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Relationship between children’s environment and
organophosphate pesticide exposures among
children living in agricultural area, Thailand
Rohitrattana Juthasiri, Siriwong Wattasit, Tunsaringkarn Tanasorn,
Robson G. Mark, Fiedler Nancy
 

Presented by Ms.Juthasiri Rohitrattana, M.Sc.
College of Public Health Sciences, Chulalongkorn University, Thailand
Rationale





Pesticide use for agricultural purposes is rising in Thailand.
Organophosphate (OP) insecticide is one of the most
popular agents used for crop protection and known as
nervous system toxicants or cholinesterase inhibitor.
Chlorpyrifos is the most popularly used in rice fields in
Pathum Thani Province, Central Thailand.
Rationale





OP exposure has been associated with delays in mental
development, behavioral problems and poor short-term
memory and motor skill.
In Thailand, farms and residential areas are not totally
separated.
Child who lives near the agricultural area can be exposed
to the pesticides via their environment and daily activities.
5
Objectives

To compare the pesticide exposure between
children living in rice area and in aquaculture area.
 To determine the relationship between children’s
environment and activities with pesticide exposure
among children living in agricultural areas


6
Methodology





Research design: cross-sectional study
Study population:
- Healthy children aged 6 to 8 years old (N = 53)
- 24 children from rice area (high OP application
area) in Khlong Luang District, Pathum Thani Province,
Thailand.
- 29 children from aquaculture area in Lum Luk Ka
District, Pathum Thani Province, Thailand.
Data collection: October 2011
Rice farming area
Aquacultural area
Measurement tools
 Questionnaires

– Face-to-face interview with the
participant’s parents about their child’s activities
and environments.
 Urine samples - First morning void urine
samples were analysed for the OP class-specific
metabolites (diakylphosphate; DAPs).

10
Results

11
Children’s environmental conditions.
Characteristics

Study area
Aquaculture area

Rice area
(n=24)
Rice farmer family

n
24

Significance
(χ2 test)

(n=29)
%
100

n
0

%
0

Proximity to rice farm:

p
<0.001
<0.001

≤500 m.

24

100

10

34.5

>500 m.

0

0

19

65.5

Frequency of floor cleaning:

0.29

Not everyday

6

25.0

4

13.8

Everyday

18

75.0

25

86.2

Frequency of OPs usage on farm:

<0.001

Never

1

4

29

100

1 time/month

23

96

0

0

12
Children’s activities
Activities

Study area

Significance

Rice area

Aquaculture area

(n=24)

(n=29)

(χ2 test)

n

%

n

%

P

Washing hand before
consuming meals

13

54.2

21

72.4

0.36

Playing on rice farm

12

52.2

5

17.9

0.01

Observable dirt on body

19

82.6

16

57.1

0.05

 No significant differences in the time spent in play (indoors or
outdoors) and object-to-mouth behavior.

13
Concentrations of organophosphate metabolites in urine
samples

Rice children had significantly higher DAP concentrations compared with
aquaculture children (Mann-Whitney U test; p<0.05).
14
Concentrations of organophosphate metabolites in urine samples

 Diethylthiophosphate (DETP) and diethylphosphate
(DEP) were commonly found in urine samples.
 DEP and DETP had a positively correlation with DAPs
(DEP; rho=0.92, p<0.001, DETP; rho=0.69, p<0.001).
 Suggesting that the primary OP to which participants
were exposed was chlorpyrifos.

15
Relationship between children’s
environment and activities with pesticide
exposure


From linear regression analysis, DAP concentrations had

significant associations with being a member of rice farming
family (β=0.32, p=0.02) and frequency of OP use on farms
(β=0.39, p=0.006).
Children

of rice farmers lived in closer proximity to farms, spent

more time played while parents worked on the farm and tended
to have more dirt on their bodies.
Take-home

contaminants from farmers to their family member

was a possible pathway of OP exposure.
16
Conclusions
 Children living near rice field had higher OP exposure
than who living near aquacultural areas.
 The levels of OP metabolites in participants living near
rice areas also greater than other areas in Thailand.
 The risk of pesticide exposure is undoubtedly a concern
that require public health attention.
 The neurobehavioral deficits among children with longterm OP exposure will be our further study.
Acknowledgements






The NIH research grant (NIEHS R21ES18722)
Thai Fogarty International Training and Research in
Environmental and Occupational Health (ITREOH grant
number D43TW007849-01NIHFIC)
The 90th Anniversary of Chulalongkorn University grant
Conference grant for Ph.D. student, Graduate School,
Chulalongkorn University
19

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Relationship between children’s environment and organophosphate pesticide exposures among children living in agricultural area, Thailand

  • 1. Relationship between children’s environment and organophosphate pesticide exposures among children living in agricultural area, Thailand Rohitrattana Juthasiri, Siriwong Wattasit, Tunsaringkarn Tanasorn, Robson G. Mark, Fiedler Nancy   Presented by Ms.Juthasiri Rohitrattana, M.Sc. College of Public Health Sciences, Chulalongkorn University, Thailand
  • 2. Rationale    Pesticide use for agricultural purposes is rising in Thailand. Organophosphate (OP) insecticide is one of the most popular agents used for crop protection and known as nervous system toxicants or cholinesterase inhibitor. Chlorpyrifos is the most popularly used in rice fields in Pathum Thani Province, Central Thailand.
  • 3. Rationale    OP exposure has been associated with delays in mental development, behavioral problems and poor short-term memory and motor skill. In Thailand, farms and residential areas are not totally separated. Child who lives near the agricultural area can be exposed to the pesticides via their environment and daily activities.
  • 4.
  • 5. 5
  • 6. Objectives To compare the pesticide exposure between children living in rice area and in aquaculture area.  To determine the relationship between children’s environment and activities with pesticide exposure among children living in agricultural areas  6
  • 7. Methodology    Research design: cross-sectional study Study population: - Healthy children aged 6 to 8 years old (N = 53) - 24 children from rice area (high OP application area) in Khlong Luang District, Pathum Thani Province, Thailand. - 29 children from aquaculture area in Lum Luk Ka District, Pathum Thani Province, Thailand. Data collection: October 2011
  • 10. Measurement tools  Questionnaires – Face-to-face interview with the participant’s parents about their child’s activities and environments.  Urine samples - First morning void urine samples were analysed for the OP class-specific metabolites (diakylphosphate; DAPs). 10
  • 12. Children’s environmental conditions. Characteristics Study area Aquaculture area Rice area (n=24) Rice farmer family n 24 Significance (χ2 test) (n=29) % 100 n 0 % 0 Proximity to rice farm: p <0.001 <0.001 ≤500 m. 24 100 10 34.5 >500 m. 0 0 19 65.5 Frequency of floor cleaning: 0.29 Not everyday 6 25.0 4 13.8 Everyday 18 75.0 25 86.2 Frequency of OPs usage on farm: <0.001 Never 1 4 29 100 1 time/month 23 96 0 0 12
  • 13. Children’s activities Activities Study area Significance Rice area Aquaculture area (n=24) (n=29) (χ2 test) n % n % P Washing hand before consuming meals 13 54.2 21 72.4 0.36 Playing on rice farm 12 52.2 5 17.9 0.01 Observable dirt on body 19 82.6 16 57.1 0.05  No significant differences in the time spent in play (indoors or outdoors) and object-to-mouth behavior. 13
  • 14. Concentrations of organophosphate metabolites in urine samples Rice children had significantly higher DAP concentrations compared with aquaculture children (Mann-Whitney U test; p<0.05). 14
  • 15. Concentrations of organophosphate metabolites in urine samples  Diethylthiophosphate (DETP) and diethylphosphate (DEP) were commonly found in urine samples.  DEP and DETP had a positively correlation with DAPs (DEP; rho=0.92, p<0.001, DETP; rho=0.69, p<0.001).  Suggesting that the primary OP to which participants were exposed was chlorpyrifos. 15
  • 16. Relationship between children’s environment and activities with pesticide exposure  From linear regression analysis, DAP concentrations had significant associations with being a member of rice farming family (β=0.32, p=0.02) and frequency of OP use on farms (β=0.39, p=0.006). Children of rice farmers lived in closer proximity to farms, spent more time played while parents worked on the farm and tended to have more dirt on their bodies. Take-home contaminants from farmers to their family member was a possible pathway of OP exposure. 16
  • 17. Conclusions  Children living near rice field had higher OP exposure than who living near aquacultural areas.  The levels of OP metabolites in participants living near rice areas also greater than other areas in Thailand.  The risk of pesticide exposure is undoubtedly a concern that require public health attention.  The neurobehavioral deficits among children with longterm OP exposure will be our further study.
  • 18. Acknowledgements     The NIH research grant (NIEHS R21ES18722) Thai Fogarty International Training and Research in Environmental and Occupational Health (ITREOH grant number D43TW007849-01NIHFIC) The 90th Anniversary of Chulalongkorn University grant Conference grant for Ph.D. student, Graduate School, Chulalongkorn University
  • 19. 19