What are the non-food impacts of GM crop cultivation on farmers’ health?
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Although approved for commercialisation in a number of countries since the 1990s, the potential environmental, human/animal health, and socio-economic impacts of genetically modified (GM) crops are still widely debated. One category of human health impacts (designated in this review as non-food health impacts) focuses on indirect effects of GM crop cultivation; amongst which the most prominent are health benefits via: (1) reduced use of pesticides, and (2) an increase in income. Both of these pathways have raised a lot of interest in the developing world, especially in areas experiencing high rates of pesticide poisonings and low agricultural incomes. However, evidence to support such benefits has been relatively scarce in comparison to that of GM food health impacts. Non-food health impacts of GM crop cultivation on farmers deserve more attention, not just because of an apparent knowledge gap, but also because of, potential economic and environmental implications, involving for example CO2 emissions, underground water contamination and improved sanitation.
The primary research question was: What are the non-food impacts of GM crop cultivation on farmers’ health? To address this primary question, the study focused on two related secondary questions: (1) Does the cultivation of GM crops result in a lower number of pesticide-related poisonings as compared to the cultivation of their non-GM counterparts?, and; (2) Does the cultivation of GM crops allow for higher financial resources to be used by farmers to improve the health status of themselves and their family, as compared to the cultivation of the non-GM counterpart? The extent to which information relevant to the two secondary questions was freely-available was also evaluated. The search and assessment methodologies were adapted following experience gained during a scoping exercise, and followed the published protocol.
The 20 databases and 10 reviews searched returned 4,870 hits, with 19 identified as relevant for data extraction. It was apparent that the 19 articles were derived from only 9 original studies, of which 7 were relevant to the first research question, whilst the remaining 2 were relevant to the second question. The studies showed both an overall decrease in the amount of pesticides applied and an increase in household income from GM crop cultivation as compared to the cultivation of the non-GM counterpart.
In the absence of additional confounding variables or statistical analyses to support these findings, any correlation from these studies should be considered circumstantial at best. Even though the cultivation of GM crops appears to increase household income, evidence to demonstrate that farmers invested this extra income in improving their health remained inconclusive. Further research is therefore needed to clarify the possible correlation between GM crop cultivation and (1) pesticide poisonings, and (2) overall health improvements. Future impact evaluations should include: both written records and surveys; statistical correlations between independent and dependent variables; testing the characteristics of the samples for statistical significance to indicate their representativeness of a particular population, and; increasing the importance of confounding variables in research design (by identifying specific variables and selecting sample and control groups accordingly).
KeywordsGM crops Farmers Pesticides Poisonings Incomes Health expenditures
International Centre for Genetic Engineering and Biotechnology
Genetically modified organism
International Service for the Acquisition of Agri-biotech Applications
The first GM crop approved for commercialisation was a delayed-ripening tomato in 1994 in the USA. By 2014 there were 28 countries growing GM crops on a cumulative area of 181 million hectares, making GM crops the technology with the fastest rate of uptake in modern agriculture . However, many contradictory reports have been published concerning the impacts of GM crop cultivation. Whilst some have pointed towards an array of socio-economic and environmental advantages, others have indicated that GM crop cultivation comes with adverse consequences. For example, in addition to an increase in farm income , the cultivation of GM crops has been reported to reduce the environmental impact of agriculture through: lowering the amount of pesticides applied ; decreasing the amount of fossil fuel consumed and CO2 emitted due to a reduction or avoidance of ploughing , and; facilitating conservation tillage, resulting in better maintenance of agricultural soils [5, 6]. Conversely, other reports have indicated that the cultivation of GM crops resulted in: an increase in the use of pesticides ; failures to provide significantly increased yields , and; an increase in allergenic and toxic effects .
Within the vast array of impacts ascribed to GM crop cultivation, those pertaining to human health may not be as easily analysed. Effects on human health can be considered separately or included in economic or environmental evaluations . Exposure pathways determine how health effects are considered, either (1) directly, due to the consumption of GM food , or direct contact with the plant during harvest, or (2) indirectly, depending on the influence of GM crop cultivation on on-farm pesticide use , or impacts on overall welfare related to changes in on-farm incomes. Where health effects have been included in economic evaluations, both pecuniary and non-pecuniary effects have been described . In other instances, impacts on human health have been considered under broader environmental impacts, within indicators such as Environmental Impact Quotients (EIQs) .
The choice of research objectives for the present systematic review has been guided by the links between agricultural productivity and health. Such links include health impacts derived from changes in household income and from impacts on agricultural production chains generated by the introduction of new crops . Any modification of household income can affect patterns of spending within the household, including the money available for buying more and/or better food, paying for medical expenses, and saving . The introduction of a new crop can bring changes to: (1) consumption patterns of other agricultural commodities; (2) agricultural practices e.g. time assigned to on-farm work can interfere with other activities, or an intensification of agriculture practices with heavy use of pesticides and fertilisers which in turn can increase the number of accidents and toxicity from pesticides, and; (3) markets (availability of better/worse products than before) .
In addition, in addressing the human health impacts of GM crops, the focus is usually on effects resulting from the consumption of GMOs and their derived agricultural products. Non-food effects on human health are generally overlooked or ignored. In the few instances when they are addressed, the non-food impacts are not tackled in a separate category but rather variables pertaining to such impacts are included selectively in other categories of GMO impacts, such as those pertaining to the environment (CO2 emissions, underground water contamination) or economics (improved sanitation). Further, due to the controversies surrounding GM crops, the objectivity of articles analysing the impacts of GM crop cultivation are often questioned. Amongst the latter category are reports that infer human health benefits from a reduction in pesticide use without performing any analyses to support the position . For these reasons, a systematic review was chosen as the most appropriate methodology to guide the evaluation of the existing evidence of GM crop non-food effects on human health and/or to point to a gap(s) in existing knowledge.
This systematic review considered the impacts of GM crop cultivation arising from changes in on-farm pesticide usage and household income, and the resulting effects on health. As the primary beneficiaries of GM crop technology to date, farmers were the population selected for this study. “Farmers” were considered to include farm owners, farm labourers and agricultural contractors in developing and developed countries. As the focus of the systematic review concerned non-food impacts on GM crop cultivators rather than more general indirect impacts, this review did not investigate the possible contribution of GM crop cultivation to the lowering of greenhouse gas emissions, sometimes considered as an indirect health effect , nor did it explore other indirect effects such as the contamination of underground water or impacts on sanitation.
The primary research question was: What are the non-food impacts of GM crop cultivation on farmers’ health? To specifically address the primary research question, the study focused on two related secondary questions: (1) Does the cultivation of GM crops result in a lower amount of pesticide usage compared to the cultivation of non-GM crops, hence leading to a reduction in pesticide-related poisonings?, and (2) Does the cultivation of GM crops allow for greater financial resources to be used by farmers to improve the health of themselves and their family, compared to farmers cultivating non-GM crops? Both secondary questions looked at final outcomes (number of pesticide-related poisonings and health-related expenditures) through a well-established pathway, via intermediary outcomes (amount of pesticide usage and income derived from GM crop cultivation). The main concepts addressed in this systematic review (“PICO”; P—Population, I—Intervention, C—Comparator, O—Outcome) [14, 15, 16, 17] were formulated as shown in Table 1 of the published protocol .
The review also evaluated the extent to which information relevant to the two secondary questions was freely-available (understood to be data that could be accessed without expense, i.e. publicly-accessible materials from the Internet, databases routinely available to universities and public research institutions on a no-cost basis, as well as articles provided freely by the authors when contacted).
The following combination of keywords and wildcard symbols (*, $), linked with Boolean operators ‘AND’ and ‘OR’ were used to search online databases: (farmer* OR agric* OR worker OR contractor) AND ([genetic*modif*] OR [genetic*engineer*] OR GE OR transgene* OR herbicide$tolerant OR insect$resistant OR biotech* OR BT OR GM OR stacked$trait*) AND (crop* OR plant* OR flower*) AND (health OR poisoning OR security OR safety OR welfare OR benefit) AND (pesticides OR insecticides OR herbicides OR fungicides OR bactericides OR income OR revenue OR gains OR wage OR profit OR earnings OR livelihood).
The composition of the search string was established following the experiences gained during a scoping exercise preceding the publishing of the protocol. At the time, a short combination of key words was employed to search in four databases. Afterwards the search string was improved with more synonyms (almost doubled the length of the search string), which increased the number of hits. The search string was established to reach a balance between comprehensiveness (reaching as many relevant hits as possible) and manageability (databases cannot handle searches with too many key words).
A special attention was given to the hits in Spanish or Portuguese. Since we employed databases that had abstracts in English for articles published in English, Spanish and Portuguese, we could use a search with English key words, yet retrieve articles in all three languages. The number of articles in English far exceeded the articles in Spanish or Portuguese. Combined with the fact that the language competencies of most of the members of the review team did not include Spanish or Portuguese, it was established that the search would focus only on articles in English.
The structure of the search string followed a PICO structure, albeit in a slightly modified form. The Intervention was represented by the GM crop cultivation. However, to ensure that the search terms referring to the Intervention were as inclusive as possible but yet captured only GM crops (and not GM insects or animals), “GM” and “crop” were separated into different categories. No string of key words was dedicated to the Comparator, as it was already included in the Intervention section: (crop* OR plant* OR flower*).
The Outcomes category was further separated into intermediary (pesticides OR insecticides OR herbicides OR fungicides OR bactericides OR income OR revenue OR gains OR wage OR profit OR earnings OR livelihood) and final outcomes (health OR poisoning OR effects OR welfare OR environment).
List of databases and collections searched
Database of Promoting Health Effectiveness Reviews (DoPHER)
Latin America and the Caribbean (LILACS)
Medical Literature Analysis and Retrieval System Online (MEDLINE)
PubMed Central (PMC)
Web of Knowledge
Agricultural Biotechnology Network in Africa (ABNETA)
African Centre for Biosafety (ACBIO)
Database of the Safety and Benefits of Biotechnology—CropLife International
International Food Policy Research Institute (IFPRI)
International Service for the Acquisition of Agri-biotech Applications (ISAAA)
ProQuest (Dissertations & Theses, Dissertations & Theses (PQDT) A&I, Sociology, Sociological Abstracts)
The databases were divided amongst three reviewers, with two reviewers searching each database. The databases were searched within ‘title’, ‘topics’ and ‘full text’ categories. As some databases did not accept the full search string, the reviewers were at liberty to adapt the search string to contain combinations of fewer words (for example, one term from each group within brackets united by an ‘AND’ operator). As this was database-specific, the short search strings were not specified a priori.
In cases where web searches and databases displayed large numbers of results in the order of relevance (e.g. Google Scholar), only the first 100 were evaluated. For databases that returned results of equal relevance (e.g. Web of Knowledge) and retrieved a high number of hits (in the order of thousands), a title screening was performed prior to an abstract screening.
Study inclusion criteria
The following criteria were applied to each article to determine its possible suitability for further inclusion.
Language English (the language in which the reviewers were most proficient and also the language in which the majority of articles retrieved during the scoping exercise were written).
Timeline Published after 1994—the year when the first GM crop was commercially cultivated (on-going research was not included).
Population Farmers (understood to be farm owners, farm labourers and agricultural contractors) in developing and developed countries.
Intervention GM cultivation: any type of GM trait and any type of host crop.
Comparator Non-GM crop cultivation (both conventional and organic).
Outcomes Intermediary outcomes (amount of pesticide usage and income derived from GM crop cultivation) and final outcomes (number of pesticide-related poisonings and health-related expenditures).
The primary hits retrieved were screened by each reviewer at the level of title and abstract, according to the Inclusion criteria. Each reviewer made a note of the exact search string(s) used for each database, along with the number of hits retrieved and the list of selected potentially relevant articles. The information was collected by a search coordinator. Those articles that the reviewers remained uncertain of their relevance to the Inclusion criteria were retained and included in the next step of the review process. To reduce reviewer bias, all articles deemed relevant by an individual reviewer were included in the subsequent full-text analysis.
Following the search and screening of the databases, a list was made (Additional file 1: Table S1) of articles that had been found to correspond to the Inclusion criteria. Next, the full text of every article in this list was sought, either directly from the database in which they were identified or provided by the authors upon request. Specific articles were moved to a separated list (Additional file 2: Table S2) if the full text was not immediately freely-available, even after attempts to contact the corresponding author. In some cases, the full texts became available at a later date in the review process. These full texts were evaluated for suitability but none was found to be relevant. Such articles were therefore not included in the list of full articles to be analysed, nor did they take part in the Kappa Cohen test calculations.
To verify the consistency of selection between reviewers at the level of title and abstract screening a Cohen Kappa test is usually recommended and the protocol of this systematic review included one at this step. The threshold previously set was 0.6. However, a classical Cohen Kappa test could not be performed at this step due to the combination of the search and screening done independently by each reviewer. However, to avoid losing potentially relevant articles, all articles selected during individual screening were included in the full text analysis step.
To test the reviewers’ screening consistency at the level of title and abstract, a Cohen Kappa test was undertaken as a separate exercise: all three reviewers ran a full-string search within Science Direct and exported the first 100 hits that were then analysed using the inclusion criteria. The 100 hits were divided between the reviewers to evaluate for potential inclusion: reviewer 1—all hits; reviewer 2—the first 50 hits; reviewer 3—the second 50 hits. A Cohen Kappa test was then undertaken to determine the degree of agreement between reviewers 1 and 2, and between reviewers 1 and 3, respectively. The results indicated weak agreements between reviewers 1 and 2 (0. 498) and reviewers 1 and 3 (0.36). As both results were lower than the 0.6 threshold established in the protocol, a discussion ensued between all reviewers to clarify how to consistently apply the inclusion criteria. The reason for the initial poor results of the Cohen Kappa was determined as being the tendency of one reviewer to include articles when the title and abstract could not supply sufficient information, whilst the other two reviewers tended to reject them. As this did not affect the inclusion criteria, they did not require a re-evaluation. However, all reviewers then agreed that it was necessary to retain those articles for which the title and abstract did not supply sufficient information to confidently assess their relevance to the inclusion criteria.
All full-text articles were divided amongst the reviewers for a full-text analysis using the inclusion criteria, with each article evaluated by two reviewers. At the end of the full-text analysis, the Cohen Kappa test was repeated; the results (0.615 and 0.612) demonstrated an acceptable degree of agreement between the reviewers.
Potential effect modifiers and reasons for heterogeneity
- 1.Type of intervention (GM crops):
Number of crops analysed
Type of crop
Type of trait introduced
Type of pesticide(s) applied
Agro-ecological climate (average temperatures, precipitation, etc.)
Weather (during the study cultivation)
- 3.Farm and farmer profiles:
Areas cultivated with GM/non-GM crops
Use of pesticide protective measures (if relevant)
- 4.Institutional context:
Price control policies
Agricultural extension services
- 5.Study design:
Frequency and period of data collection
Data extraction from all studies was done by one reviewer, and then subsequently reviewed and validated by a second reviewer (see Additional file 3: Appendix 1). For each study, the variables included the main findings for the intermediary and final variables, as well as the potential effect modifiers and reasons for heterogeneity listed above.
Data quality assessment
Huang et al. (2005)
Huang et al. (2002)
Kouser and Qaim (2011)
Kouser and Qaim (2013)
Morse and Bennett (2008)
Dev and Rao (2007)
Bennett et al. (2006)
Wang et al. (2008)
QA: Did the study include more than one study area (country/region within a country)?
QA: Were the farmers randomly selected?
QA: Did the study include data from more than 1 year?
QA: Did the sources of data rely on written records?
QA: Were there any measures in place to deal with attrition?
QA: Did the study test differences between GM adopters and non-GM adopters?
QA: Did the study test if the farmers’ use of pesticides protective measures was related to the pesticides-related poisonings?
QA: Did the study include confounding variables in the calculation of farmers’ income?
Results for 1st research question
ID of the form
Huang et al. (2005)
Huang et al. (2002)
Kouser and Qaim (2011)
Kouser and Qaim (2013)
Dev and Rao (2007)
Bennett et al. (2006)
Bibliographic reference (main article)
J Huang, R Hu, S Rozelle, C Pray (2005). Insect-resistant GM rice in farmers’ fields: Assessing productivity and health effects in China. Science 308(5722): 688–690
J Huang, R Hu, C Fan, CE Pray, S Rozelle (2002). Bt cotton benefits, costs, and impacts in China. AgBioForum 5(4): 153–166
S Kouser, M Qaim (2011). Impact of Bt cotton on pesticide poisoning in smallholder agriculture: A panel data analysis. Ecological Economics 70(11): 2105–2113
S Kouser, M Qaim (2013). Valuing financial, health, and environmental benefits of Bt cotton in Pakistan. Agricultural Economics 44(3): 323–335
MS Dev, NC Rao (2007). Socio-economic impact of Bt cotton. Monograph No. 3. Hyderabad: Centre for Economic and Social Studies (CESS)
R Bennett, S Morse, Y Ismael (2006). The economic impact of genetically modified cotton on South African smallholders: Yield, profit and health effects. The Journal of Development Studies 42(4): 662–677
EM Liu (2008). Essays on development economics in China. PhD thesis, Princeton University, New Jersey, USA
China/Hubei province and Fujian province; preproduction trials
China/In 1999—Hebei and Shandong. In 2000, Henan. In 2001, Anhui and Jiangsu provinces were added
India/ Maharashtra, Karnataka, Andhra Pradesh, and Tamil Nadu in central and Southern India
Pakistan/ Punjab Province, the leading cotton production province
India/ Districts of Warangal, Nalgonda, Guntur and Kurnool in Andhra Pradesh are selected to represent the four agro-climatic zones
South Africa/ Makhathini Flats
China/ Henan, Shandong, Hebei and Anhui provinces
Survey, 2 years, counties involved in pre-production trials; farmers selected sometimes randomly sometimes not (some villages had a low number of adopters so all were selected); the survey allegedly has no drop-outs but only 69 households were interviewed in both years (77 households in the first year and 101 in the second); regression analysis to establish the effect of confounding variables
Survey, 3 years; counties selected based on the cultivation of Bt cotton, villages and farmers selected randomly; some farmers were later dropped from survey (non-GM adopters become GM adopters); econometric model to verify the survey results
Panel survey, 4 years; 4 states chosen, randomly choosing districts, villages, and households; attrition occurred, yet sample balanced, then checked if any bias was incurred; fixed-effects Poison regression model for pesticide poisoning incidence and fixed-effects linear regression model for pesticide use
Survey, 1 year; districts chosen, but tehsils, villages and farmers randomly selected
Survey, 1 year; districts, counties, villages and farmers selected randomly based on the area cultivated with cotton/Bt cotton, samples selected to be representative of the population;
Archival data (time series records) for 3 years and in-depth interviews. An element of triangulation between primary and secondary data sources. The primary data came from Vunisa records held over 3 years which the company itself had not analysed for farm-level trends.
The primary data came from an in-depth survey of 32 farmers (selected randomly from a farmer organisation) combined with field measurement and observation
Survey, 1 year; Four provinces (Henan, Shandong, Hebei, and Anhui) that have the same cotton growing season (April to October) and have high Bt cotton adoption rates were selected; randomly selected two counties per province and two villages per county. In each village, twenty households were selected randomly and surveyed
Sprayings: 0.5 vs. 3.7 (GM vs. non-GM); amount of pesticides (kg/season/ha) GM farmers: 2.0 kg/ non-adopters 21.2 kg
Sprayings: 6.6 vs. 19.8 (Partial information, only for 1999, provided in Huang 2002, Science). As Bt cotton reduced pesticide use by 35.7 kg per hectare, or a reduction of 55% of pesticide use in the entire sample between 1999 and 2001. High variation between provinces
Sprayings: 1.52 vs. 2.22 (GM vs. non-GM); In all four seasons, lower quantities of pesticides were used on Bt than on non-Bt plots. Bt crop-using farmers reduce pesticides mostly in the most toxic hazard category I pesticides (1.1 kg per acre is equivalent to a 70% reduction)
Sprayings: 6 vs. 7 (GM vs. non-GM). Farmers use significantly lower pesticide quantities on Bt than on non-Bt plots. Still the reduction is less than in India or China
Sprayings: 9 vs. 12 (GM vs. non-GM). Decreased by 18%; spraying pesticides either as a precautionary measure or on noticing pest without any regard to the economic threshold levels of the pest
With the Bt variety farmers reduced the sprayings by 3 on average. Adopters also used less insecticide (bollworm and non-bollworm) especially in seasons 1 and 3, than non-adopters. Pesticide use was reported to costs not amounts
All else equal, the average Bt cotton farmer reduced the use of pesticides by 19.5 kg/ha, or 73.3 percent, on his Bt plot compared with his non-Bt plot
0 for full adopters; both insect-resistant GM and non-GM plots, 7.7% (2002) and 10.9% (2003) reported health problems. Only non-GM varieties: 8.3% (2002) and 3% (2003) had health problems
5% (1999), 7% (2000), and 8% (2001) for full adopters. 11% (1999), 19% (2000) and 10% (2001) for both types of plots. 22% (1999), 29% (2000) and 12% (2001) for non-adopters
On average, only 0.19 poisoning cases per cotton season were reported by Bt farmers, as compared to 1.60 cases by non-Bt farmers
1.42 (Bt) vs 1.96 (non-Bt) average number of poisonings
25% (Bt cotton) vs 27% (non-Bt) number of poisonings
When the number of adoptions of Bt cotton increases, the number of poisonings decrease (logarithm of the number of hospital admissions due to pesticide poisoning, as a function of adoption of Bt cotton). The previous article on the same study (2003) shows that in the first year of adoption (0.1% Bt cotton adoption) there were 20 poisonings registered for the peak month of February. Four seasons later, at 60% adoption rate for Bt cotton, in February, there were 4 cases of poisonings
30% (129) of farmers reported that they experienced at least one symptom since 1996, but it is not reported to the cultivation of Bt cotton
Main sources of bias
1. farmer recall was used, although farmers were interviewed about recent data (same season); 2. personal protective measures for pesticide applications as confounding variables were not analysed to connect GM cultivation and health effects; 3. attrition was not dealt with, although it obviously occurred (out of 77 households in the first year, only 69 remained in the second)
1. farmer recall was used, although farmers were interviewed about recent data (same season); 2. personal protective measures for pesticide applications as confounding variables were not analysed to connect GM cultivation and health effects; 3. differences between GM and non-GM farmers were not analysed
1. farmer recall was used, although farmers were interviewed about recent data (same season); 2. personal protective measures for pesticide applications as confounding variables were not analysed to connect GM cultivation and health effects; 3. differences between GM and non-GM farmers were not analysed
1. farmer recall was used, although farmers were interviewed about recent data (same season); 2. only one year survey; 3. personal protective measures for pesticide applications as confounding variables were not analysed to connect GM cultivation and health effects (it was stated as a general observation that farmers do not use protective measures, but the farmers interviewed were not asked about such measures)
1. farmer recall was used but at least 2 years after the cultivation (the limits of the farmers recollection is stated as one of the limits of the study); 2. only 1 year survey; 3. personal protective measures for pesticide applications as confounding variables were not analysed to connect GM cultivation and health effects
1. only one area studied. 2. the written records which form the majority of the data were not selected randomly
1. farmer recall was used but at least 2 years after the cultivation (the limits of the farmers recollection is stated as one of the limits of the study); 2. only 1 year survey; 3. personal protective measures for pesticide applications as confounding variables were not analysed to connect GM cultivation and health effects; 3. differences between GM and non-GM farmers were not analysed
Institutional conditions such as subsidies, extension services, price controls were registered as general background but their impact on the results has not been assessed
The only study that registers the types of pesticides used. The season 2000–2001 shows a marked decrease in pesticide poisoning for non-GM users and farmers with both GM and non-GM plots. This finding is left unexplained
Although having a quite good random selection (except for state level) the authors also control for non-random selection bias. The paper points out that hired labourers might reduce the reporting of poisonings. The correlation between Bt adoption and reduction on number of poisonings is strong for full adopters and insignificant for partial ones. Also, the effect of Bt cotton adoption on poisonings is significant only after a few years of cultivation (authors hypothesize it to be due to a suppression of bollworm infestation following a widespread adoption of Bt cotton)
Authors control for self-selection bias by verifying the results on the sub-sample of partial adopters. No statistical correlation was performed between pesticide amounts and poisonings. It was a reduction in the pesticides used but not as much as in China or India (authors suppose it was due to a higher pressure of sucking pests or lack of experience with the technology)
No statistical correlation was performed between pesticide amounts and poisonings. The poisonings are reported as “health problems at the time of the spray”. Whether or not they are correlated with the pesticide use, it is not stated. In fact, the study does not have any comment about the health effects of pesticide use. An important confounding variable is the rainfall: during the studies year it was 33% less than normal
The possibility for a self-selecting bias was eliminated through a cohort study research. No systematic bias due to loss of written records by Vunisa (data was validated). For the number of pesticide poisonings, there was no comparison between Bt and non-Bt adopters. It looks like that the authors attempted to bring only circumstantial evidence between Bt adoption and health benefits
It points toward another possibly determinant affecting the impact of GM crops cultivation: spurious seeds. Liu focuses very well on some issues like pest pressure but completely ignores other such as irrigation and the reasons for returning to conventional cotton cultivation.
Dealing with selection bias: the 1st chapter of the dissertation focuses on what determined the adoption of Bt cotton. Data on health effects has no details: impossible to say if the number of poisonings are connected to Bt cultivation
Results for the 2nd research question
ID of the form
Morse and Bennett (2008)
Wang et al. (2008)
Bibliographic reference (main article)
S Morse, R Bennett (2008). Impact of Bt cotton on farmer livelihoods in South Africa. International Journal of Biotechnology 10(2–3): 224–239
G Wang, Y Wu, W Gao, M Fok, W Liang (2008). Impact of Bt cotton on the farmer’s livelihood system in China. Integrating Social Science Research Into Cotton Reform Implementation lined with the international outlook (ISSCRI) International Conference, 13–17 May 2008, Montpellier, France
South Africa/ Hlokoloko, lying at the centre of Makhathini Flats in KwaZulu Natal
China/ Guangzong, Shenzhou and Hejian counties; main cotton production areas in Hebei province
Survey 2 years. Follow-up survey of members previously interviewed in 2001. Semi-structured questionnaires. One farmer organisation
Survey 2 years
88 out of 100 respondents claimed that they benefited in terms of higher income
Net incomes: 2002: 8708.6 yuan/ha (GM cotton) vs 3059.4 yuan/ha (non-GM); in 2003: 13633.3 yuan/ha (GM) vs 7231.7 yuan/ha (non-GM). How was the income calculated (not including labour)?
The increased income was not used to improve health; ‘spend on themselves’ includes entertainment, electronic goods and clothes
Increased income translated into increased expenditures on education, leisure and health care; was a significant correlation between the transportation, communication, education, health care expenditure and cotton income through the canonical coefficient analysis
Main sources of bias
1. Only one area studied; 2. producer recall was used, although farmers were interviewed about recent data (same season and the previous one); 3. differences between GM and non-GM farmers were not analysed; 4. no confounding variables in the calculation of farmers’ income
1. Only one area studied; 2. producer recall was used, although farmers were interviewed about recent data (same season interview); 3. differences between GM and non-GM farmers were not analysed; 4. no measures to deal with attrition
Increased income was registered as a perception. Actual numbers on Gross Margin were compiled to see any differences between seasons (no differences). There was no baseline or benchmark to compare before/after situation
Some contradiction about the weather: in 2003 weather it is stated was favourable to cotton toward the end of the article and unfavourable at the beginning
Characteristics of studies included
The remaining nine studies were analysed to extract data according to the protocol . The studies took place in a total of four different countries: China, India, Pakistan and South Africa. An overwhelming majority (8) of the studies concerned cotton, whilst one study focused on pre-production trials for rice. There were no studies focusing on more than one crop. In terms of cultivation study duration, the surveys and written data covered: 1 cropping season (3 studies), 2 seasons (3 studies), 3 seasons (2 studies) and even 4 seasons (1 study) (see Tables 3, 4). All the GM events were insect-resistant. Information concerning the types of pesticides used by farmers was generally absent with a few exceptions. There was one study that investigated pesticides in terms of the hazard categories to which they belonged according to World Health Organization definitions, and ranked and reported the amount of pesticides used in each category (study #3, see Appendix 1). In addition, two other studies reported the most popular pesticide for the region surveyed [Emamectin (study #4) and Cypermethrin (study #7)] yet did not register the exact amounts used by farmers.
The grey literature was a source of a diverse range of publications included in data extraction: 13 peer-reviewed articles, 2 working papers, 2 conference articles, 1 monograph and 1 doctoral thesis.
Regarding the funding sources, among the nine studies, with the exception of two studies that did not mention funding agencies or donors, funding for research generally came from academic and research institutions. Industry contributed to the funding in only one case (study #2).
As mentioned previously, context is very important in measuring the impact of GM crop cultivation, as it can introduce confounding variables that can considerably change the conclusion drawn and the potential for generalisation of the results. In this systematic review, the main constituents of agricultural context were the weather (including climate and pest pressure), farm and farmers’ characteristics, and institutional characteristics (agricultural credits and subsidies, price control policies, agricultural extension services, etc.). The study farms were subject to climate typical for the cultivation of cotton or rice. However, for studies that spanned more than 1 year, variations in weather conditions, especially rain, impacted the amount of pesticides applied and cultivation costs (especially due to the need for increased pesticide use and irrigation). Cotton bollworm infestation, for example, usually increases in a wet season, whilst a drought makes the use of irrigation necessary. Information about the weather helps to demonstrate causality between the cultivation of the GM crops and the increase/decrease of pesticides or increase/decrease of farm incomes. It also gives numerical results (statistics) a better understanding. If GM crop adopters receive greater benefits than non-adopters, even in seasons with bad weather and increased pest pressure, it is a strong indication of the added value of the GM crops.
For the first research question, pest pressure was the primary concern, because the amount of applied pesticide is usually adapted by farmers according to the level of infestation observed. Two studies formally included pest pressure in the analysis (studies #1 and #9), three mentioned it only as a potential factor impacting the use of pesticides, whilst two studies did not mention pest pressure at all. Of the last two, study #3 stated that no major climatic changes occurred for the period surveyed, and study #6 stated that rainfall was 25% lower than usual during the research period. Therefore, no weather-related bollworm infestation was reported in the areas analysed. For the second research question, one study reported a drought for the period surveyed with no irrigation measures in place (study #5), whilst the other reported neither weather nor irrigation information (study #8).
In attempts to determine causality, the characteristics of farms and farmers are routinely registered in surveys of pesticide use or economic impact. In this case, the question could be reformulated as: “is the use of pesticides or household income determined by the new technology alone or by the characteristics of the users?” Amongst the farmer characteristics most registered in surveys, the current review focused on age, gender and education, whilst those of the farm included size, area cultivated with GM/non-GM crops, and the use of any pesticide protective measures when spraying. Although age, gender and education are amongst the variables that are commonly registered in surveys, only a few studies investigated their connection with the technology (studies #2, #3 and #7). The same studies were also the only ones that analysed whether the benefits of GM crop adoption depended upon farm size. The area cultivated with GM or non-GM crops was generally registered with two exceptions (studies #4 and #9). With the exception of study #5 that used a before-after type of impact study (i.e. non-GM crop cultivation followed by GM crop cultivation on the same area), the other studies surveyed farmers cultivating GM and non-GM crop concurrently. Only study #7 tested if farmers used protective measures when spraying pesticides.
As positive results obtained with an agricultural technology such as GM crops can be attributed to price controls for seeds, credits or subsidies for their cultivation, as well as to the training of farmers in the proper use of the technology, data was also extracted concerning these institutional characteristics. Of the nine studies, six did not mention agricultural subsidies, seven did not mention agricultural credits, and eight did not mention if price control policies were in place. The role of extension services was reported in only two of the studies.
Systematic review limitations
The literature search only focused on English language articles and freely-available sources. As the results of the pre-protocol screening pilot  indicated, the number of articles published in Spanish or Portuguese was much lower than those in English. In addition, studies concerning GMO impacts tend to be published in English to garner the greatest readership. Therefore, it was considered that the limitation posed by the exclusion of studies in Spanish or Portuguese (even if the cultivation of GM crops is extensive in areas where such languages are spoken) was minimal. A possible concern, however, was the inability to conduct searches for relevant articles published in Standard Chinese/Mandarin and the present research has no way of evaluating this limitation. Furthermore, due to the search being limited to only freely-available sources, 16 articles were not retrieved, even after contacting the authors. As some of these did not have comprehensive abstracts, it was difficult to assess if the articles were likely to contain relevant data.
Furthermore it was not clear to what extent poor reporting of the results and the methodology used in the retrieved studies may have introduced bias into the analysis of those studies. However, for studies that spanned more than 1 year and for which more than one publication was produced, it was possible to identify a substantial amount of supplementary information to help reduce bias from poor reporting. In addition, a further limitation was the fact that ongoing research was deliberately not included in the protocol for this Systematic Review .
In relation to the first research question, all of the nine studies reported a decrease in the amount and number of pesticide sprayings during the cultivation of GM crops (Table 3). For the final variable, the number of poisonings, all studies reported a reduction in the number of pesticide-associated poisonings during the cultivation of the studied GM crops. However, the results varied considerably for both pesticide use and number of poisonings. Concerning pesticide quantities, the studies directly reported reductions ranging from 18% in India (study #6) to over 70% in China (study #9), and reductions in the number of sprayings by almost 13 in China (study #2) to only one in India (study #6). Sometimes there were significant variations in pesticide use between different areas included in a study (study #2). For the number of poisonings, the cases varied from 0 for farmers that had only GM crop plots (in China; study #1) to 25% of GM crop-cultivating farmers (in India; study #6). As reporting was not uniform between studies, no easily comprehensible graphs could be prepared to demonstrate the variation in results. Most studies provided information on both the amount of pesticide used and the number of sprayings, however only a few studies provided one variable for measuring pesticide use. For one study (study #9), the number of pesticide poisonings was not even separated between the GM and non-GM crop adopters, nor was it reported per year; it was simply reported as a percentage of farmers who, for the period analysed, reported pesticide-related health problems.
The variation in the amounts of pesticides used (within the same study or between studies) has been attributed by the study authors to: (1) climatic conditions driving fluctuations in the prevailing pest populations; (2) the use of lower quality seeds, either through the purchase of spurious seeds or through the practice of saving seeds; (3) the development of resistance in the target pests (study #2); (4) the rise of secondary pests; (5) differences in extension services (study #4), or; (6) different farmer attitudes to risk (risk-averse farmers using more pesticides; study #9). However, possible confounding variables in the use of pesticides were not explored in the majority of the studies analysed. Only two studies established a strong correlation through regression analysis between GM crop cultivation and a reduction in pesticide use (studies #1 and #3). Further correlations between the use of pesticides and pesticide-associated poisonings were pursued in only two studies (studies #2 and #3).
For sources of bias, a qualitative analysis (Table 2) revealed that, with one exception (study #7), the studies based their analysis on farmer recall. An attempt was made in four studies (Table 3) to minimise bias by conducting each survey at the end of the agricultural season. A major bias, however, was the fact that personal protective measures for pesticide applications as confounding variables were not analysed as an element connecting GM cultivation and health effects (with one exception, study #7). In only two cases (studies #2 and #4), it was generally stated that farmers in the study region did not usually use protective measures when spraying, but relevant questions were not included in the surveys to verify this fact. Further, three studies did not test these differences between GM and non-GM crop adopters, whilst another three reported the results of only one cultivation year.
There were studies that introduced new perspectives to consider. For example, study #2 was the only study that analysed the types of pesticides used and how the cultivation of GM crops impacted each category of pesticides. GM crops appeared to have the strongest impact (reduce the amount used) on the most toxic category of pesticides (e.g. organophosphates, pyrethroids). Given that all of the final studies reported a reduction in pesticide use with the cultivation of GM crops, it would be worth further exploring the impact on different categories of pesticides, to definitively establish whether or not GM crop cultivation results in a reduction in the use of highly toxic pesticides. In addition, as agricultural impact studies generally have to work with available acreages of the technology instead of the preferred random assignment, and that self-selection bias (when individuals become members of a specific study group due to autonomous farm-based decisions, e.g. by choosing to cultivate GM crops) was not included as a major source of bias to track, two of the studies conducted analyses to control for non-random selection bias (studies #3 and #7). Furthermore, study #9 used regression analysis to evaluate the behavioural characteristics of farmers, namely attitudes towards risk, as another potential main determinant in the use of pesticides. Farmers who were more risk averse continued to use high amounts of pesticides even after adopting GM crops. Training can correct the tendency, but needs to be repeated at regular intervals to avoid being lost over time. In addition, the study found that one of the reasons for the risk averse behaviour was the unreliable quality of the seeds. Either the presence of spurious seeds or variations in the quality of the seed of approved commercial events left farmers distrustful in the seeds that they purchased, thereby resulting in higher amounts of applied pesticides as a guarantee of harvest quality. Spurious seeds, as a possible source of quality reduction of the GM seeds and thus requiring greater numbers of pesticide spraying, were only reported in studies #2 and #4. Another confounding variable reported by authors concerned the possibility that the use of hired labourers may have affected the number of poisonings, however this hypothesis was not further explored (study #3).
For the second research question, only two studies were found to be relevant (Table 4). Both studies determined that the cultivation of GM crops increased farmers income without, however, separating the reporting between farm owners and labourers. Regarding the uses for the extra income, study #5 found that farmers mostly invest in their children’s education, in cotton cultivation (unspecified) or to repay debt, respectively. Health was not reported as an expenditure category, even as part of the lower-rated categories such as “spend on themselves”. In study #8, a canonical coefficient analysis found that education was again a priority in household expenditure for the extra income accrued, along with leisure and health care.
Both of these studies (study #5 and study #8) had several sources of bias. They focused on only one cultivation area, although this is not unusual for in-depth studies. Both studies did not test differences between GM and non-GM crop adopters (study #5 used a before-after methodology). Both also relied on farmer recall for relevant data. Moreover, study #5 undertook only one round of interviews regarding the previous two agricultural seasons. If farmers are interviewed immediately at the end of the agricultural season with questions pertaining directly to that particular season, the information gathered is still fresh in their minds and is therefore more accurate, thereby reducing recall bias. In addition, study #5 did not consider confounding variables in the calculation of farmers’ income, while study #8 had no measures to deal with survey sample attrition. Additional shortcomings included establishing increased income by reporting the perceptions of farmers instead of by direct measurement (study #5), and contradictory statements over the weather during the GM crop cultivation (study #8).
In general, the amount of pesticides applied in GM crop cultivation was lower than in non-GM crop cultivation, even though in the majority of cases the results were based on questionnaires (which may risk recall inaccuracies). The link between GM crop cultivation and a reduction in number of pesticide poisonings should be considered as still circumstantial, due to the absence of relevant confounding variables or statistical analyses to support the conclusions. The cultivation of GM crops also appeared to increase household income. It was however not possible to accurately determine what proportion of the extra income is devoted to dealing with health issues. Farmers rated the education of their children as the most important household expenditure overall.
Using surveys as the sole basis of data-gathering should be done with caution. Written records are usually the most reliable source of data, but in the developing world these are often lacking. One way to increase the accuracy of survey data, in the absence of written records, would be to take records immediately following crop harvest. The data should also be submitted to a form of validation (for example, triangulation as was done in study #7).
Although open-ended questions can be used to gather valuable data, concrete questions can more accurately establish a deterministic relationship between variables. Statistical validation of data (correlations between independent and dependent variables, statistical significance for parameters, etc.) can provide a solid basis for further analyses.
Confounding variables have always been a delicate point in surveys, and research in general. If overlooked, the causal relationship may be questioned; if too many are considered, it may make the research unmanageable. Study analyses should focus on identifying appropriate confounding variables so that they can be eliminated or minimised. For example, in relation to the first research question of this review, one essential confounding variable seldom considered in the analysed studies was the use of protective wear for farmers when spraying pesticides.
The foregoing recommendations acknowledge however that studies relying on widespread GM crop cultivation for data acquisition may have difficulty in identifying ideal test/survey areas. Study design may have to be adapted accordingly, with a possible consequence of a reduction in the power of their analyses. Many of the studies that entered the present data extraction, for example, were of high quality, considering the limitations faced by agricultural surveys in general; the unwillingness of some farmers to participate in surveys; the lack of any written data, and; the lack of funding to undertake surveys with numerous variables, to name but a few.
In addition, the review found that information relevant to the non-food impacts of GM crop cultivation on farmers’ health is generally available at no cost (either free to download or provided by authors when requested).
GM crops are a highly politicised issue and their potential impacts are presented as facts before being thoroughly studied. For example, there are reports that tend to take at face value the fact that a reduction in pesticides use associated with the cultivation of GM crops leads also to a reduction in occupational pesticides poisonings. This review indicated however, that there are several variables that could impact such possible cause-effect relationships and that further research needs to be undertaken to substantiate any such claims.
Overall, the present systematic review uncovered weak connections between GM crop cultivation and (1) pesticide poisonings, (2) income, and to any subsequent general health improvements. A possible reason for the lack of strong connections may be that they were not the main objectives of the studies analysed. In such a case, new studies aiming to expressly generate clearer evidence linking the intermediary and final variables studied in this systematic review would be very useful.
All authors read and approved the final manuscript.
The authors would like to thank two anonymous reviewers and the Editor-in-Chief, Andrew S. Pullin, for their helpful comments.
Compliance with ethical guidelines
Competing interests The authors declare that they have no competing interests. The systematic review was funded by the ICGEB, both from its core funding, as well as from external funds raised by its Biosafety Unit.
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