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Implementing food-based dietary guidelines for - United Nations ...

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S28<br />

Most of this discussion will draw on recent considerations<br />

of micronutrients [1, 2]. Additionally, there is<br />

a current international collaboration exploring systematic<br />

safety assessments of intakes of amino acids [3–5].<br />

Toxicological risk analysis and assessment<br />

The values derived by the risk assessment are estimates<br />

of the quantity of a substance that can be ingested daily<br />

over a lifetime without appreciable risk to health and<br />

are termed health-<strong>based</strong> guidance values [6–9]. These<br />

include the acceptable daily intake (ADI) [6]) and the<br />

tolerable intake (TI), which may be weekly (TWI) or<br />

daily (TDI) [8]. The ADI is applied <strong>for</strong> estimates of safe<br />

exposure <strong>for</strong> <strong>food</strong> additives, i.e., <strong>for</strong> chemicals that are<br />

permitted to be used in <strong>food</strong>s, and the TDI relates to<br />

contaminants and pollutants. The US Environmental<br />

Protection Agency has replaced ADI and TDI with the<br />

term reference dose (RfD), which has been defined<br />

as an estimate of the daily exposure in the human<br />

population that is likely to be without an appreciable<br />

risk of deleterious effects during a lifetime. All these<br />

definitions are framed to avoid implying that they<br />

are absolutely “safe”; they are advisory (although they<br />

might subsequently be translated into regulations) and<br />

are the products of a systematic process of risk analysis,<br />

of which risk assessment is one element.<br />

Risk analysis is “a detailed examination, including<br />

risk assessment, risk evaluation and risk management<br />

alternatives, per<strong>for</strong>med to understand the nature of<br />

unwanted, negative consequences to human life, health,<br />

property or the environment; an analytic process to<br />

provide in<strong>for</strong>mation regarding undesirable events:<br />

the process of quantification of the probabilities and<br />

expected consequences of identified risks” [10].<br />

The definitions used in the established process vary<br />

among the agencies involved, but with the maturation<br />

of the discipline and increased international and interagency<br />

harmonization, the definitions are very close and<br />

common wordings are emerging.<br />

In this process, the definition of a hazard is “the<br />

inherent property of a chemical to cause adverse effects<br />

depending upon the level of intake.” The modification<br />

of this to suit the needs of nutritional risk assessment<br />

(see above) is straight<strong>for</strong>ward [1]. An adverse effect is<br />

“a change in morphology, physiology, growth, development<br />

or lifespan of an organism which results in<br />

impairment of functional capacity or impairment of<br />

capacity to compensate <strong>for</strong> additional stress or increase<br />

in susceptibility to the harmful effects of other environmental<br />

influences. Decisions on whether or not any<br />

effect is adverse require expert judgment” [7]. Again,<br />

this is little different from the definition derived <strong>for</strong><br />

nutritional risk assessment.<br />

A risk is “the probability or likelihood that a hazard<br />

will actually cause harm to an individual or popula-<br />

tion group”<br />

In the model developed by the Food and Agriculture<br />

Organization/World Health Organization (FAO/WHO)<br />

and the Codex Alimentarius, Risk Analysis comprises<br />

three distinct steps: risk assessment, risk management,<br />

and risk communication. Although each is a distinct<br />

step, collectively they are intended to be a coherent<br />

and fluently progressive entity. This is a well-accepted<br />

model, because it provides a structure that ensures that<br />

any uncertainties, variabilities, or assumptions involved<br />

in the assessment can be identified, thereby enabling<br />

and encouraging a transparent explanation of the<br />

means by which these issues are compensated.<br />

Risk assessment<br />

P. J. Aggett<br />

In practice, the first step in risk analysis is that of<br />

“problem <strong>for</strong>mulation,” i.e., setting the key purpose<br />

and objective of the exercise. Usually this is done by<br />

the risk managers and regulators who will be responsible<br />

<strong>for</strong> managing the risk of any particular exposure<br />

and communicating to the public about the risk and<br />

the strategy to manage it.. Often, but not necessarily<br />

always, problem <strong>for</strong>mulation may involve consultation<br />

with those who have the task of assessing the hazards<br />

and any attendant risks.<br />

Once the problem has been set, the first phase in risk<br />

analysis, risk assessment, can start. Since this involves<br />

identifying and prioritizing hazards and the exposures<br />

at which they happen, this is the process that is most<br />

relevant <strong>for</strong> this paper. Risk assessment comprises four<br />

stages: hazard identification, hazard characterization<br />

(sometimes called dose–response assessment), exposure<br />

assessment, and risk characterization. Each is<br />

briefly described later, but in essence they involve first<br />

a full review of all relevant in<strong>for</strong>mation and a qualitative<br />

identification and evaluation of all adverse effects<br />

associated with high exposures (hazard identification),<br />

followed by a quantitative estimation of risk <strong>for</strong> each<br />

adverse effect (hazard characterization). Assessment of<br />

dose–response often includes a modeling exercise to<br />

extrapolate from high to low levels of exposure.<br />

Hazard identification, as the determination of the<br />

relationship between the exposure to the chemical and<br />

one or more associated adverse effects, needs a full<br />

appraisal of in<strong>for</strong>mation to characterize the absorption,<br />

systemic distribution, metabolism, and elimination<br />

(i.e., toxicokinetics) of the chemical and the toxic<br />

effects that the chemical, or its metabolites, may have<br />

at tissue and cellular functional levels (i.e., toxicodynamics).<br />

Both human and animal model data are used.<br />

Some of these are systematically acquired through<br />

specific studies (table 1), and this applies particularly<br />

to chemicals that are proposed as <strong>food</strong> additives. Other<br />

data may be acquired more opportunistically, such as<br />

from case studies and incident reports. This is more

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