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. 2019 May 15;8:448. Originally published 2019 Apr 11. [Version 2] doi: 10.12688/f1000research.18398.2

The association between health literacy and pesticide use behaviors among sweet corn farmers in the Pak Chong district of Thailand: a cross-sectional study

Theerachai Pobhirun 1,2, Somdej Pinitsoontorn 2,a
PMCID: PMC6743251  PMID: 31559016

Version Changes

Revised. Amendments from Version 1

Affiliations:

  • We have listed ‘Department of Community Medicine, Faculty of Medicine, Khon Kaen University, Khon Kaen, Thailand’ as an additional affiliation for Theerachai Pobhirun.

Abstract:

  • We edit the abstract to state that the present study found the response rate was 98.98 % (161 sweet corn farmers were interviewed).

Introduction:

  • We have removed mention of the top ten pesticides imported by Thailand.

Methods:

  • We added that we used ‘purposive sampling’.

  • We have removed the repeated mention of the approval of this research framework as it is already mentioned in the ‘Ethics statement’.

Results:

  • We have corrected grammatical and spelling mistakes throughout this section.

  • In the ‘Health literacy (HL) of pesticide use’ subsection, we clarify that phase 3 of pesticide use was ‘3. after pesticide application’.

Conclusions:

  • We removed the “The farmer has to find out…” statement.

Reference:

  • We deleted the ‘ChemLinked Team, 2015’ reference as we no longer list the top ten pesticides imported by Thailand in the ‘Introduction’.

Abstract

Background: Pesticide toxicity is an important health problem in Thailand due to the intensive use of hazardous pesticides.  This study aimed to determine and discuss patterns of pesticide use, health literacy, pesticide use behaviors and whether there is an association between health literacy and pesticide use behaviors among sweet corn farmers in the Pak Chong district, Thailand.

Methods: This work was carried out between May 2017-July 2017 and 161 participants were enrolled. Participant questionnaires were completed during face-to-face interviews.

Results:  This study found the response rate was 98.98%. 161 farmers were interviewed about patterns of chemical pesticide use. Two of the pesticides used in the pre-planting phase were moderately toxic: paraquat (used by 55.2% of farmers) and imidacloprid (used by 15.5% of farmers). In the pre-emergence phase, participants reported using two moderately toxic pesticides: alachlor (used by 48.8% of farmers) and chlorpyrifos (used by 2.4% of farmers). At the post-emergence phase, participants reported using six moderately toxic pesticides: chlorpyrifos (used by 60.7% of farmers), paraquat (used by 38.1% of farmers), imidacloprid (used by 7.2% of farmers), 2-4D (used by 3.6% of farmers), abamectin (used by 3.6% of farmers) and cypermethrin (used by 1.2% of farmers). Health literacy levels were moderate level (Mean score = 91.62, SD = ± 7.06) and pesticide use behaviors were low level (Mean score = 67.80, SD = ± 4.04). When examining the association between health literacy and pesticide use behaviors, we found that functional literacy was significantly associated with pesticide use behaviors. This suggests that health literacy, which includes self-management and decision-making skills, should be given greater attention as pesticide use behaviors were unsafe.

Conclusion: It may be necessary to develop approaches to reduce pesticide use and promote health literacy, thereby protecting farmers, consumers, the environment (soil, water, and air) and ecosystems from pesticide-related hazards.

Keywords: Pesticides, Health literacy, Sweet corn, Harm reduction, Farmers, Pattern, Behavior

Introduction

Agricultural production accounts for 10% of the Kingdom of Thailand’s gross domestic product (GDP) and 60% of employment. As in many developing countries, in order to achieve high yields, farmers in Thailand use pesticides and herbicides to control pests, weeds and other pathogens. Despite following stricter regulations, increasing evidence of the health risks associated with exposure to pesticides and pesticide residues contaminating food, water and air 1, 2, imports of insecticides, herbicides, and fungicides have peaked in the last decade, particularly between 2011 to 2017 3. The World Health Organization (WHO) classification of pesticides by hazard has been aligned with the GHS (The Globally Harmonized System of Classification and Labelling of Chemicals) acute toxicity hazard categories: Ia = extremely hazardous; Ib = highly hazardous; II = moderately hazardous; III = slightly hazardous; U = unlikely to present an acute hazard; O = Obsolete as pesticide (not classified) 3. Those pesticides classified as toxic include glyphosate (III), paraquat (II), 2,4-D-dimethylammonium (II), atrazine (III), ametryn (II), 2,4-D-sodium, diuron (III), propyl (O), chlorpyrifos (II), and mancozeb (U). Currently, the Thai Pesticide Alert Network (Thai-PAN) is campaigning and working with the government of Thailand to ban four pesticides (paraquat, glyphosate, chlorpyrifos, and 2,4D) due to their long-term health effects on humans. In addition, Thailand has adopted the Sufficiency Economy Philosophy as a guideline for agriculture. According to this philosophy, building immunity to environmental changes prompts individuals and their communities to be aware of the impacts their actions may have on the environment and, subsequently, their livelihoods, an awareness which leads them to live in harmony with nature 4. The environmental aspects of this guideline enable people and communities to realize the effects of pesticides on health, environment and livelihoods.

However, pesticide use trends indicate that pesticide use is increasing 5. Although pesticides are beneficial for the control of pests, there are serious concerns for humans and animals regarding associated health risks. Pesticides are chemicals which have been designed to be toxic to pests and, in many cases, their toxic nature can also be harmful to human health 1, 6, 7 and cause environmental pollution 8. There have been reports of strong associations between exposure to pesticides and cancer 9, and studies have shown that the exposure of pregnant women and breastfeeding mothers to pesticides is a risk factor for low birth weight, congenital birth defects, growth defects, learning disabilities and miscarriage 1, 10. Previous evidence suggests that farmers have awareness and a basic understanding of insecticides, pesticides and various other chemicals used in farming practices 1113 However, this awareness and knowledge alone might not lead to reduced use of the various chemicals when farming. Health literacy (HL) is a relatively new concept for social and medical sciences research. HL is the ability of individuals to understand basic health information and gain access to essential services, thereby enabling them to make informed decisions 8, 9. Health literacy can be separated into three levels 1416: (1) Functional literacy, which focuses on the ability to read, understand and access pesticide information; (2) Interactive literacy, which involves the use of cognitive skills and operates in a social environment that supports social participation in health-related issues in the community; (3) Critical literacy, which is the ability to evaluate health issues and determine the challenges of these issues.

The patterns of pesticide use were studied in three phases of sweet corn farming: pre-planting, pre-emergence and post-emergence. Sweet corn farmers use various methods when applying pesticide such as mixing, loading, spraying and washing equipment. Mixing involves weighing or measuring the pesticide in some fashion and mixing the measured concentrated product with a diluent. Loading involves pouring the diluted pesticide into the spray equipment. Spraying involves the application of the pesticide to control pests by spraying. This is the most common activity for farmers. Typical equipment used may be backpack sprayers or hand-held tank sprayers. Washing involves cleaning the equipment used for pesticide application which may be contaminated during the spraying operation. Pesticide use patterns included the number, type, toxicity and concentration of pesticides used and pesticide use behaviors. There are very few studies about pesticide use among sweet corn farmers. The aim of this research was to determine and discuss patterns of pesticide use, HL of pesticides used, pesticide use behaviors and the association between HL and the behaviors of sweet corn farmers.

Methods

This research applied a cross-sectional, quantitative design to identify determinants of health literacy and pesticide use. This study was carried out from May 2017 to July 2017. The participants were sweet corn farmers in the Pak Chong district of Nakhon Ratchasima province, Thailand. Specifically, the study was conducted in the Klangdong, Chanthuek, Wang Sai and Mu Si sub-districts of the Pak Chong district as these are the regions in which sweet corn is grown. Within these regions, 194 sweet corn farmers were identified through visits to the farms in the area (purposive sampling). However, 33 farmers were unwilling to be interviewed.

The eligibility criteria of the respondents include sweet corn farmers who live in Pak Chong district, who had used a pesticide for at least 6 months, who could read and write and who were willing to participate in the study. Written informed consent was obtained from all the participants (n = 161). Interviews were conducted by the author (T.P.) using a questionnaire, which included questions about socio-demographic factors and patterns of pesticide use, and answers from farmers were given orally. In order to assess health literacy, the three levels were further separated into 6 dimensions: cognitive skills, access, communication skills, self-management, media literacy and decision-making skills. Cognitive skills refers to the knowledge and understanding the participant has about the correct use of pesticides. Access refers to the access the participant has to pesticide effect information and health services. Communication skills refers to the ability of the participant to listen, speak, read and write about pesticide use. Self-management refers to the ability of the participant to protect their health and reduce the impact on the environment of pesticide application. Media literacy refers to the ability to compare information regarding pesticide efficacy from media such as newspapers, radio, television and pesticide advertisements. Decision-making skills refers to the ability of the participant to decide what pesticides to use and how to use them in a way that does not have a negative impact on their health or the environment.

Three experts from Thai-PAN (Thai Pesticide Alert Network) verified the content validity. The consistency index for all items was 0.61. A pilot test (sample size of 30) was used to achieve clarity for the questionnaires. Cronbach’s alpha, a measure of internal consistency, was 0.72 for the HL of pesticide use section of the questionnaire and 0.77 for the pesticide use behaviors section. Responses to questions 1–10 (cognitive skills) were marked as correct or incorrect. Responses to the remaining questions were scored qualitatively, using a 5-point Likert scale. The item responses ranged from 1 (very low) to 5 (very high). The HL of pesticide use section was composed of 36 items and it was separated into 6 parts (access, cognitive skills, communication skills, self-management, media literacy and decision-making skills). Responses to the 36 items were scored as low, moderate or high levels of health literacy for pesticide use. The maximum score for health literacy was 135. A score of <81 was considered to be low, a score of 81–108 was considered to be moderate and a score of >107 was considered to be high. A breakdown of the score thresholds for each dimension and level of health literacy can be found in Table 1. The pesticide use behaviors section was composed of 20 items, divided into 3 parts (before application, pesticide application and after application). Responses to the 20 items were scored as low, moderate and high standards of pesticide use behaviors. The maximum score for pesticide use behaviors was 100. A score of <67 was considered to be low, a score of 67–69 was considered to be moderate and a score of >69 was considered to be high. A breakdown of the score thresholds for each phase of pesticide application can be found in Table 2.

Table 1. Score thresholds for the health literacy section of the questionnaire.

HL Dimension Max Score Low Moderate High
Overall 135 <81 81-107 >107
Cognitive 10 <6 6-7 >7
Access 30 <18 18-23 >23
Communication 25 <15 15-19 >19
Self-management 25 <15 15-19 >19
Media literacy 25 <15 15-19 >19
Decision-making 20 <12 12-15 >15
Functional HL 35 <21 21-27 >27
Interactive HL 55 <33 33-43 >43
Critical HL 45 <27 27-35 >35

Table 2. Score thresholds for the pesticide use behaviors section of the questionnaire.

Application phase Max Score Low Moderate High
Overall 100 <67 67-69 >69
Before 20 <14 14-15 >15
Application 55 <33 33-34 >34
After 25 <20 20 >20

Descriptive statistics, such as frequencies, percentage, mean and standard deviation (S.D.) are used to report the socio-demographic factors, number of years using pesticides, number of annual pesticide applications, total types of pesticide used in pre-planting, pre-emergence and post-emergence phases of sweet corn farming. In addition, pesticide use behaviors such as; the type of pesticides, the level of toxicity of pesticides and the concentration of pesticides are reported using descriptive statistics. The Chi-squared test was used to test the association between HL and pesticide use behaviors using SPSS (version 20). This analysis could also be performed using a non-proprietary software such as R.

Ethics statement

During the data collection stage, we had participants provide their written consent. Personal identifiers (names, full addresses) were stripped from the dataset. This research project was approved by the Human Research Ethical Committee of Khon Kaen University (HE601107) based on the principles of the Declaration of Helsinki and the Good Clinical Practice standards of the International Council for Harmonisation of Technical Requirements for Pharmaceuticals for Human Use (ICH).

Results

The demographic characteristics of the 161 sweet corn farmers

The majority (54%) of sweet corn farmers were males and between 41–60-years-old (mean 43.14 ± 9.97 years). The average farm size for sweet corn planting was 4.67 acres (min = 1.18, max = 15.81 acres). Most of the participants have been using pesticides for between 6 and 10 years (mean 9.04 ± 4.61 years). Most (64.3%) farmers reported planting two sweet corn crops per year. The two pesticide application methods reported were spraying (reported by 88.8% of farmers) and mixing (reported by 83.2% of farmers).

Patterns of pesticide use

Patterns of pesticide use were studied over three phases of sweet corn farming. First, the soil is prepared for planting (pre-planting phase). 52.2% of farmers reported spraying paraquat to control broadleaf weeds and 16.7% of farmers reported following this with glyphosate, also to control weeds. Paraquat is a class II toxin and glyphosate is a class III toxin. According to the WHO standard and International Agency for Research on Cancer (IARC), glyphosate is likely carcinogenic to humans. For protection against insect pests, 15.5% of farmers mixed corn seeds with imidacloprid before planting, which is also a class II toxin according to the WHO. In addition, 3.6% of farmers used atrazine to control broadleaf weeds in this phase. In summary, four types of pesticides were used during the pre-planning phase, of which two were considered to be class II toxins.

During the pre-emergence phase, three pesticide types were used: alachlor spray (used by 48.8% of farmers) to control broadleaf weeds, chlorpyrifos spray (used by 2.4% of farmers) to eliminate some pests including insects and worms and atrazine (used by 38.1% of farmers) to control broadleaf weeds. Both alachlor and chlorpyrifos are toxic (class II) according to the WHO. In summary, during the pre-emergence phase, two types of pesticides were class II.

During the post-emergence phase, pesticides and herbicides are used to eliminate insect pests and weeds. Chlorpyrifos was used by 60.7% of farmers, imidacloprid by 7.2% of farmers, abamectin by 3.6% of farmers and cypermethrin by 1.2% of farmers to eliminate insect pests, all of which are class II toxins. Paraquat (used by 38.1% of farmers) and 2,4D (used by 3.6% of farmers) were used to eliminate weeds, both of which are class II toxins. Atrazine and glyphosate (both used by 2.4% of farmers) belong to toxicity class III ( Table 3). The International Agency for Research on Cancer (IARC) has defined glyphosate and 2,4D (but not atrazine) as carcinogenic.

Table 3. The percentage of farmers (n=161) using different pesticides during each of the three stages of sweet corn farming and the toxicity and carcinogenicity to humans of these pesticides.

Type
of pesticide
Common
name
Stage of sweet corn farming WHO
recommends
classification
IARC
Carcinogenic to humans
Pre
planting
Pre
emergence
Post
emergence
Herbicide Paraquat 55.2% 38.1% II Probably not carcinogenic
to humans
Glyphosate 16.7% 2.4% III Probably carcinogenic to
humans
2,4 D 3.6% II Possibly carcinogenic to
humans
Atrazine 3.6% 38.1% 2.4% III Not classified as
carcinogenic to humans
Alachlor 48.8% II Probably not carcinogenic
to humans
Pesticide Abamectin 3.6% II Probably not carcinogenic
to humans
Imidacloprid 15.5% 7.2% II Probably not carcinogenic
to humans
Chlorpyrifos 2.4% 60.7% II Probably not carcinogenic
to humans
Cypermethrin 1.2% II Probably not carcinogenic
to humans

Health literacy (HL) of pesticide use

We assessed the sweet corn farmers’ level of HL regarding pesticide use. The majority (91.30%) of the sweet corn farmers enrolled in this study had a moderate level of HL ( Table 4). We found that the cognitive score was mostly (54.66% of farmers) low, access to information was mostly (77.64% of farmers) moderate, communication skills were mostly (96.89% of farmers) low, self-management was mostly (95.65% of farmers) high, media literacy was mostly (74.53% of farmers) low and decision-making skills were moderate for 42.86% of participants and low for 41.61%. When HL was divided into the three levels, functional HL for the majority of participants (53.42%) was moderate and was classed as high for 45.34%. Interactive HL was low for 9.94% and moderate for 87.58% of participants. Critical HL was low for 53.42% and moderate for 45.34% of participants. The overall analysis of pesticide use behaviors found that 37.27 % of farmers had a low standard of pesticide use behaviors and 31.68% of farmers had a moderate standard of pesticide use behaviors. When we analyzed the three phases of pesticide use (1. before pesticide application, 2. pesticide application, 3. after pesticide application), we found that 44.10% of sweet corn farmers had a moderate standard of pesticide use behaviors at the ‘before pesticide application’ phase (mean score 14.2, ± 1.51), 42.24% had a low standard of pesticide use behaviors at the ‘application’ phase (mean score 33.16, ± 2.71) and 43.48% of farmers had a moderate standard of pesticide use behaviors at the ‘after application’ phase (mean score 19.91, ± 1.22) ( Table 5).

Table 4. The percentage Thai sweet corn farmers with low, moderate or high levels of health literacy (n=161).

Dimension Level of HL Mean
Score
S.D.
Low Moderate High
1. Cognitive skills 54.66% 34.78% 10.56% 6.46 1.28
2. Access 19.88% 77.64% 2.48% 20.38 2.29
3. Communication skills 96.89% 1.86% 1.24% 14.64 2.30
4. Self-management 0% 4.35% 95.65% 22.71 1.31
5. Media literacy 74.53% 21.74% 3.73% 14.30 2.67
6. Decision-making skills 41.61% 42.86% 15.53% 13.12 2.35
Overall HL 6.21% 91.30% 2.48% 91.62 7.06
Classification
Functional literacy 1.24% 53.42% 45.34% 26.84 2.76
Interactive literacy 9.94% 87.58% 2.48% 37.35 2.97
Critical literacy 53.42% 45.34% 1.24% 27.43 3.49

Table 5. The percentage of Thai sweet corn farmers with low, moderate or high level of pesticide use behaviors (n=161).

Pesticide use phase Standard of pesticide use
behaviors
Mean
Score
S.D.
Low Moderate High
Before application of pesticide 26.09% 44.10% 29.81% 14.72 1.51
Application pesticide 42.24% 36.02% 21.74% 33.16 2.71
After application of pesticide 32.30% 43.48% 24.22% 19.91 1.22
Overall 37.27% 31.68% 31.06% 67.80 4.04

The association between health literacy and pesticide use behaviors

The results of the data analysis showed that there was a significant statistical association between health literacy level and pesticide use behaviors (p < 0.05). Of the sweet corn farmers who had a moderate overall health literacy level, 33.33% were inclined towards a high standard of pesticide use behaviors. We found that there was an association between the self-management and decision-making skills dimensions of health literacy and pesticide use behaviors (p < 0.01). Of the sweet corn farmers who had a moderate level of self-management and a high level of decision-making skills, 85.71% and 48.00% were inclined to high standard of pesticide use behaviors, respectively. Regarding functional literacy, there was a significant statistical association with pesticide use behaviors (p < 0.01). Of the sweet corn farmers who had a moderate level of functional health literacy, 39.53% were inclined towards a high standard of pesticide use behaviors. ( Table 6).

Table 6. The association between health literacy and pesticide use behaviors (n=161).

Percentages represent the proportion of farmers with a particular level of HL who also have a particular standard of pesticide use behaviors. The p-value for association between health literacy and behavior, using the probability exact test. (*p<0.05,**p<0.01).

Health Literacy Pesticide use behaviors p-value
Low Moderate High
Cognitive skills
-   Low 36.36% 32.95% 30.68% 0.134
-   Moderate 46.43% 25% 28.57%
-   High 11.76% 47.06% 41.18%
Access
-   Low 37.50% 21.88% 40.63% 0.053
-   Moderate 35.20% 35.20% 29.60%
-   High 100.0% 0% 0%
Communication skills
-   Low 37.18% 31.41% 31.41% 0.226
-   Moderate 0% 66.67% 33.33%
-   High 100% 0% 0%
Self-management 0.006 **
-   Low 0 0 0
-   Moderate 14.29% 0% 85.71%
-   High 38.31% 33.12% 28.57%
Media literacy 0.053
-   Low 35.00% 30.00% 35.00%
-   Moderate 37.14% 42.86% 20.00%
-   High 83.33% 0% 16.67%
Decision-making skills < 0.001 **
-   Low 56.72% 28.36% 14.93%
-   Moderate 26.09% 33.33% 40.58%
-   High 16.00% 36.00% 48.00%
Overall of HL 0.020*
-   Low 80.00% 10.00% 10.00%
-   Moderate 33.33% 33.33% 33.33%
-   High 75.00% 25.00% 0%
Functional literacy < 0.008 **
-   Low 100.00% 0% 0%
-   Moderate 25.58% 34.88% 39.53%
-   High 49.32% 28.77% 21.92%
Interactive literacy 0.501
-   Low 37.50% 25.00% 37.50%
-   Moderate 36.17% 32.62% 31.21%
-   High 75.00% 25.00% 0%
Critical literacy 0.286
-   Low 44.19% 29.07% 26.74%
-   Moderate 28.77% 35.62% 35.62%
-   High 50.00% 0% 50.00%

Discussion

Findings of patterns of pesticide use, health literacy and pesticide use behaviors suggest that it is necessary to reduce the harmful effects of pesticide use. Findings included (1) the majority of sweet corn farmers did not follow the current recommended dose or number of sprays, (2) there are many pesticides used in the planting of sweet corn, (3) pesticides used in growing sweet corn have moderate toxicity and (4) the pesticide use behaviors during all phases of planting are unsafe 17. However, assessing the risk of exposure to pesticides for humans is not easy because of differences in the duration and levels of exposure to the substance 2, 6. In addition, the level of HL of the farmers was moderate. Based on these findings, pesticide use by these farmers may affect environmental health 8, 9 and lead to the pollution of soil and water (surface and groundwater) and diseases of humans 17.

Therefore, training sweet corn farmers to reduce the use of pesticides 18, 19 through an intervention program may be necessary to improve farmer safety. These findings are also consistent with previous studies 3, 20 regarding health literacy (HL) and pesticide use behaviors. When the sweet corn farmers have knowledge of the pesticide being used, they may have more appropriate pesticide use behaviors. This leads to the suggestion of developing guidelines for appropriate pesticide use for each plant, following a study of the types of pesticides used for each species.

Developing HL of the risks of pesticide use requires effective communication in order to lead to an improvement in pesticide use by sweet corn farmers, which could lead to the improvement in health in this century 21. There are a number of ways to reduce the harmful effects of pesticide use. (1) Education for farmers about how to use PPE 19, 22, 23 with a focus on apron, mask and wide-brimmed hat use because the relative absorption rate of pesticides is highest in the genital area, ear canal, forehead and scalp (11.8% 5.4% 4.2% and 3.7%) 24. Moreover, product labels should be developed that are easy to understand. (2) Promote the use of PPE while mixing, loading and applying any pesticides, especially aprons and goggles or face shields. (3) Behavior such as eating, drinking water or alcohol and smoking should not be undertaken in areas where spraying of pesticides is necessary because the body can absorb the pesticides. (4) Farmers should take a bath at the farm to avoid contaminating family or close friends 25. However, farmers cannot bathe in the immediate area where they use pesticides. There are two ways to do this: use a water jug for bathing or change clothes immediately before returning home, separating the pesticide-contaminated clothing from other clothes. (5) Sweet corn planting farmers use up to nine pesticides, seven of which belong to toxicity class II according to the WHO, including 2-4D, glyphosate and atrazine that likely cause cancer 14. Sweet corn farmers should be careful with pesticide use, should have access to information regarding pesticide toxicity and should be encouraged to switch to organic farming methods. (6) The harm reduction principle should be applied to promote a reduction in the number of pesticides used, reduce the use of especially toxic pesticides and promote the use of the recommended pesticide concentrations. This would help to protect sweet corn farmers, others indirectly exposed to the pesticides, consumers and the environment. However, promoting the use of organic farming might be rejected by farmers as some sweet corn farmers prefer to use unsuitable pesticides in order to ensure yield and quality 26.

Strengths and limitations of the study

This study was successful in collecting data with a high response rate of 82.98%. The findings of the present study can also be applied to other similar contexts. The authors suggest further qualitative study on the beliefs of farmers regarding pesticide use and organic farming as well as the study of pesticide risk reduction programs. The health literacy questionnaire was based on previously published work, pre-tested, pilot tested and edited to ensure accurate translation, coherence and relevance. However, patterns of pesticide use may be better measured using open-ended questions, where farmers are asked to provide information freely without being influenced.

Conclusions

The present study found that the health literacy of pesticide use in sweet corn farmers was at a moderate level and pesticide use behaviors were at a low level, with a tendency towards a high level of pesticide use behaviors. However, farmers had a moderate level of pesticide use behaviors at the ‘after pesticide application’ phase. This baseline study gives an insight into the range of pesticides used in the management of sweet corn pests and diseases in Thailand and found that 9 pesticides were used. The pesticides used in growing sweet corn have moderate toxicity. The major factors relating to pesticide use behaviors were the self-management and decision-making skills dimensions (p < 0.01). The lack of health literacy regarding pesticide calls for training for sweet corn farmers. To reduce the dependence on pesticides it is important to promote health literacy, especially in the cognitive skills, media skills and decision-making skills.

Data availability

Underlying data

Open Science Framework: The association between health literacy and pesticide use behaviors among sweet corn farmers in the Pak Chong district of Thailand: a cross-sectional study. https://dx.doi.org/10.17605/OSF.IO/KJ5M3 27

This project contains the following underlying data:

  • -

    Data_Theerachai.csv (demographic and questionnaire response data)

  • -

    Data Dictionary_Theerachari.csv (data dictionary for Data_Theerachai.csv)

  • -

    Correct Responses_Theerachai.csv (scoring system for questionnaire responses in Data_Theerachai.csv)

Extended data

Open Science Framework: The association between health literacy and pesticide use behaviors among sweet corn farmers in the Pak Chong district of Thailand: a cross-sectional study. https://doi.org/10.17605/OSF.IO/KJ5M3

This project contains the following extended data:

  • QN-page1 - QN-page8 (questionnaire)

Data are available under the terms of access to the dataset requires registration, and is granted to those that wish to use the data for legitimate research purposes. A guide for how to apply for dataset access is available at: https://doi.org/10.17605/OSF.IO/KJ5M3 27

Data are available under the terms of the Creative Commons Attribution 4.0 International license (CC-BY 4.0)

Acknowledgments

This research was supported by the Pakchong Nana Hospital of Public Health Ministry, Nakhon Ratchasima, Thailand. The authors wish to thank all of the sweet corn farmers that participated in this study.

Funding Statement

The author(s) declared that no grants were involved in supporting this work.

[version 2; peer review: 2 approved]

References

  • 1. Tano ZJ: Ecological Effects of Pesticides. Pesticides in the modern world risks and benefits Salaam, Tanzania,2011. 10.5772/20556 [DOI] [Google Scholar]
  • 2. Damalas CA, Eleftherohorinos IG: Pesticide exposure, safety issues, and risk assessment indicators. Int J Environ Res Public Health. 2011;8(5):1402–1419. 10.3390/ijerph8051402 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 3. Tawatsin A, Thavara U, Siriyasatien P: Pesticides used in Thailand and toxic effects to human health. Med Res Arch. 2015;3:1–10. 10.18103/mra.v0i3.176 [DOI] [Google Scholar]
  • 4. Ministry of Foreign Affairs: Sufficiency Economy Philosophy: Thailand’s Path towards Sustainable Development Goals. Thailand,2017. Reference Source [Google Scholar]
  • 5. World Health Organization: The WHO recommended classification of pesticides by hazard and guidelines to classification. Stuttgart, Germany,2009. Reference Source [Google Scholar]
  • 6. Chan I, Devi NL: Pesticides Classification and its Impact on Human and Environment. Environ Sci Eng. 2017;6:140–158. Reference Source [Google Scholar]
  • 7. World Health Organization: Public Health effect impact of pesticide used in agriculture. England,2019. [Google Scholar]
  • 8. Tirado R, Englande AJ, Promakasikorn L, et al. : Use of agrochemicals in Thailand and its consequences for the environment. Greenpeace Research Laboratories Technical. Bangkok, Thailand,2008. Reference Source [Google Scholar]
  • 9. Alewu B, Nosiri C: Pesticides and Human Health. Pesticides in the Modern World-Effects of Pesticides Exposure University Campus STeP Ri Slavka Krautzeka, Rijeka, Croatia,2011. Reference Source [Google Scholar]
  • 10. de Araujol JS, Delgadol IF, Paumgartten FJ: Glyphosate and adverse pregnancy outcomes, a systematic review of observational studies. BMC Public Health. 2016;16:472. 10.1186/s12889-016-3153-3 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 11. Sorat W: The Relationship Between Health Beliefs, Pesticide Use and Safety Behaviors with Acute Poisoning Symptoms of Farmers in Chaiyaphum Province [thesis]. Bangkok: Mahidol University;2004. Reference Source [Google Scholar]
  • 12. Suklim N, Raksanam B, Songthap A: Risk behaviors related agrochemical use among rubber farmers in Southern of Thailand (2014). European Journal of Research on Education. 2014;2(2):109–115. 10.15527/ejre.201426254 [DOI] [Google Scholar]
  • 13. Ratzan SC: Health literacy: communication for the public good. Health Promot Int. 2001;16(2):207–214. 10.1093/heapro/16.2.207 [DOI] [PubMed] [Google Scholar]
  • 14. Hepburn M: Health literacy, conceptual analysis for disease prevention. Int J Collab Res Intern Med Public Health. 2012;4(3):227–238. Reference Source [Google Scholar]
  • 15. Baker DW: The meaning and the measure of health literacy. J Gen Intern Med. 2006;21(8):878–883. 10.1111/j.1525-1497.2006.00540.x [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 16. Nutbeam D: Health literacy as a public health goal: a challenge for contemporary health education and communication strategies into the 21st century. Health Promot Int. 2000;15(3):259–267. 10.1093/heapro/15.3.259 [DOI] [Google Scholar]
  • 17. Nutbeam D: Defining, measuring and improving health literacy. HEP. 2015;42(4):450–455. 10.7143/jhep.42.450 [DOI] [Google Scholar]
  • 18. Abbassy MM: Farmer’s Knowledge, Attitudes and Practices, and their Exposure to Pesticide Residues after Application on the Vegetable and Fruit Crops. Case Study: North of Delta, Egypt. J Environ Anal Toxicol. 2017;7(5):1–6. 10.4172/2161-0525.1000510 [DOI] [Google Scholar]
  • 19. Panuwet P, Siripong W, Prapamontol T, et al. : Agricultural Pesticide Management in Thailand: Situation and Population Health Risk. Environ Sci Policy. 2012;17:72–81. 10.1016/j.envsci.2011.12.005 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 20. Okonya JS, Kroschel J: A Cross-Sectional Study of Pesticide Use and Knowledge of Smallholder Potato Farmers in Uganda. Biomed Res Int. 2015;2015:759049. 10.1155/2015/759049 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 21. Rivera EP, Siriwong W, Taneepanichskul N, et al. : Health risk related to pesticide exposure in the agriculture system in Thailand: A systematic review. J Health Res. 2016;30(Suppl 1):S71–S80. 10.14456/jhr.2016.69 [DOI] [Google Scholar]
  • 22. Nutbeam D: The evolving concept of health literacy. Soc Sci Med. 2008;67(12):2072–2078. 10.1016/j.socscimed.2008.09.050 [DOI] [PubMed] [Google Scholar]
  • 23. Rijal JP, Regmi R, Ghimire R, et al. : Farmers’ knowledge of pesticide safety and pest management practices: A case study of vegetable growers in Chitwan, Nepal. Agriculture. 2018;8(1):16 10.3390/agriculture8010016 [DOI] [Google Scholar]
  • 24. Ogg CL, Hygnstrom JR, Albert CA, et al. : Managing Pesticide Poisoning Risk and Understanding the Signs and Symptoms. NEBRASKA EXTENSION.2006;1–15. Reference Source [Google Scholar]
  • 25. Lorenz AN, Prapamonto T, Narksen W, et al. : Pilot study of pesticide knowledge, attitudes, and practices among pregnant women in Northern Thailand. Int J Environ Res Public Health. 2012;9(9):3365–3383. 10.3390/ijerph9093365 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 26. Raksanam B, Taneepanichskul S, Siriwong W, et al. : Factors associated with pesticide risk behaviors among rice farmers in the rural community, Thailand. J Environ Earth Sci. 2012;2(2):32–39. 10.7282/T30Z71NB [DOI] [Google Scholar]
  • 27. Pobhirun T: The association between health literacy and pesticide use behaviors among sweet corn farmers in the Pak Chong district of Thailand: a cross-sectional study.2019. 10.17605/OSF.IO/KJ5M3 [DOI] [PMC free article] [PubMed] [Google Scholar]
F1000Res. 2019 Sep 11. doi: 10.5256/f1000research.20773.r52608

Reviewer response for version 2

Archin Songthap 1

Page 1: Abstract:

  1. In methods, the authors should add the study design, sampling technique and statistics used.

  2. Objectives should be: to determine patterns of pesticide use, health literacy, pesticide use behaviors, and the association between health literacy and pesticide use behaviors among sweet corn farmers in Pak Chong District, Thailand.

  3. The conclusion from the findings on HL should promote focusing on the significant factors to HL including cognitive skills.

Page 3: Introduction:

  1. In paragraph 2, please show the statistics of the increasing pesticide use among Thai farmers to see the trend.

  2. As the authors mentioned about the effect of pesticide use to human health, please give an example of the screening results of the toxins prevalence in Thai farmer blood stream from a survey.

Page 4: Methods: Statistics:

  1. Levels of health literacy can be explained by descriptive statistics.

  2. If the authors use the chi-square test, please check the assumption since there are some expected values, less than 5, greater than 20% of the cells in self efficacy management and functional literacy. The authors should use Fisher exact text or Pearson chi –square test instead for these two factors.

Page 7-8: Results:

  1. Please check percentage in each variables in Table 4. For example, communicable skill, the total of percentage in low, moderate, and high levels must be 100.0% in total, not 99.9 or 100.1%.

  2. The results in Table 7, zero numbers in low level of self-management should be deleted for presentation or analysis if possible.   

I confirm that I have read this submission and believe that I have an appropriate level of expertise to confirm that it is of an acceptable scientific standard.

F1000Res. 2019 May 29. doi: 10.5256/f1000research.20773.r48535

Reviewer response for version 2

Kishor Atreya 1

The authors have revised the manuscript given the initial comments. No theoretical relationship is sought for the health literacy and pesticide use behavior as suggested earlier, however. The revised version has a few minor corrections before indexing.

Page 3 introduction section:

  • Delete “The World health Organization……………..mancozeb (U)”.

Page 4 last paragraph:

  • Delete “This analysis…….as R”. 

Page 5, last para:

  • Change “pesticides” to “insecticides” and “are” to “were”.

A number of reference citation are required. Please cite reference to the following statement/tables:

  • Page 5 - “According to the WHO standard and International Agency for Research on Cancer (IARC), glyphosate is likely carcinogenic to humans.”

  • Table 3, Column: “Who recommends classification”.

  • Table 3, Column: "IARC Carcinogenic to humans”.

  • Most of the percentage figures are given in 2 digits after the decimal. 1 digit is suggested.

Page 8, 2 column, 1 para:

  • Delete “however, promoting the use of organic farming……yield and quality” – this is contradiction to your earlier recommendation.

Conclusions Section:

  • Delete p values. 

I confirm that I have read this submission and believe that I have an appropriate level of expertise to confirm that it is of an acceptable scientific standard.

F1000Res. 2019 Apr 30. doi: 10.5256/f1000research.20131.r47851

Reviewer response for version 1

Kishor Atreya 1

Page 1, Abstract:

  • “89.98%” - 90%. What about the remaining participant? In the method section, the total participant mentioned was 161, and in results section it is said 90%. Confusion!

  • “Functional literacy” - What is functional literacy? Briefly define the working definition of health literacy and pesticide use behavior in the abstract.

Page 3, Introduction:

  • “The top ten pesticides imported by Thailand…” - This is not required.

Page 3, Methods:

  • “194 sweet corn farmers were identified” - What was the sampling method? Random and purposeful? Any sample size calculations done? What was the population of the sweet corn farmer?

  • “The research framework was approved…” - It is better suited in the text later - under the heading “ethical statement”.

  • “who could read and write” - This study intentionally excluded illiterate sweet corn farmers? Why? These farmers might be at higher risk of exposure?

  • “6 dimensions” - Any reference?

Page 4, Methods:

  • “36 items” - What are those 36 items? Please provide in the appendix.

  • “low, moderate or high levels” - It is not clear that whether the authors demarcated these levels or derived from literature.

  • “low, moderate and high standards of pesticide use behaviors” - Please provide 20 items in the appendix.

  • “A score of <67 was considered to be low, a score of 67–69 was considered to be moderate and a score of >69 was considered to be high.” - Any literature published on these 3 categories? If so, please cite.

  • “This analysis could also be performed using a non-proprietary software such as R.” - This is not required.

Page 4, Results, The demographic characteristics of the 161 sweet corn farmers:

  • “male” – Males.

  • “had been” – Have been.

  • “mixing” - What is the mixing method?

Page 5, Results, Patterns of pesticide use:

  • “four pesticide types” – Four types of pesticides.

  • “pesticides” – Insecticides.

  • “are” - Were

Page 5, Results, Health literacy (HL) of pesticide use:

  • “2. pesticide application, 3. pesticide application” – What is the difference between 2 and 3?

Page 6, Discussion:

  • “did not follow the current recommended dose or number of sprays” – I did not see any data on it in the result section.

  • Ref 18 - This reference may be wrong here.

  • Discussion is poor. Most of the discussion was done on the “consequences” of pesticide use, not on the results. The paper finds significant association between cognitive literacy and pesticide use behaviors, but not explained it in details. I would suggest having the results explained in the discussion section with some theory and recent literature.

Page 7, Table 6:

  • I see a number of zero values in the cells. How did authors consider these values in the Chi-square test?

Page 8, Conclusions:

  • “the self-management and decision-making skills dimensions (p < 0.01)” - This relationship should be explained in the discussion section.

  • “The farmer has to find out…” - This is not required.

I confirm that I have read this submission and believe that I have an appropriate level of expertise to confirm that it is of an acceptable scientific standard, however I have significant reservations, as outlined above.

Associated Data

    This section collects any data citations, data availability statements, or supplementary materials included in this article.

    Data Availability Statement

    Underlying data

    Open Science Framework: The association between health literacy and pesticide use behaviors among sweet corn farmers in the Pak Chong district of Thailand: a cross-sectional study. https://dx.doi.org/10.17605/OSF.IO/KJ5M3 27

    This project contains the following underlying data:

    • -

      Data_Theerachai.csv (demographic and questionnaire response data)

    • -

      Data Dictionary_Theerachari.csv (data dictionary for Data_Theerachai.csv)

    • -

      Correct Responses_Theerachai.csv (scoring system for questionnaire responses in Data_Theerachai.csv)

    Extended data

    Open Science Framework: The association between health literacy and pesticide use behaviors among sweet corn farmers in the Pak Chong district of Thailand: a cross-sectional study. https://doi.org/10.17605/OSF.IO/KJ5M3

    This project contains the following extended data:

    • QN-page1 - QN-page8 (questionnaire)

    Data are available under the terms of access to the dataset requires registration, and is granted to those that wish to use the data for legitimate research purposes. A guide for how to apply for dataset access is available at: https://doi.org/10.17605/OSF.IO/KJ5M3 27

    Data are available under the terms of the Creative Commons Attribution 4.0 International license (CC-BY 4.0)


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