(Part of Pesticide Issues Conference)
Daniel L. Sudakin
Pacific Northwest Agricultural Safety and Health Center
Objectives
- To appreciate the complexity of monitoring, managing, preventing acute pesticide managing, preventing acute pesticide exposures
- To briefly focus on specific pesticide classifications of concern for acute exposures
-
2.4 million human exposures reported in 2002
- 92.3% residential exposures
- 2.2% of exposures in a workplace
- 51.6% of cases involved children < 6 years of age
- 96,112 human exposures to pesticides
- 4% of total exposures reported to poison centers
- Most frequently implicated pesticides.
- 4% of total exposures reported to poison centers
Table 17A. Substances Most Frequently Involved in Human Exposures
Substance |
No. |
%* |
| Analgesics | 256,843 | 10.8 |
| Cleaning substances | 225,578 | 9.5 |
| Cosmetics and personal care products | 219,877 | 9.2 |
| Foreign bodies | 119,323 | 5.0 |
| Sedatives/hypnotics/anti psychotics | 111,001 | 4.7 |
| Topicals | 105,815 | 4.4 |
| Cough and cold preparations | 100,612 | 4.2 |
| Antidepressants | 99,860 | 4.2 |
| Bites/envenomations | 98,585 | 4.1 |
| Pesticides | 96,112 | 4.0 |
| Plants | 84,578 | 3.6 |
| Food products, food poisoning | 75,813 | 3.2 |
| Alcohols | 69,215 | 2.9 |
| Antihistamines | 69,107 | 2.9 |
| Antimicrobials | 63,372 | 2.7 |
| Cardiovascular drugs | 61,056 | 2.6 |
| Hydrocarbons | 59,132 | 2.5 |
| Chemicals | 54,623 | 2.3 |
Note: Despite a high frequency of involvement, these substances are not necessarily the most toxic, but rather may only be the most readily accessible.
*Percentages are based on the total number of human exposures (2,380,028) rather than the total number of substances.
Watson WA et al., (2003): 2002 Report of the AAPCC, TESS Am J Emerg Med 21(5)
Table 18. Categories with Largest Numbers of Deaths
Substance |
No. |
% of All Exposures in Category |
| Analgesics | 659 | .257 |
| Sedative/hypnotics/psychotics | 364 | .328 |
| Antidepressants | 318 | .318 |
| Stimulants and street drugs | 242 | .528 |
| Cardiovascular drugs | 181 | .296 |
| Alcohols | 139 | .200 |
| Chemicals | 50 | .091 |
| Anticonvulsants | 65 | .181 |
| Gases and fumes | 44 | .106 |
| Antihistamines | 71 | .103 |
| Muscle relaxants | 52 | .260 |
| Hormones and hormone antagonists | 33 | .062 |
| Cleaning substances | 33 | .013 |
| Automotive products | 30 | .213 |
| Cough and cold preparations | 22 | .022 |
| Pesticides | 18 | .019 |
Note: Tables 18, 22A and 22B are based on an unlimited number of substances coded per exposure, while Table 21 only includes up to 3 substances per case.
Pesticides implicated in fatal cases (2002): Sulfuryl fluoride Paraquat Strychnine Brodifacoum Dinitrophenol(?) OP’s
Strengths, Limitations of Poison Center Strengths, Limitations of Poison Center Data: Acute Pesticide Exposures Data: Acute Pesticide Exposures
-
Strengths
- Number of cases
- Ease of access
- 24 hour/day service Toll-free access in U.S.
- Consistency of reporting mechanism
- Current initiatives in
toxicosurveillance
- Electronic reporting of acute pesticide exposures from PCC's to State Health Depts.
- Real-time data uploading and
analysis by CDC
- Temporal, spatial trends
- Limitations
- May not be capturing occupational exposures
- High-risk population
- Limited specificity of
reporting
- Identity of active ingredient
- EPA Reg. #
- Details on circumstances
surrounding exposure
- Important for unintentional exposures
- May not be capturing occupational exposures
| 1994 | 1995 | 1996 | 1997 | 1998 | Total | |
| Arsenates | 13 | 9 | 9 | 9 | 6 | 46 |
| Organophosphate | 215 | 183 | 152 | 151 | 168 | 869 |
| OP + carbamate | 10 | 18 | 7 | 18 | 14 | 67 |
| OP + chlorinated HC | 2 | 1 | 2 | 2 | 1 | 8 |
| OP + other substance | 9 | 17 | 11 | 15 | 12 | 64 |
| OP + carbamate + chlorinated HC | 2 | 0 | 1 | 0 | 0 | 3 |
| Carbamate | 49 | 42 | 32 | 44 | 33 | 200 |
| Carbamate + other | 11 | 4 | 5 | 5 | 7 | 32 |
| Chlorinated HC | 45 | 47 | 63 | 75 | 39 | 269 |
| Chlorinated HC + other | 2 | 3 | 4 | 2 | 0 | 11 |
| Borates | 69 | 69 | 35 | 50 | 67 | 290 |
| Piperonyl butoxide + pyrethrins | 82 | 106 | 64 | 84 | 94 | 430 |
| Pyrethrins | 64 | 100 | 64 | 92 | 82 | 402 |
| Rotenone | 3 | 2 | 1 | 2 | 2 | 10 |
| Metaldehyde | 20 | 18 | 31 | 25 | 42 | 136 |
| Piperonyl Butoxide | 1 | 3 | 3 | 1 | 2 | 10 |
| Nicotine | 0 | 1 | 1 | 0 | 0 | 2 |
| Misc repellents | 68 | 126 | 67 | 71 | 48 | 380 |
| Other insecticides | 24 | 17 | 20 | 26 | 25 | 112 |
| Veterinary insecticide | 61 | 54 | 41 | 50 | 47 | 253 |
| Unknown | 58 | 56 | 40 | 54 | 60 | 268 |
| Total Carbamates | 65 | 51 | 44 | 50 | 41 | 251 |
| Total Organophosphates | 238 | 219 | 173 | 186 | 195 | 1011 |
| Total OP + carbamates | 303 | 270 | 217 | 236 | 236 | 1262 |
| Total Insecticides | 808 | 876 | 653 | 776 | 749 | 3862 |
| Carbamate | 5 | 5 | 7 | 1 | 1 | 19 |
| Mercurial | 0 | 0 | 0 | 0 | 0 | 0 |
| Non-mercurial | 9 | 8 | 8 | 4 | 5 | 34 |
| Unknown | 19 | 13 | 19 | 8 | 13 | 72 |
| Phthalimide | 6 | 4 | 2 | 2 | 2 | 16 |
| Total Fungicides | 39 | 30 | 36 | 15 | 21 | 141 |
| Strychnine | 7 | 5 | 1 | 8 | 5 | 26 |
| Short-acting anticoagulant | 5 | 5 | 6 | 7 | 7 | 30 |
| Long-acting anticoagulant | 193 | 130 | 74 | 90 | 119 | 606 |
| Others | 12 | 8 | 12 | 8 | 7 | 47 |
| Total Rodenticides | 217 | 148 | 93 | 113 | 138 | 709 |
| 2,4- or 2,4,5-T | 99 | 112 | 85 | 82 | 112 | 490 |
| Paraquat | 2 | 2 | 4 | 3 | 6 | 17 |
| Diquat | 2 | 4 | 1 | 2 | 4 | 13 |
| Others | 113 | 144 | 108 | 138 | 93 | 596 |
| Total Herbicides | 216 | 262 | 198 | 225 | 215 | 1116 |
| Total Pesticides | 1280 | 1316 | 980 | 1129 | 1123 | 5828 |
BZ Horowitz, S Griffin, CL Thomsen (2002): Pesticide-Related Illnesses: Are Poison Centers Reporting to the State Health Department?
Vet Hum Toxicol; 44(1):49-51.
- Over 5-year period, Oregon Poison Center receives ~1,000 calls/year for acute pesticide exposures
- Insecticides most frequently implicated
- OP’s, OP/carbamates, pyrethrin, pyrethroids
- % of OPC cases reported to State Health Department ….?

-
Active ingredient exists as a gas
- Relevant to inhalation pathways of exposure
- Diverse chemical structures
- Utilized to control pests in enclosed spaces, soil, and structures
- Many are restricted use
- Modern epidemiological data suggest fewer exposure cases than other pesticide classes
- Higher case-severity and case-fatality rate than
fungicides
- Many exposures are accidental
- Applicators, workers, non-occupational (residential)
- Many exposures are accidental
- Scenarios of concern: Inadequate ventilation of a treated structure, unanticipated cross-ventilation from a treated structure

- Highly lipid soluble
- Well-absorbed via inhalation pathways
- Wide volume of distribution
- CNS, liver, kidneys are target organs
- Me-Br is strong alkylating agent
- Cell membrane disruption
- Inhibition of critical enzyme function
- Metabolism of MeBr occurs rapidly
- Parent compound (MeBr MeBr) not usually detectable in tissues
- Management of overexposure is supportive
- No antidotes are available
- Decomposition products of phosphide fumigants include phosphine gas, phosphoric acid
- Phosphine inhibits electron transport chain
-
Mechanism similar to cyanide
- Unlike cyanide, there are no specific antidotes for gas
- Reliable biomarkers of exposure are not readily available
-
Mechanism similar to cyanide
- Acute inhalation overexposure
- Pulmonary injury, cardiogenic shock, neurological depression

- http://www.cdc.gov/niosh/99-126.html
- A review of 205 occupational exposure cases
- Common accidental exposure scenarios
- Lack of proper handling during fumigant application
- Failure to monitor air concentrations during application
- Failure to use appropriate respiratory equipment
- Improper disposal of unused fumigant products
- Incidental exposure from nearby fumigant application
- Majority of exposures associated with agricultural applications
- Most symptomatic exposures occurred among non-applicators
- Workers in proximity to or entering recently treated areas

Fumigants and Acute Toxicity
- Inhalation pathways of exposure
- Broad, non-selective mechanisms of toxicity
- Relevance of major morbidity, mortality from accidental exposures
- Applicators and non-applicators (bystanders)
- In most cases, biomarkers are of limited or no utility
- Specific therapies after overexposure are not available
- Need for vigilance in prevention
- Education, training, engineering controls, and appropriate use of PPE

- Insecticides with a common mechanism of toxicity
- Inhibitors of acetylcholinesterase
- Vary in chemical properties, dermal absorption, potency
- Inhibitors of acetylcholinesterase
- Acute overexposure results in cholinergic signs, symptoms
- Excess acetylcholine at muscarinic, nicotinic
receptors
- Muscarinic SLUDGE toxidrome: Salivation,
Lacrimation, Urinary incontinence,
Diarrhea, GI symptoms, Eyes (miosis) - Nicotinic signs
- Fasiculations, weakness, acute paralysis (in worst-case scenario)
- Muscarinic SLUDGE toxidrome: Salivation,
Lacrimation, Urinary incontinence,
- Excess acetylcholine at muscarinic, nicotinic
receptors
- Blood (serum and RBC) monitoring
- Cholinesterase enzyme activity as a biomarker of effect for OP’s, carbamates
- Difficulties, and challenges in cholinesterase monitoring as biomarker
- Reliability (inter-laboratory) Reliability (inter-laboratory)
- Variation in normal reference ranges
- Rapid recovery in cholinesterase activity after overexposure to N-methyl carbamates
- Importance of education, engineering controls, appropriate use of required PPE to reduce unnecessary exposure

Other Insecticides: Pyrethroids and Acute Toxicity
- Commonly utilized in agriculture, residential settings, public health (vector control)
- Mechanism of toxicity
- Prolong deactivation of sodium channels, excitation of nerve fibers
- Systemic intoxication is rare
- Local effects from dermal overexposure to concentrated formulations
- Transient paresthesias (12-24 hours)
- Usually occur in absence of any signs of skin injury
- Irritant effects (eye, throat, respiratory irritation) from inhalation overexposure

Insecticides and Acute Toxicity: Misapplication

-
Content of 19 “bug-bombs” released within a 470 sq. foot residence
- Product label indicated use application for 700 square feet
- Pilot light ignited the gas that had accumulated, resulting in explosion
- The Label is the Law

-
Imidacloprid
- Neonicotinoid family of insecticides
- Selective for the nicotinic acetylcholine receptor of the insect
- Targets the insect nervous system
- Poor penetration across blood-brain barrier in mammals
- Registered applications in agriculture, structural pest control, pet care (topical structural solution)
- Experience with human overexposure is very limited
Newer Insecticides
- A case of intentional (ingestion) poisoning (Wu, 2001)
- Farmer ingested 100 mL of insecticide
formulation
- 9.7% imidacloprid
- < 2 % surfactant
- Remainder: N-methyl pyrrolidone
- Clinical course: initial drowsiness, dizziness,
abdominal pain, vomiting GI endoscopy revealed corrosive injury
- Mainly upper GI tract
- Individual recovered, discharged at 4 days post-ingestion
- Were most significant effects (GI tract
injury) caused imidacloprid or N-methylpyrolidone?
-
Authors suggest N-methylpyrolidone as
more likely explanatory factor
- dermal, ocular effects from occupational exposures in humans
- Low potency of imidacloprid as skin, eye irritant in animal studies
-
Authors suggest N-methylpyrolidone as
more likely explanatory factor
- Health care providers need to consider the entire formulation when assessing risks after acute overexposure
- Intended to educate health
care providers
- Importance of exposure history Importance of exposure history
- Understanding prevention
- Engineering controls, PPE, decontamination,
- Clinical assessment
- Biomarkers of exposure
- Role of public health surveillance, other State Agencies
- Examples:
- Pyrethroids and paresthesias
- Inhalation risks of phosphide fumigants
- Pesticide incident reporting
Daniel L. Sudakin, M.D., M.P.H.
Assistant Professor
Department of Environmental and Molecular Toxicology
Oregon State University
sudakind@ace.orst.edu
NPIC: http://www.npic.orst.edu/
Disclaimer and Reproduction Information: Information in NASD does not represent NIOSH policy. Information included in NASD appears by permission of the author and/or copyright holder. More
Reviewed for NASD: 06/2006
