Implementing food-based dietary guidelines for - United Nations ...
Implementing food-based dietary guidelines for - United Nations ...
Implementing food-based dietary guidelines for - United Nations ...
You also want an ePaper? Increase the reach of your titles
YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.
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