Table 3.
Parameter | Score assigned
|
||
---|---|---|---|
2 | 1 | 0 | |
Exposure assessment | Specific biomarkers (e.g., blood chlorpyrifos) | General biomarkers (e.g., DAP metabolites) | Ecological dataa; Hospital records of intoxication or poisoning |
Neurodevelopmental assessmentb | Standardized, well-validated tests for diagnostic or neurobiologically based markers of development | Screening tests, interviews, checklists or questionnaires. Older versions of well validated tests. Not widely used tests in neurodevelopmental assessment | Selected sections of full test batteries |
Study design | Longitudinal, exposures precede outcome | Case control | Cross-sectional, case study |
Sample size | >200 | ≥50 | <50 |
Confounder control | Good control for important confoundersc and standard variables | Standard variables controlled in analysesd | Not considered |
Categories of rating: 0–2 = low rating, 3–7 = intermediate rating, 8–10 = high rating.
Ecological data: Exposure assumed by the proximity to places where pesticides were applied or in children or adolescents that worked in farms.
For specific characteristics of the neurodevelopmental assessment instruments see Table 2.
Important confounders to control in this class of studies could be: Parental intelligence, quality of the home environment, potential factors on the causal pathway (birth weight, gestational age, abnormal reflexes), other suspected neuro-toxicants (i.e., PCBs, lead, and DDT), other high-level exposures in the population (i.e., β-hexachlorocyclohexane and hexa-chlorobenzene), exposure to environmental tobacco smoke (ETS).
Standard variables considered: age, sex, education, income, race/ethnicity.