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Combined Actions and Interactions of Chemicals in Mixtures

Combined Actions and Interactions of Chemicals in Mixtures

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Physicochemical <strong>in</strong>teractions will therefore not be considered <strong>in</strong> any detail <strong>in</strong> this<br />

report.<br />

The processes lead<strong>in</strong>g to a biological <strong>and</strong>/or toxicological response from exposure<br />

<strong>of</strong> animals <strong>and</strong> humans to a given chemical can be divided <strong>in</strong>to two dist<strong>in</strong>ct parts,<br />

toxicok<strong>in</strong>etics <strong>and</strong> toxicodynamics (Renwick 1993, IPCS 1994). Toxicok<strong>in</strong>etics<br />

relates to those processes that determ<strong>in</strong>e the extent <strong>and</strong> duration <strong>of</strong> exposure at the<br />

target organ or site <strong>of</strong> toxicity to the active chemical species (parent compound or<br />

metabolite). Toxicok<strong>in</strong>etics <strong>in</strong>volves processes such as absorption, distribution,<br />

biotransformation, <strong>and</strong> excretion <strong>of</strong> the compound <strong>and</strong> metabolites.<br />

Toxicodynamics refers to the processes <strong>in</strong>volved <strong>in</strong> the translation <strong>of</strong> such<br />

exposure <strong>of</strong> the target organ or site <strong>of</strong> action <strong>in</strong>to the generation <strong>of</strong> a toxic effect.<br />

Toxicodynamics may <strong>in</strong>volve a large number <strong>of</strong> different processes that determ<strong>in</strong>e<br />

the mechanisms <strong>of</strong> action <strong>of</strong> a given chemical. These processes may <strong>in</strong>volve<br />

<strong>in</strong>hibition <strong>of</strong> cellular enzymes, damage through b<strong>in</strong>d<strong>in</strong>g to prote<strong>in</strong>s or DNA, or<br />

<strong>in</strong>teractions at endogenous receptor sites, just to mention a few events that may<br />

pertubate the normal homeostasis <strong>of</strong> the organism or tissue.<br />

2.2 No <strong>in</strong>teraction<br />

Accord<strong>in</strong>g to Plackett <strong>and</strong> Hewlet (Table 1.3.1) there are two types <strong>of</strong> comb<strong>in</strong>ed<br />

action without <strong>in</strong>teraction: simple similar action (dose addition, Loewe additivity)<br />

<strong>and</strong> simple dissimilar action. This latter type conta<strong>in</strong>s two concepts: effect or<br />

response additivity <strong>and</strong> Bliss <strong>in</strong>dependence. The <strong>in</strong>dependence criterion seems not<br />

to be widely used <strong>in</strong> toxicology (Groten et al., 2001). The response to a mixture <strong>of</strong><br />

compounds depends not only on the dose, but also on the correlation <strong>of</strong> tolerances<br />

between the effects <strong>of</strong> the chemicals <strong>in</strong> the mixture, which can vary between –1<br />

<strong>and</strong> +1 (Bliss 1937). There is a complete negative correlation (r =-1) between the<br />

effects <strong>of</strong> two chemicals if the <strong>in</strong>dividuals that are most susceptible to one toxicant<br />

are least susceptible to the other, while a complete positive correlation (r = +1)<br />

exists if the <strong>in</strong>dividuals most susceptible to one toxicant are also most susceptible<br />

to the other.<br />

2.2.1 Simple similar action (dose addition, Loewe additivity)<br />

Simple similar action (simple jo<strong>in</strong>t action or concentration/dose addition) is a non<strong>in</strong>teractive<br />

process <strong>in</strong> which the chemicals <strong>in</strong> the mixture do not affect the toxicity<br />

<strong>of</strong> one another. All the chemicals <strong>of</strong> concern <strong>in</strong> the mixture act on the same<br />

biological site, by the same mechanism <strong>of</strong> action, <strong>and</strong> differ only <strong>in</strong> their potencies.<br />

The correlation <strong>of</strong> tolerances is completely positive (r = +1) <strong>and</strong> each chemical<br />

contributes to the toxicity <strong>of</strong> the mixture <strong>in</strong> proportion to its dose, expressed as the<br />

percentage <strong>of</strong> the dose <strong>of</strong> that chemical alone that would be required to obta<strong>in</strong> the<br />

given effect <strong>of</strong> the mixture. Thus the <strong>in</strong>dividual components <strong>of</strong> the mixture act as if<br />

they were dilutions <strong>of</strong> the same toxic compound <strong>and</strong> their relative potencies are<br />

assumed to be constant throughout all dose levels. An important implication is that<br />

<strong>in</strong> pr<strong>in</strong>ciple no threshold exists for dose additivity.<br />

Simple similar action serves as the basis for the use <strong>of</strong> “toxic equivalency factors”<br />

<strong>of</strong>ten used to describe the comb<strong>in</strong>ed toxicity <strong>of</strong> isomers or structural analogues.<br />

Additive effects are described mathematically us<strong>in</strong>g summation <strong>of</strong> doses <strong>of</strong> the<br />

<strong>in</strong>dividual compounds <strong>in</strong> a mixture adjusted for differences <strong>in</strong> potencies. This<br />

method is assumed to be only valid for compounds that produce l<strong>in</strong>ear dose<br />

response curves. Probably, the best validated example <strong>of</strong> a group <strong>of</strong> compounds<br />

that obey the pr<strong>in</strong>ciples <strong>of</strong> simple similar actions are the diox<strong>in</strong>s (polychlor<strong>in</strong>ated<br />

dibenzo-p-diox<strong>in</strong>s <strong>and</strong> dibenz<strong>of</strong>urans) that produce most (if not all) <strong>of</strong> their<br />

toxicities through <strong>in</strong>teraction with the Ah-receptor.<br />

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