Skip to main content
. 2022 Nov 11;10:1001760. doi: 10.3389/fpubh.2022.1001760

Table 1.

Epidemiological studies on the effects of exposure to organophosphorus pesticides (OPs) on human auditory system.

OPs No. of subject Country Type of study Co-exposure to noise Methods Result Reference
Mixture 16246 Iowa or North Carolina
in USA
Cohort study Not specified Self-report Compared with no exposure,the odds ratio for the highest quartile of exposure was 1.17 (1.03 to 1.31) for OPs; and 1.11 (0.99–1.24) for fonofos. (29)
Mixture (methyl parathion, chlorpyrifos, diethyl succinate) 127 The Pontal do Paranapanema region in Brazilian The observational, prospective, and cross-sectional study Not specified Pure tone audiometry, Vocal audiometry, Immittance testing Auditory complaint and tinnitus with high pitch, had a higher incidence (p < 0.05) in groups exposed to pesticides in comparison to the control group (31)
Mixture (insecticides, herbicides, and fungicides) 175 conventional farmers and 176 organic farmers Three agricultural areas in Thailand Cross-sectional study Agricultural noise exposure Standard pure tone audiometry (PTA);
An interview
The highest category of cumulative insecticide exposure (score-years), cumulative OPs exposure (score-years) and cumulative noise exposure (dB(A)-years) were associated with an increased high-frequency band hearing threshold among conventional farmers (32)
Organophosphorus compound (OPC) 100 patients of OPC poisoning India Prospective observational study Not specified Distortion Product Oto Acoustic Emission (DPOAE);
Brain evoked response audiometry (BERA)
DPOAE was absent in 17 patients with respiratory failure and 51 patients without respiratory failure. BERA showed significant prolongation in wave I, wave III and wave V latencies in both the groups. (33)
Mixture (organophosphates) 18 rural workers Teresópolis, RJ in Brazilian Cohort cross-sectional study Not specified Otorhinolaryngological, audiological, and vestibular examination; Questionnaires. Sixteen workers had irritative peripheral body balance disorder and seven workers had sensorineural hearing loss. Agricultural pesticides cause vestibular alterations through a slow and silent intoxication. (37)
Organophosphates and pyrethroid insecticides 98 workers exposed to insecticides and 54 non-exposed workers Brazil Cohort study Not specified An interview;
Frequency patterns and duration patterns testing
Relative risk for hearing dysfunction was 7.58 for the exposure group (95% CI 2.9–19.8) in comparison with the non-exposed group. (38)
Mixture (DDT and BHC organophosphates) 98 Brazil Cross-sectional prevalence studies Noise Tonal audiometric test The intensity of hearing loss in the group exposed to insecticides and noise was higher than in the group exposed to insecticides. The mean values of hearing loss intensity were increasing from 2 to 6 kHz, and decreasing by 8 kHz in relation to 6 kHz. (39)
Malathion 120 Not mentioned Retrospective study With noise Audiological interview; threshold tonal audiometry; Immittance measures The group with concurrent exposure to noise and pesticide presented a higher incidence of hearing loss than group exposed to noise alone. (40)
Mixture (organophosphates and pyrethroids) 56 Brazil Cross-sectional cohort study With noise Pure-tone audiometry; acoustic immittance measurement;
Brainstem auditory evoked potentials (BAEP);
Dichotic digits test (DDT) assessment; Transient evoked otoacoustic emissions (TEOAE)
Compared with control group, the absolute latency of wave III and wave V was delayed, while the latency between peaks I—III and I—V increased at 2–4 kHz in the group exposed to Insecticides. (41)
Mixture (chlorpyrifos, diazionon, fonofos, malathion, parathion-ethyl, parathion-methyl, profenofos, terbufos) 116 infants China Cohort study Not specified ABR Exposure to multiple pesticides prenatally caused longer central conduction time and wave V latencies (44)
Organophosphate insecticide 359 healthy women and 237 of their infants China Cohort study Not specified ABR Many infants missed ABR wave I and III data at 18 months (n = 132); Methamidophos exposure was significantly different among infants with and without 18-month ABR data (45)