Pesticides Around the Home: Safe Use and Alternatives author: Tayren N. Ben-Abraham, MPH, MSc, M.A., M.A.
Figure 1. Man spraying crops with
Introduction
Pesticides
are chemicals or other substances used to control organisms considered pests
(Khan et al., 2023). They can help control insects, weeds, fungi, rodents, and
other unwanted organisms around homes, gardens, and farms (Daraban et al., 2023).
Pesticides can be useful, but unnecessary use can increase opportunities for
exposure and toxicity (Tudi et al., 2022). So, one may ask, “Are there any
alternatives I can consider to lessen my exposure?” Gladly the answer is yes. The
alternative, Integrated pest management (IPM), offers another approach:
prevent pest problems when possible, use nonchemical methods first, and use
pesticides when they are actually needed (Angon et al., 2023).
What Is a Pesticide?
Different
pesticides target different types of organisms:
- Insecticides control
insects (Gul et al., 2023)
- Herbicides control
unwanted plants and weeds (Ofusu et al., 2023).
- Fungicides control
fungi (Islam et al., 2024).
- Rodenticides control
rodents (Blazic et al., 2024).
- Molluscicides control
slugs and snails (Adomaitis et al., 2022).
Pesticides
work in different ways with some interfering with the nervous system, while
others affect growth, reproduction, metabolism, or cellular function (Garud et
al., 2024). Some pesticides come from natural sources. Pyrethrins, for
example, are insecticides derived from chrysanthemum flowers (Hodosan et al.,
2023). Other pesticides are synthetic chemicals developed to target specific
biological processes (Khan et al., 2023). Whether a pesticide is natural or
synthetic does not by itself determine its safety. All pesticides can
contribute to toxicity.
A Brief History of Pesticides
Humans
have used pesticides for thousands of years. Ancient civilizations used
substances such as sulfur and plant extracts to protect crops and stored food
(Nwankwo & David, 2025). Later, compounds containing arsenic, copper,
mercury, and nicotine were used for pest control (Jayaprakas et al., 2023). During
the nineteenth and twentieth centuries, advances in chemistry led to
increasingly powerful synthetic pesticides. The discovery of
insecticidal properties of DDT in 1939 marked an important development in
modern pest control (Cardon et al., 2026). Many of the pesticides that were not
effective found other uses such as in war or as crowd control measures (Claar
et al., 2022). Organophosphates, carbamates, pyrethroids, and other pesticide
classes subsequently became widely used in places like home gardens and other
argricultural settings (Jayaprakas et al., 2023). This history illustrates an
important environmental-health principle: natural does not automatically
mean safe, and synthetic does not automatically mean dangerous. Toxicity
depends on the substance, dose, route of exposure, duration, and other factors
(Gupta et al., 2022).
Pesticides and the Nervous System
Some
pesticides affect the nervous system by interfering with chemical signaling
(Rodriguez et al., 2025). For example, organophosphate pesticides can
inhibit acetylcholinesterase (AChE), an enzyme that normally breaks down the
neurotransmitter acetylcholine (Aroniadou-Anderjaska et al., 2023). When AChE
is inhibited, acetylcholine can accumulate and cause excessive cholinergic
signaling (Aroniadou-Anderjaska et al., 2023). Here are some examples of these concepts.
Malathion is an organophosphate insecticide that inhibits AChE
(Aroniadou-Anderjaska et al., 2023). Carbaryl is a carbamate insecticide
that also inhibits AChE, although its interaction with the enzyme differs from
that of organophosphates (Voris et al., 2024). These examples demonstrate why
pesticide toxicity depends on the specific chemical and its biological
mechanism, not simply on the fact that it is a pesticide.
Pesticides and Chemical-Weapons Research
Figure 2. Gerhard Schrader, German
Pesticide
chemistry also has a historical connection to chemical-weapons research. In the
1930s, German chemist Gerhard Schrader was researching organophosphorus
insecticides when his work led to the discovery of highly toxic compounds,
including tabun (GA) in 1936 and sarin (GB) in 1938
(Valenzuela-Tapia et al., 2025). These compounds were not simply agricultural
pesticides that were repurposed as weapons (Valenzuela-Tapia et al., 2025).
Rather, research into potent organophosphorus chemistry led to compounds whose
extreme toxicity made them suitable for chemical warfare. Other agents such as
a collection of gases known as tear gases also require discussion.
The
modern history of tear gas began before World War I, when ethyl bromoacetate
was used by French police in 1912; after the war began, the French Army used
rifle grenades containing the irritant against German forces beginning in August
1914 (Raue, 2024). These early grenades lacrymogènes (tear gas grenades)
were largely ineffective in open battlefield conditions because they delivered
too little agent, despite ethyl bromoacetate being highly toxic (Honeyman et
al., 2025). During the early months of the war, British forces also
investigated or used chemical irritants, including sulfur dioxide,
although the historical record distinguishes these early experiments from the
large-scale chemical warfare that followed (Honeyman et al., 2025). Germany
subsequently employed other irritant agents, while the introduction of chlorine
at Ypres in April 1915 marked the beginning of effective large-scale chemical
warfare (Honeyman et al., 2025). Modern tear gas, named more precisely as riot-control
agents such as 2-chlorobenzalmalononitrile (CS) and related compounds,
is used primarily by law-enforcement agencies for crowd control and by
militaries for certain training and security applications; exposure produces
irritation of the eyes, skin, and respiratory tract and can cause serious
injury under sufficiently intense or prolonged exposure (Econdi et al., 2025). This
history illustrates the importance of understanding how chemicals interact with
biological systems.
Figure 3. Tear gas being deployed by
How Can People Be Exposed?
Using a
pesticide does not automatically mean that someone will become sick.
Risk depends on the chemical, dose,
route, and duration of exposure (Tudi et al., 2022). People can
potentially be exposed by breathing contaminated air or dust, getting
pesticides on the skin or in the eyes, accidentally swallowing them, touching
recently treated surfaces, or bringing contaminated soil or dust indoors (Sahoo
et al., 2022). Children and pets may have additional exposure opportunities
because they frequently contact floors and other surfaces (Negev et al., 2022).
The goal of any alternative to pesticides is therefore not to eliminate every
possible pesticide exposure, but to reduce unnecessary exposure while maintaining
effective pest control.
Integrated Pest Management (IPM)
Integrated pest management (IPM) is a strategy for controlling pests
while minimizing unnecessary pesticide use (Angon et al., 2023). The basic
approach is to identify, monitor, prevent, control, and evaluate (Angon et al.,
2023). First, identify the pest because different pests require different solutions,
and seeing one insect does not necessarily mean that treatment is needed (Angon
et al., 2023). Next, look for ways to prevent the problem. Pests often need food,
water, shelter, and access, so removing these resources can make a home
less attractive to them (Angon et al., 2023). Prevention may include storing
food in sealed containers, cleaning crumbs and spills, fixing leaks, removing
standing water, sealing cracks and openings, installing screens and door
sweeps, and keeping outdoor areas free of conditions that attract pests (Angon
et al., 2023). If prevention is not enough, physical or mechanical controls can
sometimes be used (Angon et al., 2023).
If
You Need to Use a Pesticide
Sometimes
pesticides are necessary. When using pesticides, follow the product label
exactly (Barwant et al., 2025). The label specifies where and how the product
may be used, how much should be applied, and what precautions are necessary.
Use pesticides only for their labeled purpose and only in the amount directed. Do not mix
products unless the label specifically permits it, and keep pesticides in their
original containers away from children and pets (Mohafrash & Mossa, 2024).
Follow instructions concerning ventilation and reentry,
wash your hands after handling pesticides, and store and dispose of pesticides
according to the label and applicable local requirements (Mondal & Nag,
2022). More pesticide does not mean better pest control; using excessive
amounts can increase opportunities for exposure without improving effectiveness
(Munoz-Junior et al., 2023).
What About Foggers?
Total-release
foggers, sometimes called bug bombs, release pesticide throughout an
enclosed space (Luckyjane et al., 2023). When used incorrectly, they can create
unnecessary exposure and may not address the underlying cause of an infestation
(Norton, 2024). For example, if insects are entering through cracks, treating
an entire room does not eliminate the entry point. A targeted approach may
therefore be more appropriate. Precautions for use are generally the same as other
pesticide products.
What You Can Do Today
Start
by identifying the pest before treating it. Seal cracks and other entry points,
store food in closed containers, clean up crumbs and spills, fix leaks, reduce
excess moisture, and remove standing water. Try physical or mechanical controls
before resorting to widespread pesticide use. If a pesticide is necessary, read
the label before using it, use only the amount directed, and keep the product
away from children and pets. Good pest management does not require choosing
between effective control and environmental health. IPM provides a way to
manage pests while reducing unnecessary pesticide use and exposure.
References
Adomaitis, M., Skujienė, G., &
Račinskas, P. (2022). Reducing the application rate of molluscicide pellets for
the invasive Spanish slug, Arion vulgaris. Insects, 13(3), 301.
https://doi.org/10.3390/insects13030301
Angon, P. B., Mondal, S., Jahan,
I., Datto, M., Antu, U. B., Ayshi, F. J., & Islam, Md. S. (2023).
Integrated Pest Management (IPM) in agriculture and its role in maintaining
ecological balance and biodiversity. Advances in Agriculture, 2023,
1–19. https://doi.org/10.1155/2023/5546373
Aroniadou-Anderjaska, V.,
Figueiredo, T. H., de Araujo Furtado, M., Pidoplichko, V. I., & Braga, M.
F. M. (2023). Mechanisms of organophosphate toxicity and the role of
acetylcholinesterase inhibition. Toxics, 11(10), 866.
https://doi.org/10.3390/toxics11100866
Barwant, M. M., Ogidi, O. I.,
Yogita, C., & Munje, R. (2025). Study of consumers choices on pesticides
use and sustainability. In The interplay of pesticides and climate change:
environmental dynamics and challenges (pp. 469-516). Cham: Springer Nature
Switzerland.
Blažić, T., Stojnić, B., Milanović, S., & Jokić, G. (2024). A
strategy to improve rodent control while reducing rodenticide release into the
environment. Heliyon, 10(8), e29471.
https://doi.org/10.1016/j.heliyon.2024.e29471
Cardon, V., Levain, A.,
Pellissier, F., Dedieu, F., Joly, P. B., & Barbier, M. (2026). Continuous
discontinuation: the DDT ban as a framework for the perpetuation of pesticides
use. Environmental sociology, 12(1), 143-154.
Claar, M., & Kovačević, D. (2022). Nowhere to hide: the use of
chemical agents during the Vietnam War. The Nonproliferation Review, 29(4-6),
219-242.
Daraban, G. M., Hlihor, R.-M., & Suteu, D. (2023). Pesticides
vs. biopesticides: From pest management to toxicity and impacts on the
environment and human health. Toxics, 11(12), 983.
https://doi.org/10.3390/toxics11120983
Econdi, S., Marchesi, S., Bisio,
C., & Guidotti, M. (2025). Dual-use chemicals. Information Systems
Engineering and Management, 63–109.
https://doi.org/10.1007/978-3-032-00202-0_3
Garud, A., Pawar, S., Patil, M.
S., Kale, S. R., & Patil, S. (2024). A scientific review of pesticides:
Classification, toxicity, health effects, sustainability, and environmental
impact. Cureus. https://doi.org/10.7759/cureus.67945
Gul, H., Gadratagi, B. G., Güncan,
A., Tyagi, S., Ullah, F., Desneux, N., & Liu, X. (2023). Fitness costs of
resistance to insecticides in insects. Frontiers in Physiology, 14.
https://doi.org/10.3389/fphys.2023.1238111
Gupta, R., Rajpoot, K., Tekade,
M., Sharma, M. C., Safavi, M., & Tekade, R. K. (2022). Factors influencing
drug toxicity. In Pharmacokinetics and Toxicokinetic Considerations (pp.
27-50). Academic Press.
Hodoșan, C., Gîrd, C. E., Ghica, M. V., Dinu-Pîrvu, C.-E., Nistor,
L., Bărbuică, I. S., Marin, Ș.-C., Alexandru Mihalache, & Popa, L. (2023).
Pyrethrins and pyrethroids: A comprehensive review of natural occurring
compounds and their synthetic derivatives. Plants, 12(23),
4022–4022. https://doi.org/10.3390/plants12234022
Honeyman, D. A., Heslop, D. J.,
Lim, S., & MacIntyre, C. R. (2025). Chemical warfare through the ages: A
systematic review from antiquity to the present. Journal of Toxicology, 2025(1).
https://doi.org/10.1155/jt/7363632
Islam, T., Danishuddin, Tamanna,
N. T., Matin, M. N., Barai, H. R., & Haque, M. A. (2024). Resistance
mechanisms of plant pathogenic fungi to fungicide, environmental impacts of
fungicides, and sustainable solutions. Plants, 13(19), 2737.
https://doi.org/10.3390/plants13192737
Jayaprakas, C. A., Tom, J., &
Sreejith, S. (2023). Impact of insecticides on man and environment. Biomedical
Applications and Toxicity of Nanomaterials, 751–768.
https://doi.org/10.1007/978-981-19-7834-0_28
Khan, B. A., Nadeem, M. A., Nawaz,
H., Amin, M. M., Abbasi, G. H., Nadeem, M., Ali, M., Ameen, M., Javaid, M. M.,
Maqbool, R., Ikram, M., & Ayub, M. A. (2023). Pesticides: Impacts on agriculture
productivity, environment, and management strategies. Springer eBooks,
109–134. https://doi.org/10.1007/978-3-031-22269-6_5
Mohafrash, S. M., & Mossa, A.
T. H. (2024). Disposal of expired empty containers and waste from pesticides.
Egyptian Journal of Chemistry, 67(4), 65-85.
Mondal, T.,
& Nag, P. K. (2022). Guidance on Pesticides Handling in Farming. In
Agrochemicals in Soil and Environment: Impacts and Remediation (pp. 143-155).
Singapore: Springer Nature Singapore.
Muniz-Junior,
G., de Oliveira Roque, F., Pires, A. P., & Guariento, R. D. (2023). Are
lower pesticide doses better? An evolutionary perspective on integrated pest
management. Ecological Modelling, 482, 110408.
Negev, M.,
Barnett-Itzhaki, Z., Berman, T., Reicher, S., Cohen, N., Ardi, R., ... &
Diamond, M. L. (2022). Hazardous chemicals in outdoor and indoor surfaces:
artificial turf and laminate flooring. Journal of Exposure Science &
Environmental Epidemiology, 32(3), 392-399.
Norton, S. A. (2024). Concerns for Infestation (CI): Dermatologic
Evaluation of Patients with Unwanted, Uncomfortable, and Unexplained
Sensations. In The Physician's Guide to Delusional Infestation (pp. 173-225).
Cham: Springer International Publishing.
Nwankwo, N. E., & David, J. C. (2025). A review of
sulfur-containing compounds of natural origin with insights into their
pharmacological and toxicological impacts. Discover Chemistry, 2(1).
https://doi.org/10.1007/s44371-025-00286-w
Ofosu, R., Agyemang, E. D.,
Márton, A., Pásztor, G., Taller, J., & Kazinczi, G. (2023). Herbicide
resistance: Managing weeds in a changing world. Agronomy, 13(6),
1595. https://doi.org/10.3390/agronomy13061595
Raue, T. (2024). The Technology of
Control—A Guide to “Less Lethal” Police Weaponry. Towards Anti-policing:
Prefiguring Possibilities beyond the Thin Blue Line, 123.
Rodríguez, A., Castrejón-Godínez, M. L., &
Monterrosas-Brisson, N. (2025). Pesticides: Environmental stressors implicated
in the development of central nervous system disorders and neurodegeneration. Stresses,
5(2), 31. https://doi.org/10.3390/stresses5020031
Sahoo, G., Majid, W. A., Laxmana,
S. S., Rout, S., & Gupta, S. (2022). Indoor pollution and human health. AIP
Conference Proceedings, 2385(1). https://doi.org/10.1063/5.0070902
Tudi, M., Li, H., Li, H., Wang,
L., Lyu, J., Yang, L., Tong, S., Yu, Q. J., Ruan, H. D., Atabila, A., Phung, D.
T., Sadler, R., & Connell, D. (2022). Exposure routes and health risks
associated with pesticide application. Toxics, 10(6), 335.
https://doi.org/10.3390/toxics10060335
Valenzuela-Tapia, L. N., Quintul,
C. A., Rubio-Concha, N. D, Toledo-Ríos, L., Salas-Kuscevic, C., Leisewitz, A.
V., Cámpora-Oñate, P., & Campanini-Salinas, J. (2025). The blurred lines
between new psychoactive substances and potential chemical weapons. Toxics,
13(8), 659–659. https://doi.org/10.3390/toxics13080659
Voris, D., Cavalcante, S., Borges,
C., & Lima, A. (2024). Carbamates: Are they “good” or “bad guys?” Journal
of the Brazilian Chemical Society, 35(9).
https://doi.org/10.21577/0103-5053.20240058




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