McCracken R J, Van Rhijn J A, Kennedy D G
Chemical Surveillance Department, Veterinary Sciences Division, Department of Agriculture and Rural Development, Belfast, Northern Ireland, UK.
Food Addit Contam. 2005 Jun;22(6):567-72. doi: 10.1080/02652030500137868.
The global problem of food products contaminated by residues of the banned carcinogenic nitrofuran drugs has prompted research into how such residues accumulate in tissues. In the study described here, two aspects have been investigated where the nitrofurans accumulate in tissues from chickens exposed to either a dietary or an environmental source of contamination. Twenty groups of broilers were fed a diet containing one of the nitrofurans: furazolidone, nitrofurazone, nitrofurantoin or furaltadone at concentrations of 30, 100, 300, 1000 and 3000 microg kg(-1). At the lowest concentration of furazolidone contamination (0.01% of the therapeutic dose) tissue bound AOZ metabolite residues were detected in liver (1.1 +/- 0.2 microg kg(-1)) and in muscle (0.33 +/- 0.03 microg kg(-1)). Similar results were obtained for AMOZ (0.6 +/- 0.2 microg kg(-1) in liver), the tissue bound metabolite of furaltadone. There was no appreciable accumulation of nitrofurantoin in chicken muscle. The AHD metabolite was not detected in muscle from birds fed nitrofurantoin at either 30 or 100 microg kg(-1). For nitrofurazone the concentrations of the SEM metabolite were higher in muscle than in liver for all dietary concentrations. The potential for a contaminated environment to cause nitrofuran residues in chickens was investigated. Six chickens were placed in a pen that was previously occupied by birds fed a diet containing 3000 microg kg(-1) of furazolidone. After 24 hours' exposure of the chickens to the litter in the pen, AOZ residues of 0.13 +/- 0.04 and 0.10 +/- 0.03 microg kg(-1) were detected in liver and muscle, respectively. The results of both experiments have implications for the poultry industry in trying to eliminate nitrofurans from their production systems, and for regulatory analysts faced with the detection of low concentrations of the drugs, both in tissues and in feedingstuffs.
全球食品受禁用致癌硝基呋喃类药物残留污染的问题,促使人们研究此类残留物如何在组织中蓄积。在本文所述的研究中,对硝基呋喃在受饮食或环境污染源污染的鸡组织中的两个蓄积方面进行了调查。将二十组肉鸡分别饲喂含有呋喃唑酮、呋喃西林、呋喃妥因或呋吗唑酮这几种硝基呋喃之一的饲料,浓度分别为30、100、300、1000和3000微克/千克。在呋喃唑酮污染的最低浓度(治疗剂量的0.01%)下,在肝脏(1.1±0.2微克/千克)和肌肉(0.33±0.03微克/千克)中检测到了与组织结合的AOZ代谢物残留。对于呋吗唑酮的组织结合代谢物AMOZ(肝脏中为0.6±0.2微克/千克),也获得了类似结果。在鸡肌肉中未检测到呋喃妥因有明显蓄积。在饲喂30或100微克/千克呋喃妥因的鸡的肌肉中未检测到AHD代谢物。对于呋喃西林,在所有饮食浓度下,肌肉中SEM代谢物的浓度均高于肝脏。研究了受污染环境导致鸡体内硝基呋喃残留的可能性。将六只鸡放入一个先前被饲喂含有3000微克/千克呋喃唑酮饲料的鸡占用过的围栏中。鸡在围栏中的垫料上暴露24小时后,在肝脏和肌肉中分别检测到0.13±0.04和0.10±0.03微克/千克的AOZ残留。这两个实验的结果对于家禽业试图从其生产系统中消除硝基呋喃,以及对于面临在组织和饲料中检测低浓度药物的监管分析人员都有影响。