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免疫测定法并非免疫错误:来自两个淡水鳟鱼养殖场类固醇产量研究的实例。

Immunoassays are not immune to errors: Examples from two studies of steroid output from freshwater trout farms.

机构信息

Centre for Environment, Fisheries and Aquaculture Science (Cefas), Weymouth Laboratory, Barrack Road, The Nothe, Weymouth, Dorset DT4 8UB, UK.

Brunel University London, Institute for Environment, Health and Societies, Uxbridge, Middlesex UB8 3PH, UK.

出版信息

Gen Comp Endocrinol. 2020 Jan 1;285:113226. doi: 10.1016/j.ygcen.2019.113226. Epub 2019 Jul 30.

Abstract

A "reproducibility crisis" is widespread across scientific disciplines, where results and conclusions of studies are not supported by subsequent investigation. Here we provide a steroid immunoassay example where human errors generated unreproducible results and conclusions. Our study was triggered by a scientific report citing abnormally high concentrations (means of 4-79 ng L) of three natural sex steroids [11-ketotestosterone (11-KT), testosterone (T) and oestradiol (E2)] in water samples collected from two UK rivers over 4 years (2002-6). Furthermore, the data suggested that trout farms were a major source because reported steroid concentrations were 1.3-6 times higher downstream than upstream. We hypothesised that the reported levels were erroneous due to substances co-extracted from the water causing matrix effects (i.e. "false positives") during measurement by enzyme-linked immunoassay (EIA). Thus, in collaboration with three other groups (including the one that had conducted the 2002-6 study), we carried out field sampling and assaying to examine this hypothesis. Water samples were collected in 2010 from the same sites and prepared for assay using an analogous method [C18 solid phase extraction (SPE) followed by extract clean-up with aminopropyl SPE]. Additional quality control ("spiked" and "blank") samples were processed. Water extracts were assayed for steroids using radioimmunoassay (RIA) as well as EIA. Although there were statistically significant differences between EIA and RIA (and laboratories), there was no indication of matrix effects in the EIAs. Both the EIAs and RIAs (uncorrected for recovery) measured all three natural steroids at <0.6 ng L in all river water samples, indicating that the trout farms were not a significant source of natural steroids. The differences between the two studies were considerable: E2 and T concentrations were ca. 100-fold lower and 11-KT ca. 1000-fold lower than those reported in the 2002-6 study. In the absence of evidence for any marked changes in husbandry practice (e.g. stock, diet) or environmental conditions (e.g. water flow rate) between the study periods, we concluded that calculation errors were probably made in the first (2002-6) study associated with confusion between extract and water sample concentrations. The second (2010) study also had several identified examples of calculation error (use of an incorrect standard curve; extrapolation below the minimum standard; confusion of assay dilutions during result work-up; failure to correct for loss during extraction) and an example of sample contamination. Similar and further errors have been noted in other studies. It must be recognised that assays do not provide absolute measurements and are prone to a variety of errors, so published steroid levels should be viewed with caution until independently confirmed.

摘要

“可重复性危机”在各个科学领域普遍存在,研究的结果和结论无法得到后续调查的支持。在这里,我们提供了一个类固醇免疫分析的例子,其中人为错误导致了不可重复的结果和结论。我们的研究是由一份科学报告引发的,该报告称在英国两条河流的水样中检测到三种天然性激素[11-酮睾酮(11-KT)、睾酮(T)和雌二醇(E2)]的浓度异常高(平均值为 4-79ng/L)[1]。此外,数据表明,鲑鱼养殖场是主要的污染源,因为报告的类固醇浓度下游比上游高出 1.3-6 倍。我们假设报告的水平是错误的,因为在酶联免疫分析(EIA)测量过程中,从水中共同提取的物质会导致基质效应(即“假阳性”)。因此,我们与其他三个小组(包括进行 2002-6 年研究的小组)合作,进行了实地采样和分析,以检验这一假设。2010 年,从同一地点采集水样,并采用类似的方法[C18 固相萃取(SPE),然后用氨基丙基 SPE 进行萃取净化]进行检测[2]。还处理了额外的质量控制(“加标”和“空白”)样品。使用放射免疫分析(RIA)和 EIA 测定水样中的类固醇。尽管 EIA 和 RIA(以及实验室)之间存在统计学差异,但 EIA 中没有基质效应的迹象。两种 EIA 和 RIA(未经回收率校正)在所有河水样本中均测量到所有三种天然类固醇的浓度<0.6ng/L,表明鲑鱼养殖场不是天然类固醇的重要来源[3]。两项研究之间的差异相当大:E2 和 T 的浓度比 2002-6 年研究报告的浓度低约 100 倍,11-KT 低约 1000 倍[3]。在研究期间,没有证据表明养殖实践(例如,种群、饮食)或环境条件(例如,水流速度)有任何明显变化的情况下,我们得出结论,在第一项(2002-6)研究中,可能由于在提取物和水样浓度之间混淆而导致计算错误[4]。第二项(2010)研究也有几个确定的计算错误示例(使用不正确的标准曲线;在最低标准以下外推;在结果处理过程中对测定稀释液的混淆;在提取过程中未校正损失)和一个样本污染的示例[5]。在其他研究中也注意到类似的和进一步的错误。必须认识到,测定方法并不能提供绝对测量值,并且容易出现各种错误,因此在独立确认之前,应谨慎看待已发表的类固醇水平。

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