Reigart, Routt, Roberts, James, “Pesticides in Children,” Pediatric Clinics of North America, 2001, 48:5, DOI: 10.1016/S0031-3955(05)70368-0.
The term pesticide includes various agents devised to control a wide range of pests. Although the public perception of pesticides is often that pesticide is synonymous with, most pesticide usage and much acute and chronic toxicity from pesticides are not related to insecticidal agents. Other important classes of pesticide agents are herbicides (for plants), fungicides (for fungi), nematocides (for nematodes), and rodenticides (for rodents). An additional important class is the fumigants, highly toxic volatile agents or gases that are used as broad-spectrum killing agents for many forms of plant and animal life. Although most pesticide agents are synthetic chemical toxicants, a significant and increasing proportion are biologic agents, such as Bacillus thuringiensis, a microbial insecticide. In addition, sulfur and other elemental chemicals have been used as pest-control agents but usually are not considered as “conventional” pesticides.
The most recent (1997) US Environmental Protection Agency () estimate of pesticide usage in the United States was 443 million kg (975 million lb) of .3 Of this enormous total, approximately 66% were herbicides and fungicides, which tend to have low in humans but may be persistent in the environment and in the human body. Some of these agents, including, for instance, vinclozolin, a fungicide, and atrazine, an herbicide, also are thought to be endocrine disruptor agents.
Children in the United States and elsewhere are exposed to enormous quantities of pesticides of various types, by multiple routes. Although some of this exposure is by ingestion of food and water—routes that are considered by the public to be primary—much exposure occurs in homes, gardens, and schools. A total of 34.5 million kg (76 million lb) of active pesticide ingredients were used in home and garden settings in this survey. Approximately 75% of home and garden pesticides are herbicides and fungicides, and approximately 22% are. The insecticides most used in homes and gardens are diazinon and chlorpyrifos, both , and carbaryl, an anticholinesterase carbamate. Recent decisions by the EPA to remove the approval for usage of diazinon and chlorpyrifos in homes and gardens is likely to cause a significant shift in patterns of insecticide usage. It is likely that there will be significant increases in the use of pyrethroid compounds, requiring more intense evaluation of the risks of these compounds to infants and children.
Although there is considerable public concern over pesticide usage and exposure, the quantity of pesticides used each year has remained relatively constant over the past 20 years. The concerns shared by the public, environmental activists, and many scientists have not resulted in appreciable decreases in usage of pesticides or in children’s exposure to pesticides.
In considering pediatric pesticide effects, it is essential to attend to issues of exposure and effect. Because children differ from adults in behavior, physiology, and physical configuration, their patterns of exposure are dramatically different. Likewise, differences in the biology of children, particularly as related to developmental effects, result in quantitatively and qualitatively different responses to pesticide exposure. In the case of children, a further important complication is the need to assess the risks for subclinical effects that may lead to lifetime morbidity. This morbidity may occur in the absence of the acute poisoning symptoms that often have dominated the consideration of pesticide effects on children.
Reigart, Routt, Roberts, James, “Recognition and Management of Pesticide Poisoning,” USOffice of Pesticide Programs, 2013, Sixth Edition.