食品中微量元素形态:酶解- sec - icp - ms联合方法

H. Crews, R. Massey, D. J. Mcweeny, J. Dean
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引用次数: 4

摘要

食物中的微量元素可以是可取的,可以是可容忍的,也可以是不可取的。它们作为农产品的天然成分、故意添加的添加剂以及来自环境和加工来源的污染物出现在饮食中。从历史上看,它们对人类的重要性一直是根据食物中元素的总浓度或整体饮食中的总量来评估的(汞的测量除外,在较小程度上,砷有时会测量特定形式)。近年来,人们越来越认识到仅仅测量总浓度的不足,现在正在努力提供更准确地满足营养学家和毒理学家需要的信息。在过去几年中,农业部食品科学实验室开展了一个小型项目,研究如何获得有关食品中微量元素的化学形式的更有意义的信息。作为解决该问题的一般方法的第一阶段,人们的注意力一直局限于用正常单胃哺乳动物消化酶处理后在中性pH附近可溶的物种。已经开发出一种程序,在该程序中,食物依次用pH约为2的胃蛋白酶和pH约为7的胰酶在37℃下处理。该程序的局限性在于它是一个“静态”系统,而吸收是动态的;如果在可溶性和不可溶性物种之间存在平衡,系统将低估潜在的生物可利用量。在一些非常简单的实验中,研究人员检测了英国饮食中谷类、肉类、鱼类和绿色蔬菜组成的食物组合物是否添加了少量的铜、锌、镉和铅作为无机盐。对酶处理后可溶的内源元素与添加元素的性能进行了比较。在所研究的所有食物中,内源性铜和添加铜的表现相似,但其他一些元素的表现存在显著差异。例如,鱼中的锌基本上是不溶的,添加的锌也变得不溶;其他食物以可溶性形式释放出大量锌。另一方面,肉中的铁大部分是可溶的,但添加的铁就变得不溶了。在一种食物对另一种食物释放微量元素的影响的研究中,这项调查得到了进一步的发展。如果与全麦面包一起消化,蟹肉中的酸溶性镉含量会减少75%;白面包的效果很小。类似的实验表明,在碎牛肉中加入10%的大豆会大大降低牛肉中锌的释放量——可能是大豆植酸盐效应。加工牛肉会影响铁的溶解度;在膳食补充剂中摄入的无机铁,如果与谷物和蔬菜一起消化,比与肉和鱼一起消化更容易溶解。这些实验的主要结论是:a)酸度提高溶解度,b)酶作用改变溶解度,c)加工会影响溶解度,d)其他食物的存在会影响溶解度。即使一种元素是可溶的,也有迹象表明,由于酶的作用、加工或其他食物的存在,化学形式会发生变化。在设计对这些变化的调查时,标准是:i)食品中含有正常食品供应中典型有毒元素的水平;Ii)系统:
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Trace Element Speciation in Food: A Combined Enzymolysis—SEC-ICP-MS Approach
Trace elements in food can be either desirable, tolerable or undesirable. They occur in the diet as natural constituents of agricultural produce, as deliberate additives and as contaminants from environmental and processing sources. Historically, their significance to man has been assessed on the basis of total concentration of the element in the food item-or the total amount in the diet as a whole (with the exception of the measurement of mercury and to a lesser extent arsenic where specific forms are sometimes measured). In recent years the inadequacy of simply measuring the total concentration has been increasingly appreciated and efforts to provide information which is targeted more accurately to the needs of the nutritionist and the toxicologist are now being made. Over the last few years, the MAFF Food Science Laboratory has had a small programme investigating ways of obtaining more meaningful information about the chemical forms of trace elements in food. As a first stage of a general approach to the problem, attention has been restricted to species which are soluble at around neutral pH after treatment with normal monogastric mammalian digestive enzymes. A procedure has been developed in which food is treated sequentially with pepsin at around pH 2 and with pancreatic enzymes at around pH 7 at 37 'C. A limitation of this procedure is that it is a "static" system, whereas absorption is dynamic; if there is equilibrium between soluble and insoluble species, the system will underestimate the amount which is potentially available biologically. In some very simple experiments, food composites representing the cereal, meat, fish and green vegetable components of the UK diet were examined with and without the addition of small amounts of copper, zinc, cadmium and lead as inorganic salts. The properties of the endogenous element which was soluble after enzyme treatment has been compared with that of the added element. For all the foods studied, endogenous and added copper behaved similarly, but there were marked differences for some of the other elements. For instance, zinc from fish is largely insoluble, and added zinc also becomes insoluble; other foods release much zinc in soluble form. On the other hand, iron from meat is largely soluble but added iron becomes insoluble [1]. This investigation has been developed further in studies of the effect of one food upon the release of trace elements from another. The amount of acidsoluble cadmium available from crab meat is reduced by 75% by digesting it along with wholemeal bread; white bread has very little effect. Similar experiments show that addition of 10% soya to ground beef gives a much lower release of zinc from the beef-presumably a soya phytate effect. Processing of beef can affect the solubility of iron; inorganic iron as taken in dietary supplements is much more soluble if digested along with cereals and vegetables than with meat and fish [2]. The broad conclusions of these experiments were that: a) acidity enhances solubility, b) enzyme action changes solubility, c) processing can affect solubility, and d) presence of other foods can affect solubility. Even where an element was soluble, there were indications of changes in chemical form as a result of enzyme action, processing or the presence of other foods. In devising an investigation of these changes, the criteria were that it should be, i) with foods containing levels of toxic elements typical of those in the normal food supply; ii) with systems which,
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