COMSUMPTION RISK ASSESSMENT OF PESTICIDES...
Transcript of COMSUMPTION RISK ASSESSMENT OF PESTICIDES...
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COMSUMPTION RISK ASSESSMENT OF PESTICIDES
CONTAMINATION IN CHILI FROM FARM TO FORK
WATTASIT SIRIWONG1,2,*, Sutisar Ooraikul3,4, Sumana Siripattanakul4,5,
Srilert Chotpantarat4,6, and Mark Robson2,7
1 College of Public Health Science, Chulalongkorn University, Bangkok, Thailand
2 Thai Fogarty ITREOH Center, Chulalongkorn University, Bangkok, Thailand
3 International Postgraduate Programs in Environmental Management, Graduate School, Chulalongkorn University, Bangkok, Thailand
4 National Center of Excellence for Environmental and Hazardous Waste Management (NCE-EHWM), Chulalongkorn University, Bangkok, Thailand
5 Faculty of Engineering, and NCE-EHWM, Ubon Ratchathani University, Ubonratchathani, Thailand
6 Department of Geology, Faculty of Science, Chulalongkorn University, Bangkok, Thailand
7 School of Environmental and Biological Sciences, Rutgers University, New Jersey, USA
The 3rd International Conference
on Public Health among Greater
Mekong Sub-Regional Countries 9 August 2011
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Chilli consumption
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The Ministry of Public Health reported “ Thai’s chilli consumption as approximately 5 g/day or 1 teaspoon. ”
Thai people, especially Northeasterners,
like chilli spiciness and prefer using the chilli
as an ingredient in their daily cooking.
Photo by: http://www.google.co.th/imghp?hl=th&tab=wi
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The chilli growing farmers have to use many loads of pesticides
both pre- and post- harvest to control chilli pests, protect the crops from
disease and meet high production of targets.
Literature review
3Photo by: Norkaew, Robson, Siriwong and Taneepanichskul, 2010
(Aksornsri, 2005; Nokaew, 2009)
Chilli-growing farmers had “Low knowledge, Less concern and Fair practices”
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Literature review
4Photo by: Siriwong et al., 2009-2010 Pesticide survey at Ubonrachthani province, North-eastern Thailand
Pesticide usage at Hua Rua sub-district, Ubonratchathani
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Literature review
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Saowanee Norkaew (2009) interviewed the 330 chilli-growing farmers at Hua Rua.
Organophosphate pesticides (OPPs)
are the most widely used in chilli farming area at Hua Rua
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Pesticide Uses
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Literature reviews
7Photo by: Norkaew, Robson, Siriwong and Taneepanichskul, 2010
Questionnaire based pesticide usage (February 2011)
Chlorpyrifos (podium 600), Profenofos (Selecon), EPN, Abamectin
Mixed more than 2 types of pesticide
Sprayed pesticide every 7 days by using potable pump
Applied over the recommendation dose
Collected chilli after 6 – 7 days of pesticide spraying.
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Pesticide residues
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Hua Rua survey, February 2011
The chilli are directly brought from the planting farms.
Pesticide residue
on Chilli
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Does the consumer get risk ?
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Yes or No ?
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Hypothesis
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“ Local people in a chilli farming area in Hua Rua sub-district,
Ubonratchathani province, Thailand are at risk of organophosphate
pesticide residue from their consumption. ”
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Objective
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To assess the human health risks associated with the consumption of
organophosphate pesticides residues of local people living in Hua Rua sub-
district, Ubonratchathani province, Thailand.
To analyze the residues of organophosphate pesticides in chilli products.
To compare the level of organophosphate pesticides residues on chilli with
the national and international Maximum Residue Limits (MRLs).
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Research Methodology
Analytical technique for determination of OPPs in chilli“QuEChERS method”
Questionnaire based dietary survey
Photo by: QuEChERS, 2010.
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Sampling SitesThe 11 sampling sites at Hua Rua Sub-districts, Ubonratchathani Province
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October 2010 – February 2011
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• Chilli sampling were conducted on February 2011.
• Thirty-three chilli samples (n = 33) were collected from 11 chilli farm areas in
Hua Rua after pesticide spraying 7 days.
• The collected chilli were maintained below 4°C during transportation
• OPPRs in chilli were extracted by using QuEChERS method and analyzed by
GC-FPD.
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Chilli Sampling
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Questionnaire based dietary survey
• Interview randomly for local people who consume chilli
in Hua Rua area
• Face-to-face interview
• The questionnaire consists of 3 parts:
1. General Information: age, gender, body weight, occupation,
education level
3. Health information: signs and symptoms
2. Consumption behavior: exposure information, intensity (how
much), frequency (how often) and duration (how long)
Questionnaire
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Photo by: Ooraikul, S., 2010
The questionnaire-based
socio-demographic and
dietary survey
October – December 2010
Methodology: Face-to-face interview
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Mean age (range 15-79 years) 47 ± 14
Sex
Female
Male
65
45
59.1
40.9
Mean weight (range 35-86 kg) 57 ± 10
CharacterizationHua Rua Sub-district, Ubonratchathani
Number (n = 110) Percentage (%)
The questionnaire-based socio-demographic and dietary survey
110 local people at Hua Rua were participant
Dietary Survey
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Occupation
Agriculturist / Farmer
Student
Business owner
Government officer / Officer
86
11
7
6
78.2
10.0
6.4
5.5
19
Education
≥ Elementary school
Secondary school
Bachelor’s degree
Diploma
83
20
4
3
75.5
18.2
2.7
3.6
CharacterizationHua Rua Sub-district, Ubonratchathani
Number (n = 110) Percentage (%)
Dietary Survey
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Dietary Survey
CharacterizationHua Rua Sub-district, Ubonratchathani
Number (n = 110) Percentage (%)
The source of chilli usage
Own chilli farm; Used pesticide
Own chilli farm; No pesticide usage
Local market; Used pesticide
Local market; Organic farm
72
20
16
2
65.5
18.2
14.5
1.8
Washing chilli before cooking
Never
Sometime
Always
11
18
81
10.0
16.4
73.6
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CharacterizationHua Rua Sub-district, Ubonratchathani
Number (n = 110) Percentage (%)
Spicy level (Chilli quantity)
Very spicy (≥ 7 chilli/menu)
Moderate spicy (6-4 chilli/menu)
Less spicy (1-3 chilli/plate)
No
39
51
20
0
35.5
46.4
18.2
0
Average chilli consumption (g/day) 18 ± 15*
* 1 Chilli 1.32 g
The average daily chilli consumption of local people in Hua Rua was 18 g/day
more than 3 times the average of general Thai (5 g/day).
Dietary Survey
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Step 1: Preparation and Extraction step
Step 2: Cleanup step
Step 3: Analysis
Photo by: QuEChERS, 2010
Pesticide Concentration Analysis: QuEChERS
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Column: DB-1701 (30.0 m, 0.25 mm i.d., 0.25 μm film)
Detector: Flame Photometric Detector (FPD)
Inj. Temp: 220°C
Det Temp: 250°C
Carrier Gas: He
Splitless: 0.75 minutes
Inj. Volume: 1 µl
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1. Dichlorvos
2. Acephate
3. Omethoate
4. Demeton-S-
methyl
5. Dimethoate
6. Tolclofos-methyl
7. Pirimiphos-
methyl
8. Malathion
9. Chlorpyrifos
10. Methidathion11. Prothiofos
12. Profenofos
13. Ethion
OPPRs analysis: GC-FPD
Organophosphate pesticide
LODs = 0.01 µg/mL
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OPPRs analysis
Chlorpyrifos
Profenofos
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OPPRs were identifiedby GC- FPD.
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Chlorpyrifos concentration
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0.65
0.75
0.72
0.17
0.36
0.41
1.27
1.38
1.01
0.51
0.65
0.90< 0.01< 0.01< 0.01< 0.01< 0.01< 0.01< 0.01< 0.01< 0.01
0.40
0.45
0.41< 0.01< 0.01< 0.01< 0.01< 0.01< 0.01
0.33
0.26
0.40
0.00 0.10 0.20 0.30 0.40 0.50 0.60 0.70 0.80 0.90 1.00 1.10 1.20 1.30 1.40 1.50
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
30
31
32
33
mg/kg
sample no.chlorpyrifos concentration
MRLs of chlorpyrifos 0.5 mg/kg
The levels of 9 chlorpyrifos contaminated chilli samples exceeded MRL
(< 0.01 – 1.38 mg/kg)
MRL reference: Codex Alimentarius, 2010
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Profenofos concentration
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6.29
5.79
5.49
0.81
0.74
1.13
5.33
5.08
4.77
1.08
1.17
1.49
1.44
1.94
1.18
4.89
3.34
2.51
2.55
2.05
1.51
2.09
1.83
2.14
3.80
4.83
3.28
0.52
0.68
0.90
2.03
2.40
2.60
0.00 0.50 1.00 1.50 2.00 2.50 3.00 3.50 4.00 4.50 5.00 5.50 6.00 6.50 7.00
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
30
31
32
33
mg/kg
sample no.
profenofos concentration
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MRLs of profenofos 5 mg/kg
The levels of 5 profenofos contaminated chilli samples exceeded MRL
(0.52 – 6.29 mg/kg)
MRL reference: Codex Alimentarius, 2010
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Human Health Risk Assessment
Analytical technique for
determination of OPPs in chilli“QuEChERS method”
Questionnaire survey
Photo by: QuEChERS, 2010.
Human Health
Risk Assessment
Human Health Risk Assessment
Hazard identification
Dose-response Assessment
Exposure Assessment
Risk Characterization
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1. Hazard Identification
“Major OPPs toxicological effects are an irreversible
inhibition of acetylcholinesterase enzyme (AChE)in the nervous system”
Human Health Risk Assessment
Chlorpyrifos and Profenofos are classified as
non-carcinogenic pesticide
ChlorpyrifosProfenofos
Organophosphate Pesticides (OPPs)
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Photo by: http://www.epa.gov/IRIS/
Human Health Risk Assessment
2. Dose-Response Assessment
Oral reference dose of Chlorpyrifos (RfD)
= 0.003 mg/kg-day (US EPA, 1988)
Oral reference dose of Profenofos (RfD)
= 0.0001 mg/kg-day (Jaipieam, 2009)
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Where,
ADD = Average Daily Dose (mg/kgday)
C = Pesticide concentration (mg/kg) Obtained from OPPs Analysis
AT = Averaging time (day); For non-carcinogenic effects, AT = ED in days
IR = Intake rate (kg chilli/day)
EF = Exposure frequency (days/year) Obtained from interview
ED = Exposure duration (years)
BW = Body weight (kg)
• Profenofos and chlorpyrifos are classified as non-carcinogen pesticide
• Average Daily Dose (ADD) is the expression of average exposures of substances
which have non-carcinogenic effect. (US EPA)
ADD = C × IR × EF × EDBW × AT
Human Health Risk Assessment
3. Exposure Assessment
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1.07
10.10
24.20
8.00
45.90
110.00
0.00
20.00
40.00
60.00
80.00
100.00
120.00
Mean 95th Maximun
ADD Chlorpyrifos
ADD Profenofosx 10-4 mg/kg/day
Average Daily Dose (ADD)
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• Profenofos and chlorpyrifos are classified as non-carcinogen pesticide
• Reference dose (RfD) is the criterion in non-carcinogenic risk characterization.
Where,
HQ 1 Acceptable level (no concern)
HQ 1 Adverse non-carcinogenic effect concern (risk)
Evaluation of non-carcinogenic toxicity of Individual risk computes by
using the hazard quotient (HQ). (US EPA)
4. Risk Characterization
Human Health Risk Assessment
HQ = Exposure = ADDRfD RfD
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HQ Chlopyrifos
33
0.00010.036
0.337
0.807
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1
Minimum Mean 95th Maximum
Acceptable level
HQ chlorpyrifos
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HQ Profenofos
34
0.09
8.00
45.90
110.00
0
10
20
30
40
50
60
70
80
90
100
110
120
Minimum Mean 95th Maximum
HQ Profenofos
Acceptable level
RME
Maximum
High Risk
1
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0.0001
0.036
0.337
0.807
0.0912
8.008
45.9
110
0.0001
0.001
0.01
0.1
1
10
100
Minimum Mean 95th Maximum
HQ chlorpyrifos
35
Acceptable level
4. Risk Characterization
Human Health Risk Assessment
High Risk
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Oral Rfd-Chlorpyrifos = 0.003 mg/kg-day
Oral Rfd-Profenofos = 0.0001 mg/kg-day
Conclusion
36
Health Risk Assessment
Chlorpryifos is not concern
Profenofos is at risk
Profenofos, Chlorpyrifos
Non-carcinogenic pesticide
AchE inhibition effect
ADD-Chlorpyrifos = 1.07 x 10-4 mg/kg-day
ADD-Profenofos = 8.00 x 10-4 mg/kg-day
Risk Management
1. Hazard identification
2. Dose-response Assessment
3. Exposure Assessment
4. Risk Characterization
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THANK YOU
ACKNOWLEDGEMENTS
CPHS, Chulalongkorn University
Thai Fogarty ITREOH Center (ITREOH: D43 TW007849-01)
The Higher Education Research Promotion and National Research University Project of
Thailand, Office of the Higher Education Commission (AS581A)
The 90th Anniversary of the Chulalongkorn University Fund
(Ratchadaphiseksomphot Endowment Fund)
University of Health Sciences, Ministry of Health, Laos