Pesticides: are the risks different for men and women?
Margreet van der BurgThe different lifestyles, occupations and biology of men and women could mean that pesticides affect them in different ways. Margreet van der Burg shares evidence from SPRINT that highlights some of these differences.
When you think of pesticides, you may not immediately think of gender inequality issues. However, more and more scientists are recognising that many environmental health risks affect men and women in different ways – either because of their gender (social roles, norms and power relations) or because of their sex (biological characteristics, such as hormonal and reproductive systems).
In the case of potentially toxic pesticides, understanding differences in how they affect males and females could lead to more comprehensive risk assessments of pesticides.
Moreover, they could also enable more effective health protection measures. Studies have linked pesticides to illnesses including cancer and Parkinson’s disease. They have also been linked to disruption of the hormonal system. This is key given that the hormonal system is not the same in male and female bodies.
Currently, safety standards to protect people from pesticides’ possible risks, such as the acceptable daily limit (ADI – an intake limit set by regulators) are designed to protect the population as a whole. They do not differentiate between different groups of people, some of whom may be more at risk than others.
To help understand the potential risks of pesticides, the SPRINT research project measured pesticides residues in the environment, in homes, in our food, and in human and animal bodies. We also explored some of their possible effects on health.
Importantly, we separated out results for males and females. Here are some of our key findings.
How do gender roles in farming affect pesticide exposure?

The scale and nature of exposure are key factors in determining whether pesticides pose a risk to you or not. That is: how likely are you to encounter pesticides, how many, in what quantities and how often? The higher the exposure, the higher the potential risk.
In farming, gender roles often shape who performs which tasks. Previous studies show that men are often more likely than women to spray pesticides.
In one SPRINT test, we found that male farmers working on conventional farms in Europe had the highest numbers and levels of pesticide residues on silicone wristbands that picked up residues from their environment. This was compared with female farmers, organic farmers, and non-farmers. These results suggest that male non-organic farmers had the most direct contact with pesticide mixtures.
However, men and women’s roles can differ depending on the type of farm (e.g. organic vs. non-organic), the farm’s size, and the country. We recommend that future research looks into this variation in more detail, as well as changes in gender roles that influence farmers’ pesticide exposure. Gendered divisions of labour are changing on many farms and in many places, with more women taking on tasks traditionally performed by men.
It is also important to look into broader structural factors that shape gendered patterns of pesticide exposure in farming, including differences in access to training, the use of protective equipment and decision-making power.
Pesticide residues in the home: gender implications of exposure

While it is concerning that male farmers may be exposed to the highest levels of pesticide residues in Europe, it is not necessarily surprising. What may be more remarkable are SPRINT’s findings in the home.
SPRINT found high numbers of pesticide residues in farmers’ household dust – many more than out on the field. The concentrations were much lower than those on farmland, but the ‘mixtures effect’ (where pesticides interact with one another to have unexpected effects) is a potential concern here.

Total number of different pesticides detected in samples of air, crops, sediment, soil, water and dust collected from 10 European countries. Source: Silva et al (2023)
While all household members could be affected by these residues, women tend to do more domestic work than men and take on more care responsibilities. This may mean women spend more time indoors, increasing their exposure to pesticide residues in household dust.
Certain life stages and health conditions, such as early childhood, pregnancy, older age or chronic illness, also potentially put people at greater risk from exposure to multiple pesticides in the home.
We also found that homes that are regularly cleaned tend to contain fewer pesticide residues in dust. Hygiene practices, such as removing shoes and work clothing before entering the home by (mostly male) farmers, and household cleaning are key.
That said, exposure prevention should not rely solely on domestic surveillance. The primary responsibility lies with effective regulation, safer pesticide use practices and broader risk reduction strategies.
Among non-farmers, our research indicates that women have more direct contact with pesticides in their daily surroundings than men, as shown by our silicone wristband study. More research is needed to understand these findings and their potential health implications, but they may reflect differences in occupations, consumption habits or time spent in particular environments.
It is unclear how our wristband results translate into uptake of pesticides by the body. When we tested blood, urine and faeces for pesticide residues, we did not see clear differences between men and women. This may be because diet drives the intake of pesticides.
However, while the methods used do not show gender differences in uptake, the combined evidence suggests that exposure routes can vary between men and women.
Biological differences affect pesticide risks

So far, we have considered how exposure is affected by gender. We will now turn to the influence of biological sex on how pesticides affect the body after exposure has occurred, drawing on our tests with mice and rats.
In one of our recent studies (now under peer review), we gave mice drinking water containing glyphosate, the world’s most commonly used herbicide. The results were surprising. Even at very low, environmentally relevant exposure levels, the male mice started behaving differently in social situations.
When we introduced a new mouse into their space, they were noticeably less interested in the newcomer. Normally, mice are curious to meet newcomers. This is even the case for mice kept in a laboratory.
The female mice, on the other hand, seemed mostly unaffected by glyphosate at these low levels. It was only at the highest dose that they showed any clear change, moving around less than usual.
These early findings hint at the influence of the gut microbiome on the brain and behaviour. The contrasts in behaviour may be because the pesticide affected different bacterial species in the gut of males than in females, with potential differential knock-on effects on the brain and body.
Further tests on rats revealed adverse effects in males that were not observed in females. For example, glyphosate and acetamiprid affected the circulatory systems of males, tebuconazole harmed their alimentary (nourishment) system and all three of these pesticides affected male reproductive systems.
Future research needs to investigate these sex-differentiated patterns in more depth to better understand why the pesticides had these effects.
Also critical is to investigate whether these sex-specific effects are seen in other species including, of course, humans, but also farm animals. This remains unclear.
Most farm animals (notably cows, sheep, pigs and chickens) are female. They typically live in, or alongside, pesticide-sprayed fields and consume feed that contains pesticide residues. This raises questions about sex-specific exposure and effects in livestock.
We know that pesticides can affect the hormonal system, and it may be hormonal responses that drove the different effects in the mice and rats in our experiments.
Also important is to consider that changes in hormonal status (e.g. puberty, pregnancy, menopause, or medical hormone therapy) may also influence the effects of pesticides. In human research, this also implies that we need to acknowledge that binary male/female categories do not fully capture biological variation.
Gender awareness in research: lessons from SPRINT for other projects
Integrating a meaningful gender dimension in a research project is not just about disaggregating data by sex.
In SPRINT, we established a Gender Committee, including an experienced gender scholar, to ensure that sex and gender considerations were embedded across the project.
The Committee organised training sessions, conducted internal surveys, and worked closely with each Work Package to identify where and how gender/sex analysis could strengthen research design, data interpretation and policy recommendations.
For future research projects, we recommend:
- Include gender expertise from the project design stage.
- Allocate sufficient time and resources for integrating sex and gender considerations across all work areas, both for the gender committee and for project members.
- Allocate sufficient resources to collect sex-disaggregated data for all species involved (and provided this complies with 3R principles for animal tests, notably minimising the number of animals used).
- Consider whether and how any observed patterns relate to sex or gender issues by examining potential correlations with behavioural and wider social patterns more closely.
- Ensure gender experts are fully embedded in meetings, training and communication processes.
The SPRINT Gender Committee’s work appeared to be effective. A survey among the consortium members at the end of the project showed a considerable increase of gender awareness, knowledge, and capabilities.
SPRINT’s findings suggest that pesticide exposure and health risks cannot be fully understood through a neutral lens that disregards sex and gender. Exposure pathways are shaped by gender roles, while biological responses may vary by sex and hormonal issues.
Integrating these dimensions into research and risk assessment does not complicate science unnecessarily, it makes policies and protection measures more accurate and more equitable.
Dr. Margreet van der Burg is Chair of the SPRINT Gender Committee and a Senior Lecturer/Researcher in Intersectional Gender Studies/History related to Food, Agricultural and Rural Research and Development at Wageningen University.
Many thanks to Antonia Riedel, Eoin Gunnigle, Paul Scheepers, Paul Nathanail, Vera Silva and Michelle Kilfoyle for their valuable contributions to this blog.
Want to know more?
- Keep a close eye on our publications page for new research papers on the effects of pesticides on male and female mice.
- SPRINT Report: Exposure to PPPs by gender in farmers, neighbours and consumers (2025)
- SPRINT Report on the gender-specific analysis addressing distinct toxicological effects patterns of pesticides mixtures (2025) Available upon request: This email address is being protected from spambots. You need JavaScript enabled to view it.
- SPRINT Report: Gender insights into the EU-SPRINT project (2022)
- Conference presentation: Pesticide exposure and the microbiota-gut-brain axis, presented by Eoin Gunnigle. Discusses some of the effects of pesticides on male mice.
- Poster (2025): The Gender+ Dimension in SPRINT
Could pesticides affect your gut health? Microbiome findings from SPRINT
Maaike Gerritse
You may have heard that some pesticides can disrupt the gut microbiome. In this post, Maaike Gerritse shares findings from the SPRINT project that show how pesticides affect this delicate ecosystem. She also describes the first ever evidence that pesticides can change the microbiome in your nose that protects you from disease.
Back in 2022, I explained why our research project, SPRINT, was so keen to explore the links between pesticides and the gut microbiome in my blog: How and why SPRINT are studying microbiomes.
A microbiome is the combination of millions to trillions of bacteria, fungi and other micro-organisms that live together. A healthy microbiome in your gut, with ‘good’ bacteria, helps protect you from diseases including cancer, obesity, coronary heart disease, diabetes and dementia. Not only that, but it helps you digest fibre, provides certain vitamins, and keeps stomach bugs at bay by keeping your gut occupied: no space for ‘bad guys’.
Fast forward to today, we have now completed our microbiome investigations on SPRINT. You will be able to learn more about many of these in forthcoming peer-review journal papers (anticipated in 2026).
For now, I am very pleased to give you a preview of some of our key findings. As these results have not yet been peer-reviewed, do interpret with some caution. We will list journal papers as they are published on our website – keep an eye out for them there.
Which pesticides affect the gut microbiome?
Our researchers investigated the gut microbiome by extracting bacterial DNA from faecal samples. Based on this DNA, we could see which bacteria are present in the gut microbiome.
We also looked at which pesticides enter the body from our diets and environment by analysing the blood, faeces, and urine of hundreds of volunteers.
From this, we could link eight pesticides or classes of pesticide with small changes in the composition of the gut microbiome. These substances were: pyrethroids, glyphosate, metalaxyl, hexachlorobenzene, pirimiphos-methyl, propiconazole, DDT and chlorpyrifos.
‘Composition’ refers to which bacterial species are present in the gut, and how abundant they are relative to other species. Importantly, four of these pesticides (propiconazole, pirimiphos-methyl, metalaxyl, and hexachlorobenzene) had not been linked to the gut microbiome before. This suggests that more pesticides may be connected with changes in the gut microbiome than previously thought.
The effects of higher pesticide levels on the gut microbiome
As part of SPRINT, we asked volunteers to wear silicone wristbands that absorb pesticides from the environment, and not from their diet, to learn more about which chemicals they encounter in everyday life.
We found that people exposed to certain pesticides have a slightly different gut microbiome than people exposed to a very low number or a low concentration of pesticides.
Our test results suggest that mixtures of pesticides may have more impact on the gut microbiome than pesticides that are tested individually. This is an important finding since we are usually exposed to mixtures of pesticide residues rather than single compounds.
Which gut microbes are affected by pesticides?
A higher pesticide burden (i.e. total pesticide numbers and concentrations) was associated with a loss of some bacteria, including beneficial bacteria. For example, Bifidobacterium was reduced with a higher total pesticide burden.
Research shows that Bifidobacteria reduce inflammation and are linked to a lower risk of gastrointestinal diseases, allergies, metabolic disorders and depression.
Bacteroides, a dominant group of bacteria in the gut, was also reduced with higher concentrations of pesticide mixtures. Bacteroides help provide energy for the gut and prevent inflammation.
The population of Akkermansia, a group of bacteria associated with metabolic health and a lower body weight, was also lower at higher concentrations of multiple pesticides.
These findings indicate that pesticide-associated changes in the gut microbiome might have consequences for human health.
The nasal microbiome?
Some of you might know that SPRINT also investigated the microbiome in the nose. It is not only the gut microbiome that plays a role in human health; the nasal microbiome also supports your immune system as well as your ability to smell.
An imbalance in the respiratory microbiome is suspected to be a risk factor in respiratory infections, such as asthma, but also Parkinson’s disease and Alzheimer’s disease.
The effect of pesticides on the nasal microbiome has not previously been studied. The respiratory microbiome has many parts. For example, the microbiome of the nose is very different to the microbiome in your throat, mouth and lungs. Our researchers were the first research team to find out that pesticide exposure can be linked to changes in the nasal microbiome.
We discovered an association between the total number of pesticides detected on silicone wristbands worn for one week and changes in nasal microbiome composition – as detected by swabbing the nostrils of our participants and extracting bacterial DNA from the swab.
The pesticides on wristbands mostly came from the participants’ environments, rather than their diets. This suggests that the effects on the nasal microbiome may be due to inhalation of pesticides in the air or dust.
Could pesticides affect your mental health and behaviour?
The gut microbiome is increasingly recognised as an important influence on brain function and behaviour, with good gut health linked to improved mental wellbeing.
However, exposure to pesticides, and other chemicals in the environment may influence the relationship between the gut and the brain by altering the presence or balance of microbes that are involved with communications between the two organs.
In SPRINT, we investigated the effects of glyphosate — a commonly used herbicide — on the gut microbiome and behaviour in mice
Normally, mice are curious to meet newcomers. This is even the case for mice kept in a laboratory. We found that male mice had disrupted social behaviour when we exposed them to glyphosate at low levels, i.e., at the ‘acceptable daily intake’ (ADI) which is the limit set by regulators.
Specifically, the mice interacted less with a new mouse that was introduced to the lab setting, compared with mice in the experiment that were not exposed to glyphosate.
In another test, male mice showed some signs of increased anxiety-like behaviour following glyphosate exposure. Female mice showed fewer behavioural changes (to find out more about sex differences, look out for our upcoming blog on pesticides, sex and gender).
These effects appear to be linked to changes in the gut microbiome. Glyphosate exposure corresponded with subtle but measurable shifts in the composition of gut microbes in both sexes.
When we transferred microbiota from glyphosate-exposed male mice to mice that we did not expose to glyphosate, the recipient mice developed the same social behavioural trait as the glyphosate-exposed mice.
This demonstrates that the microbiota changes were sufficient to drive this effect. Anxiety-like behaviour, however, was not transferable. This suggests that different processes are involved in anxiety and social behaviour.
Many studies, including ours, show that glyphosate is associated with small changes in the human gut microbiome. However, more research is needed to see whether similar effects on behaviour occur in humans. These findings raise important questions about how every day, low-dose exposure to widely used herbicides may influence our behaviour through the gut microbiome.
What do these findings mean for your health?
These changes to microbiomes may have consequences for your health. Regulators have many safety considerations when deciding whether to approve a pesticide for the market. The effects of pesticides on the microbiome might be an interesting new factor for them to consider.
However, while we know that the gut microbiome is very important for health, many other factors can interfere with its composition, such as your age, diet, exercise, sleep and medication use.
If you want to protect your gut microbiome, the most important thing is to eat a fibre-rich diet with many fruits and vegetables and consider buying organic products when you can.
To further support your gut health, you should limit your sugar consumption, stay well‑hydrated, get enough sleep, and exercise regularly.
What about your nose? Just as for the gut microbiome, there are many factors that influence the nasal microbiome, and many more studies are needed to better understand how it works.
However, it is possible that regularly cleaning and airing your home may help protect the nasal microbiome from pesticides in your environment. SPRINT has also shown that pesticide residues accumulate in household dust. In our silicone wristband study, we found that study participants who reported regularly cleaning their homes and opening their windows were less likely to have direct contact with pesticides.
Want to know more?
Keep a close eye on our publications page for new research papers on pesticides and the microbiome.
Webinar: Pesticides and Human Gut Health, presented by Maaike Gerritse and Milla Brandão Gois.
Research paper: Pesticide exposure and the microbiota-gut-brain axis. By: Matsuzaki, R., Gunnigle, E., Geissen, V., Clarke, G., Nagpal, J., Cryan, J F., in The ISME Journal (2023).
Research summary: Linking synthetic pesticide exposure to the gut microbiota and brain functioning.
Conference presentation: Pesticide exposure and the microbiota-gut-brain axis, presented by Eoin Gunnigle.
Thank you to Eoin Gunnigle and Paul Scheepers for their valuable contributions to this blog.
How many pesticides contaminate farmers’ homes and the environment?
Michelle Kilfoyle, Charlotte Chivers, Paul Scheepers
SPRINT has quantified the ‘cocktail’ of pesticides present in freshwater, air, soil, farm household dust and crops across Europe and in Argentina. Our results support the case that regulators should consider mixtures when assessing pesticide risk.
Scientists are increasingly worried about the complex mixtures of pesticides present in our environment.
In the EU, over 400 active ingredients for pesticides are currently approved for use (as listed on the EU pesticides database). Farmers often apply multiple products to their crops to protect them from pests and disease. The resulting residues can travel far and wide – for instance, in air and water, on food, or even on the soles of our shoes.
This creates mixtures of pesticide residues – many of which are considered hazardous to humans, wildlife, and ecosystems. These mixtures are not only found on farmland; they also permeate our everyday surroundings and the wider environment too.
Of concern, a growing body of evidence finds that pesticides can have unpredictable and stronger effects when they are combined in mixtures. To give just one example, a 2022 study from France found that a pesticide mixture found in farmland soil was highly toxic to springtails – important soil-dwelling insects. This was even though the individual substances in the mix were at levels that regulators consider ‘safe’.
SPRINT: counting pesticides for more effective regulations and policy
In the largest study of its kind, the SPRINT research project measured used pesticides in the environment. We did this across multiple locations in Europe and Argentina, and in multiple matrices, or ‘components’, such as soil, water and air.
Why did we do this? Several reasons, including:
- For a better picture of pesticides’ risks to human health and the environment. Healthwise, when deciding whether a pesticide is safe to be on the market, regulators will consider how much of the substance we will encounter through food and drink. But we may also ingest pesticides from our environment, which could amplify their risks – especially for farm workers and their rural neighbours.
- For a clearer picture of which combinations of pesticides occur, and where. Little is known about the health and ecological risks posed by pesticide mixtures that you’re likely to find in the environment. What we do know about the ‘cocktail effect’ is concerning, yet regulators only tend to assess risks of individual substances.
- To guide risk-reduction strategies. Policies that aim to reduce pesticides’ risks need a clear sense of what the initial risks actually are. SPRINT measured what is in the environment now, to help define targets to work towards.
Our findings...

Infographic displaying total numbers of pesticides found by SPRINT in indoor dust, air, crops, sediment, soil, and freshwater across all samples. It is important to note that the figures above indicate the total number of different pesticides found across all samples. For example, in indoor house dust, the number of individual pesticides found in a single home were between 25-121, with a median of 80 in conventional farms and 65 in organic farm households.
How many pesticides were found in indoor dust of farms?
Pesticide residues were studied in 65 conventional farms and 63 organic farms.
Our study of household dust from farmers' homes in 10 European countries in 2021 detected 197 pesticides in total. The number of pesticides in each home ranged between 25 and 121.
They were in much lower concentrations than on farmland. But their high number is explained by their slow degradation in the dark, dry conditions of most homes – where they can linger for years.
43% of the pesticides we found in the dust are linked to highly toxic effects, including cancer and disruption of the hormonal system in humans.
This work was recently written about by the Guardian, reiterating the importance of this research. When reading this article, please consider the clarifications made above.
>> Learn more about this study in our accessible research summary: Pesticide residues and human health hazards compared against EU classifications
Blog: Pesticide residues in indoor house dust: key recommendations for minimising exposure

Total number of different pesticides detected in samples of air, crops, sediment, soil, water and dust collected from 10 European countries. Source: Silva et al (2023)
How many pesticides were found in crops?
Our study of crops from 10 European sites in 2021 found a total of 78 pesticides.
A total of 76 were found on crops from conventional farms, and 25 on crops from organic farms.
Many of these compounds were already banned, such as the carcinogenic insecticide, dieldrin, which the EU prohibited 40 years earlier in the 1980s.
>> Learn more about this study in our accessible research summary: Pesticide residues and human health hazards compared against EU classifications
How many pesticides were found in freshwater?
Many freshwater bodies, such as ponds, lakes and streams, are already in a very poor state, and suffer biodiversity loss. Pesticide contamination is partly to blame for this.
Our 2021 study of freshwater bodies in 11 heavily farmed areas of Europe and Argentina detected 115 pesticides altogether.
Up to 37% of these are listed on PAN’s International List of Highly Hazardous Pesticides. And, in some locations, concentrations of certain pesticides exceeded regulatory limits under the EU’s Water Framework Directive. This means they posed risks to wildlife.
Another of our studies, across 10 European countries, detected 112 pesticides in water.
The deterioration of freshwater ecosystems is highly concerning. While they represent just 0.01% of water on Earth, they are home to around 10% of all recorded species.
>> Learn more about these studies in our accessible research summaries:
- Assessing pesticide residues occurrence and risks in water systems: a pan-European and Argentina perspective
- Pesticide residues and human health hazards compared against EU classifications
How many pesticides were found in sediment?
Sediment accumulates at the bottom of streams, rivers and other waterbodies and is critical to the health of freshwater ecosystems. It is known to trap pollutants, including pesticides, and could act as a ‘chemical timebomb’.
Our study tested sediment from 38 water bodies across 8 European countries.
We found 99 different pesticide residues in the sediment samples.
27 of these were not approved for agricultural use at the time of the study. They included DDE, a breakdown product from the long-banned and highly toxic pesticide DDT.
>> Learn more about this study in our accessible research summary: Pesticide residues in European sediments: concerning for aquatic environments?
How many pesticides were found in air?
Agricultural pesticides can become airborne through spray drift, vapor from contaminated soil or water, or in contaminated soil particles eroded by the wind.
In 2021-2022, we tested air weekly on farms in Portugal and the Netherlands.
We found 99 pesticides in total.
Nearly all of the 96 samples contained between 10 and 30 pesticides.
In another 2021 study, this time across 10 European countries, we found 76 different substances altogether.
Levels of each pesticide were low, but we don’t yet know if inhaling these substances over the long term carries health risks, or how their risk changes within pesticide mixtures.
>> Learn more about these studies in our accessible research summaries:
- Pesticides and their breakdown products in rural air
- Pesticide residues and human health hazards compared against EU classifications
How many pesticides were found in soil?
Healthy soils are crucial to food production. As such, several EU policies, such as the Zero Pollution Action Plan, call for the prevention and reduction of soil pollution, including by pesticides.
Our study of farmland soil across 10 European countries in 2021 detected 100 different pesticides altogether.
Most of the 201 soil samples (88%) contained more than one pesticide. One sample contained 21 different substances.
We found 151 different combinations of pesticides containing 2- 21 substances.
Obsolete organochlorine pesticides, such as DDT, were among the most common compounds in these soils.
>> Learn more about this study in our accessible research summary: Pesticide residues in organic and conventional agricultural soils across Europe: measured and predicted concentrations
Things to note
Our project helps show how many pesticides are ‘out there’. However, we need more research to understand what harms (if any) these pesticides can cause to our health and the environment – in these combinations, at these levels and over the long term.
In addition, an even bigger study – or different study locations – could lead to different figures. However, we have provided a good representation of agriculture in Europe – covering conventional and organic farms that produce a variety of crops.
Conclusions and policy recommendations
Evidence from SPRINT highlights the vast number of pesticides in the environment and that they occur in many combinations.
Our results support the idea that regulators should assess pesticides’ risks within a mixtures context. This is not only the case for new pesticides that are yet to be approved (pre-market authorisation). It should also apply to substances that are already in use (post-market authorisation).
Regulators already do some testing of mixtures - of active ingredients that occur in the same plant protection product. But we have shown which mixtures are likely to be found in the environment.
The findings also highlight the persistence of banned pesticides, such as DDT. This means that risk assessments of newer pesticides may need to consider interactions with older ones.
By understanding how these chemicals interact and persist in the environment, policymakers can take effective steps towards reducing pesticide exposure and protecting human health and biodiversity.
This article was written by Michelle Kilfoyle, Dr Charlotte Chivers, and our dissemination and exploitation committee, based on SPRINT research.
Infographic designed by Charlotte Chivers.
Pesticide residues in indoor house dust: key recommendations for minimising exposure
Written by Paul Scheepers
Likely sources of pesticide residues in the indoor house dust of farming households.
This article provides key messages about the presence of indoor dust in farming households, and what you can do to minimise pesticide exposure.
Indoor dust was collected and analysed for pesticide residues in 128 homes of farmers and their families across ten European countries and Argentina. Residues of 198 pesticides and their degradation products were observed. For most contaminants, average detected residue levels were between 0.5 to 20 parts per million (µg/g). Glyphosate and pyrethroid-based insecticides were the most frequently found. In some countries, these residues were found in the homes of all farmer participants. We found that the frequency and levels were lower in homes at organic farms compared to conventional farm homes. However, we have not studied how it is possible that residues are found in homes to such extent, warranting further research.
What is dust?
Dust is a mixture of fine particles from soil and clay, air pollutants, textile fibres, animal hair, and more.
How do pesticides get into our homes?
Previous studies have suggested that residents take home pesticides as dirt under their shoes. For example, a study in the Netherlands analysed doormats and detected a wide range of pesticide residues. For seven of the detected pesticides, a moderate to high correlation was found between levels observed in doormats and residues detected in indoor floor dust collected by vacuum cleaners. In farm homes, these substances were related to fungicide applications on the farm.
Some studies also suggest that pets may carry pesticides into the home – cat and dog ownership is a predictor for increased exposure to insecticides used as flea repellent such as fipronil. Products sold as veterinary drugs and biocides for pets may also become a source of indoor dust contamination.
Another study in France found that indoor house dust can become contaminated with insecticides used for the preservation of wood.
An additional source of contamination of pesticides indoors is the use of pesticides on plants and flowers for home decoration. These ornamental plants and cut flowers may have been treated with pesticides. There is currently no EU regulation to control residues in these products, unlike for most food items.
Finally, and more obviously, is that some of us apply pesticides in our homes, sometimes maybe even without being fully aware – for example, when trying to control so-called ‘pest’ insects such as mosquitoes, fleas, and wasps.
Why do we find so many pesticides in dust?
Pesticides can cling to dust particles, which may include both long-banned, persistent chemicals still lingering in the environment and newer, less persistent pesticides. In the dry, dark conditions common in homes, even pesticides considered less persistent can remain stable for long periods. Since it's nearly impossible to eliminate dust from our homes, some of it can linger for years. As a result, dust serves as a reservoir for both old and current pesticides. Banned pesticides, often highly persistent, can still be found in topsoil and water, while even less persistent pesticides approved for agricultural use may accumulate indoors. Some pesticides break down when exposed to sunlight, but inside homes, they endure much longer due to the absence of UV light.
How does indoor dust lead to uptake of pesticides?
When dust particles are very small, they may become airborne and be inhaled. This depends on the type of floor and cleaning habits. Usually, dust stays on the floor, but when inhabitants move around, including when children play and pets run around the house, dust can become airborne through resuspension. However, even when this happens only a small fraction is inhaled by us.
A more important route of entry is direct contact with dusty surfaces followed by hand-to-mouth contact. This type of indirect exposure is known to contribute to uptake of many contaminants, including pesticide residues. In a study in the Netherlands, a metabolite of carbendazim observed in urine of adults could be linked to traces of this fungicide in hand wipes. This is more likely to occur in young children, particularly crawling toddlers and until they are old enough to fully follow hand hygiene recommendations. One study found traces of pesticides in a small number of nappies (diapers). The origin of these pesticides could not be verified but indoor dust and food intake may have contributed.

Infants and young children may be more at risk of pesticide exposure through indoor house dust due to increased hand-mouth contact.
Is hand-to-mouth contact considered a risk for pesticide uptake via indoor dust?
In national and EU policy, the risk of ingestion of residues from environmental exposures is considered as contributing to pesticide intake. Often a relatively high contribution from ingestion is assumed in risk calculations, especially for children. This leads to a so called ‘conservative’ estimation of the risk. There is not much evidence for dust ingested e.g., by children in different age groups. Recently, the Dust Ingestion Children Study (DIRT) started with funding from the Environmental Protection Agency (EPA) to study how hand-to-mouth behaviour in children translates to ingestion.
What can we do to prevent exposure to pesticides in our homes?

Key recommendations for avoiding pesticide exposure while indoors
Pesticide residues can be taken home with dirt under your shoes. This dirt may contain biological and chemical contaminants including pesticide residues. To avoid this source of contamination, it is suggested to leave shoes outside or at the door when entering your home.
When you buy products that may contain pesticides, doublecheck the label for any hazard symbols and sentences. If you see a warning which suggests calling a doctor in case of an emergency (e.g., if the product is ingested), consider whether you need to use it, particularly if you have small children at home.
Many veterinary drugs for pets are pesticides that may be toxic to humans. Once pets are treated with a flea repellent collar or oil, this may become a source of contamination of your home. Direct unprotected contact with the fur of recently treated pets may cause transfer from pet to human.
Do not cut ornamental plants and cut flowers on the unprotected kitchen bench (where you also prepare your food). Put on gloves and carefully clean the surface with a wet towel afterwards. Before preparing food, remember to wash your hands.
This article was prepared by Paul Scheepers and Hans Mol. Infographics were designed by Charlotte-Anne Chivers.
Any questions? Get in touch: This email address is being protected from spambots. You need JavaScript enabled to view it.
When considering the presence of pesticides in our environment, you might think about the outside world: soil, groundwater, sediment and crops are all contaminated with pesticide residues. But pesticides are also present in the indoor environment and accumulate in house dust. Researchers from CIEMAT have analyzed 128 dust samples from farmer households and 40 samples from non-farmer households. Results were remarkable: Even samples from non-farmer households contain 57 different pesticides (median). Many of these compounds have been banned from agricultural application in Europe, but can persist in house dust for extensive periods of time.. Not a single sample was free from pesticide residues.
Almost half of the pesticides measured are recognized as highly hazardous, and their presence in indoor dust may be of risk to human health. Potential effects of exposure to these pesticides include reproductive effects and hormone disturbances, irritation of the skin, eyes and respiratory tract, and cancer. Exposure to pesticides can also impact the gut microbiome. People and pets may be exposed to low concentrations of pesticide residues via inhalation of house dust, but also through accidental ingestion. It is estimated that the ingestion of indoor dust is approximately 30 mg/day for adults and 60 mg/day for children. For some compounds, ingestion of dust might be the main route of exposure. 
The scope of contamination
The farmers participating in this study were from 11 different case study sites in SPRINT, located throughout Europe and in Argentina, and the non-farmer participants were neighbours of farmers and ‘consumers’ living further away from farmland in France and Denmark. The participants were asked to collect the dust from their house during a period of a month, via vacuum cleaning. The presence of 198 pesticides was evaluated; 197 compounds were detected in the samples, demonstrating a huge variety of compounds found in house dust. The number of different pesticide residues detected in each sample ranged between 25 and 121 for farmer households and between 36 and 80 for neighbour and consumer households.
Conventional farms using plant protection products exhibited significantly higher numbers of different pesticide residues (80 residues/sample, median) compared to organic farms (65 residues/sample, median) and non-farmer households (57 residues/sample, median), and total concentration was also significantly higher on conventional farms.
Types of pesticide residues detected
17% of the tested compounds were present in more than three quarters of all of the farmer-household samples. Multiple pesticides were even detected in >99% of samples: The insecticides fipronil and imidacloprid, the fungicides fludioxonil, hexachlorobenzene, azoxystrobin, carbendazim, tebuconazole, and a synergist, piperonyl butoxide.
The presence of some of the compounds cannot be explained by recent pesticide applications in the area. Interestingly, imidacloprid and hexachlorobenzene were not approved as a plant protection product at time of this study. However, imidacloprid is often used to treat pets against fleas. In this study, 69% of the farmer participants owned pets, which might explain the high presence of imidacloprid. Hexachlorobenzene has a long field half live, and its presence in dust could reflect historical application of the compound.
Potential human health effects
Glyphosate, pyrethroids and the synergist piperonyl butoxide were found in the highest concentrations. Exposure to these compounds is a risk for human health; Glyphosate and some pyrethroids are possible carcinogens and hormone disruptors and are known to impact the gut microbiome. Piperonyl butoxide is also a known endocrine disruptor and known neurotoxicant. While concentrations of individual pesticides in house dust are relatively low, total concentrations of up to 283 μg/g where measured, which is high compared to other matrices measured in SPRINT. Not much is known about potential health effects of combined exposure to low concentrations of a large number of compounds. Imagine you can handle drinking 4 beers, or 3 glasses of wine, or 1 glass of whiskey, but what would happen if you drank all of them at the same time, every single day? SPRINT researchers are especially interested in elucidating the effects of these ‘cocktails’ on human health, as combined exposure is not taken into account when approving plant protection products for agricultural application. Clarifying these effects can assist future policies for pesticide application. The ultimate goal, of course, is to ensure food availability while protecting human health.
Sources:
Navarro I, De la Torre A, Sanz P, Baldi I, Harkes P, Huerta-Lwanga E, Nørgaard T, Glavan M, Pasković I, Pasković MP, Abrantes N…, Martínez, MA. Occurrence of pesticide residues in indoor dust of farmworker households across Europe and Argentina. Science of the Total Environment. Dec 20;905:167797 (2023). https://doi.org/10.1016/j.scitotenv.2023.167797
Silva V, Gai L, Harkes P, Tan G, Ritsema CJ, Alcon F, Contreras J, Abrantes N, Campos I, Baldi I, Bureau M, Christ F, Mandrioli D, Sgargi D, Pasković I, Polić Pasković M, Glavan M, Hofman J, Huerta Lwanga E, Norgaard T…, Geissen V Pesticide residues with hazard classifications relevant to non-target species including humans are omnipresent in the environment and farmer residences. Environment International. Nov 1;181:108280 (2023) https://doi.org/10.1016/j.envint.2023.108280
Icon credits:
Vacuum, hormone, cancer ribbon: flaticon.com
Inhale icon: Pike Picture from Noun Project
Ingest icon: Andrew Doane from Noun Project
Gut icon: Imron Sadewo from Noun Project
Integrated pest management (IPM) in practice: an overview.
Written by Honor Mackley-Ward
Integrated Pest Management (IPM) is an ecosystems-based approach to managing pests. It emphasises reducing the negative impacts of pest management on agro-ecosystems, through using natural pest control (such as supporting a healthy ladybird population, which helps control aphids), improving crop resilience, and minimising the use of pesticides.
IPM was developed in response to the negative impacts of synthetic pesticide use, which makes it particularly relevant for SPRINT’s work. Synthetic pesticides emerged at scale from technologies developed during the second world war, and led to radical changes in agricultural pest management. However, pesticide resistance amongst target pest species and negative environmental and human health impacts associated with pesticide use soon emerged. By the 1950s, practices which align with the modern principle of IPM were being used to combat these impacts, and the term ‘IPM’ coined in the US in 1967.
Over recent years, the term has been adopted by a broad range of agricultural stakeholders, all supporting its principles. But what is IPM, where did it come from, and what is its significance for the SPRINT project?

Pesticides and Human Health: an Overview
Written by Honor Mackley-Ward
Source: Canva Pro
Pesticides, including herbicides, insecticides, and fungicides, and also known as plant protection products, are used globally in agriculture and a number of other industries. This article explores the interactions between pesticides and human health, a subject at the core of SPRINT’s ongoing work.
In the past year, we have gathered hundreds of samples across the SPRINT case study sites (Click here for more information). Many of these samples will be used in microbiome analyses, including: soil samples, gut samples from fish, fecal samples from humans and livestock, and nasal swabs from humans. We will analyse the composition of microbes in these samples. All of these samples contain millions of bacteria, fungi and other micro-organisms, which in combination, are called the microbiome.
Agricultural pesticide use in Argentina: The extent, the risks, and the challenges
Written by Charlotte ChiversArgentina is the only non-European case study site included in SPRINT. We included Argentina in our project because it is the main exporter of soy for animal feed in Europe. In addition, this allows us to compare our findings in Europe against those in South America, where pesticides are often applied more frequently and in greater volumes. Argentina, our chosen case study, is the third biggest pesticide user in the world, with only China and the US using more. In addition, several of the pesticides used in Argentina are no longer approved for use across the EU, so this case study will provide insights into the risks of imported chemicals. This article provides an overview of farming in Argentina before examining the extent of pesticide reliance and the potential risks of current usage.
The UK governments’ decision to allow the emergency use of a neonicotinoid: unravelling the complexities
Written by Charlotte ChiversOn Friday 8th January, the UK government decided to allow the use of a neonicotinoid-based pesticide, thiamethoxam in emergencies. They had previously pledged to maintain a ban on this chemical in line with the EU’s stance towards neonicotinoids.
The UK is not the only country to make this decision, with 11 others also permitting the use of this pesticide in emergencies. These countries include Belgium, Denmark and Spain. These are not the first European countries to lift the ban of thiamethoxam on sugar beet fields; France has already lifted their ban on neonicotinoids.
The news headlines and Twitter uproar resulting from this decision suggests that the public are unhappy with this decision.
More...
When medicine feeds the problem: Are pesticides feeding crop pests?
Written by Charlotte ChiversSPRINT recently attended a fascinating talk at the Oxford Real Farming Conference. Researchers from the University of Edinburgh shared their findings surrounding why pesticides may, paradoxically, benefit crop pests. The research was born from the work by a French agronomist, Francis Chaboussou.
Plant protection products: The what, the why and the how
Charlotte ChiversWhat are ‘plant protection products’?
The term ‘plant protection product’ refers to ‘pesticides’. These chemicals are used by farmers, gardeners and foresters to protect crops and increase their yields. Pesticides contain active ingredients such as toxic chemicals, plant extracts, pheromones, micro-organisms or viruses for controlling unwanted ‘pests’. These ‘pests’ can include insects (insecticides), fungi (fungicides) or plants (herbicides).
Due to the risks associated with PPPs, European regulations[1] place limits on how they are used. These regulations are based on the risks to human and environmental health associated with the active ingredients of PPPs.

