane cellular respiration high performance liquid chromatography histopathology laboratory rat lipid metabolism membrane lipids membrane permeability mitochondrial membrane oxygen consumption phospholipids protein biosynthesis protein degradation renal toxin renal tubular transport renal tubule tissue /cell culture toxicant interaction urinalysis vancomycin
中文摘要
万古霉素(VAN)是一种阳离子糖肽抗生素,用于治疗
各种革兰氏阳性感染。范被认为是一个潜在的
耳毒性和肾毒剂。肾毒性的报告发生率
在人类中是高度可变的,范围从5%到17%。发病率
使用VAN时,肾毒性的发生率高达35%
同时使用氨基糖苷类抗生素。动物研究
对凡士林所致肾毒性机制的评价尚不完整
而且大多是描述性的。人们对此知之甚少
凡士林在肾脏内蓄积的机制
已知的是参与生产的机制
肾毒性。本实验室开发了一种货车诱导的模型。
雌性SD大鼠的肾毒性。肾毒性是
一些功能和结构上的改变证明了这一点。这些
变化包括血液尿素氮(BUN)浓度的升高,
糖异生能力下降,蓄积能力下降
有机离子。总肾重量增加所致的肾重量增加
水、蛋白质和磷脂也被观察到。大鼠的前处理
使用聚天冬氨酸(PAA),在给VAN之前,防止
肾毒性,似乎与肾VAN蓄积有关。这个
这项建议的前提是,货车必须积累起来
在肾细胞内产生肾毒性。一旦进入
细胞,VAN与肾脏蛋白质和磷脂在水平上相互作用
关键的膜系统,如质膜和
线粒体膜。这些变化导致了细胞的失调。
肾细胞运输特性和能量产生,然后是
转化为肾毒性反应。这项建议的目的是
为了阐明VAN在肾细胞内蓄积的机制,以及
然后确定VAN产生肾毒性的机制。
这些机制将在特定地点的反应方面加以解决
近端和远端肾小管上皮细胞的数量。这个目标将是
通过采用集成的机械化方法来实现
有问题。肾内VAN蓄积将在体内和体外进行测定。
膜上生长的近、远端肾小管细胞的原代培养
支撑物将被用来确定根尖与基底外侧的摄取
面包车。血管紧张素转换酶诱导的磷脂沉积和升高的机制
蛋白质含量将通过评估合成和
退化。VAN对线粒体膜和质膜的影响
磷脂图谱将通过关键的高效液相分离进行评估
磷脂。这些变化将与血浆中的变化相关
膜(顶端和基底外侧)转运能力与线粒体
能源生产。对相互作用性质的进一步考察
VAN和PAA之间的关系可能会为VAN的机制提供更多线索
与肾组织的相互作用。PAA干扰的机制
肾VAN蓄积将通过竞争性结合研究进行评估
在整个细胞和膜部分上。从这里收集的数据
建议书应提供有关机制的重要信息
并为今后的研究奠定了基础
近端肾小管与远端肾小管上皮细胞对
毒物引起的伤害。
英文摘要
Vancomycin (VAN) is a cationic glycopeptide antibiotic used to treat a
variety of gram-positive infections. VAN is regarded as a potentially
ototoxic and nephrotoxic agent. The reported incidence of nephrotoxicity
in humans is highly variable and ranges from 5% to 17%. The incidence
of nephrotoxicity increases to as high as 35% when VAN is used
concomitantly with an aminoglycoside antibiotic. Animal studies
evaluating the mechanisms of VAN-induced nephrotoxicity are incomplete
and mostly descriptive in nature. Little is known regarding the
mechanisms for renal accumulation of VAN within the kidney and nothing
is known about the mechanisms involved in the production of
nephrotoxicity. this laboratory has developed a model for VAN-induced
nephrotoxicity in the female Sprague-Dawley (SD) rat. Nephrotoxicity is
demonstrated by a number of functional and structural alterations. These
changes include elevations in blood urea nitrogen (BUN) concentrations,
decreased gluconeogenic capacity and decreased ability to accumulate
organic ions. Increases in kidney weight due to increases in total renal
water, protein and phospholipid are also observed. Pretreatment of rats
with polyaspartic acid (PAA), prior to VAN administration, prevents
nephrotoxicity and appears to be linked to renal VAN accumulation. The
premise on which this proposal is based is that VAN must be accumulated
within renal cells in order to produce nephrotoxicity. Once inside the
cells, VAN interacts with renal proteins and phospholipids at the level
of critical membrane systems such as the plasma membrane and
mitochondrial membrane. These alterations result in dysregulation of
renal cell transport properties and energy production, which are then
translated into a nephrotoxic response. The purpose of this proposal is
to delineate the mechanisms for VAN accumulation within renal cells and
then determine the mechanisms by which VAN produces nephrotoxicity.
These mechanisms will be addressed in terms of site-specific responses
of proximal & distal tubular cells to VAN. This goal will be
accomplished by taking an integrated, mechanistic approach to the
problem. Renal VAN accumulation will be determined in vivo and in vitro.
Primary cultures of proximal and distal tubular cells grown on membrane
supports will be used to determine the apical vs basolateral uptake of
VAN. The mechanisms for VAN-induced phospholipidosis and increased
protein content will be determined by evaluating synthesis and
degradation. The effects of VAN on mitochondrial and plasma membrane
phospholipid profiles will be evaluated by HPLC separation of key
phospholipids. These alterations will be correlated to changes in plasma
membrane (apical and basolateral) transport ability and mitochondrial
energy production. Further examination on the nature of the interaction
between VAN and PAA may shed some more light into the mechanisms for VAN
interactions with renal tissue. the mechanism for PAA interference with
renal VAN accumulation will be evaluated by competitive binding studies
on whole cells and membrane fractions. The data gathered from this
proposal should provide significant information regarding the mechanisms
of VAN-induced nephrotoxicity and lay the groundwork for future studies
on differential susceptibility of proximal vs distal tubular cells to
toxicant-induced injury.
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