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What is a pesticide half-life?
A half-life is the time it takes for a certain amount of a pesticide to be reduced by half. This occurs as it
dissipates or breaks
down in the environment. In general, a pesticide will break down to 50% of the original amount after
a
single half-life.
After two half-lives, 25% will remain. About 12% will remain after three half-lives. This continues until
the
amount remaining
is nearly zero. See Figure 1.
Figure 1. Approximate amount of pesticide (shaded area) remaining at the application site over time.
(photo credit: National Pesticide Information Center)
To keep your risk low in your own home, you may consider:
Each pesticide can have many half-lives depending on conditions in
the environment. For example, permethrin
breaks
down at different speeds in soil, in water, on plants, and in homes.
In soil, the half-life of permethrin is about 40 days, ranging from 11-113 days.
In the water column, the half-life of permethrin is 19-27 hours. If it sticks to sediment, it can
last over
a year.
On plant surfaces, the half-life of permethrin ranges from 1-3 weeks, depending on the plant
species.
Indoors, the half-life of permethrin can be highly variable. It is expected to be over, or well
over, 20
days.
Why is a pesticide's environmental half-life important?
The half-life can help estimate whether or not a pesticide tends to build up in the environment.
Pesticide
half-lives can
be lumped into three groups in order to estimate persistence. These are low (less than 16 day
half-life),
moderate (16
to 59 days), and high (over 60 days). Pesticides with shorter half-lives tend to build up less because
they are
much less
likely to persist in the environment. In contrast, pesticides with longer half-lives are more likely to
build up
after repeated
applications. This may increase the risk of contaminating nearby surface water, ground water, plants,
and
animals.
However, pesticides with very short half-lives can have their drawbacks. For example, imagine that a
pesticide is
needed to
control aphids in
the garden for several weeks. One
application of a pesticide
with a half-life of a few hours will probably
not be very effective several weeks out. This is because the product would have broken down to near-zero
amounts
after
only a few days. This type of product would likely have to be applied multiple times over those several
weeks.
This could
increase the risk of exposure to people, non-target animals, and plants.
What can influence a pesticide's environmental half-life?
Many things play a role in how long a pesticide remains in the environment. These include things like
sunlight,
temperature,
the presence of oxygen, soil type (sand, clay, etc.), how acidic the soil or water is, and microbe
activity.
See Table 1.
Pesticide half-lives are commonly reported as time ranges. This is because environmental conditions can
change
over time.
This makes it impossible to describe a single, consistent half-life for a pesticide.
A pesticide product's formulation can also change how the active ingredient behaves in the environment.
In fact,
the
properties of the formulation may dominate initially, until enough time has passed to allow the
ingredients to
separate
This is because small amounts of an active ingredient are 'formulated'
with
larger amounts of 'other' ingredients to make a
whole pesticide
product.
Table 1. Environmental factors that affect pesticide
persistence.4
Environmental Factors
Role in Chemical Degradation
Sunlight
Radiation from the sun breaks certain chemical bonds, creating break down products.
Microbes
Bacteria and fungi can break down chemicals, creating biodegradation products.
Plant / Animal Metabolism
Plants and animals can change chemicals into forms that dissolve better in water
(metabolites). This makes removal from the body easier.
Water
Water breaks chemicals apart to make pieces that dissolve better in water (hydrolysis). This
is typically a very slow process.
Dissociation
Chemicals can break apart into smaller pieces (dissociation products).
Sorption
Chemicals that stick tightly to particles can become inaccessible and/or move away with
those particles.
Bioaccumulation
Some chemicals can be absorbed by plants/animals from the soil, water, food, and
air. When the plant/animal is exposed again before it can remove the chemical(s),
accumulation can occur.
How is a pesticide's half-life determined?
Pesticide half-lives are often determined in a laboratory. There, conditions like temperature can be
controlled
and closely
monitored. Soil, water, or plant material is mixed with a known amount of a pesticide. The material is
then
sampled and
tested over time to determine how long it takes for half of the chemical to break down.
Field studies are also performed for some chemicals. A known amount of the pesticide is mixed with soil,
water,
or plant
material. It is then placed in an outdoor environment where it is exposed to various environmental
conditions
and tested
over time. Field studies provide researchers with a more realistic idea of how the pesticide will act in
the
environment.
However, half-life values from such studies can vary greatly depending on the exact conditions.
See Figure 2.
Before a pesticide product is registered,
manufacturers measure their
half-lives. You can find their research results in a
variety of databases, books, and
peer-reviewed articles. If you need
help, call the National Pesticide Information Center.
What happens to pesticides after they "go away"?
When a pesticide breaks down it doesn't disappear. Instead, it forms new chemicals that may be more
or
less toxic
than the
original chemical. Generally, they are broken into smaller and smaller pieces until only carbon
dioxide,
water,
and minerals
are left. Microbes often play a large role in this process. In addition, some chemicals may not
break
down
initially. Instead,
they might move away from their original location. It all depends on the chemical and the
environmental
conditions.
Inorganic pesticides like iron phosphate and
copper sulfate
don't break down in the same way as
organic
pesticides.10,12 The
"half-life" concept only applies to organic pesticides, those that contain carbon components.
Figure 2. The soil half-life of five pesticides.8,9,11,13,15
Where can I get more information?
For more detailed information about pesticide half-lives please visit the list of referenced
resources
below or call the National Pesticide Information Center, Monday - Friday,
between 8:00am - 12:00pm Pacific Time (11:00am - 3:00pm Eastern Time) at 1-800-858-7378 or visit us
on the web at http://npic.orst.edu. NPIC
provides objective, science-based
answers to questions about pesticides.
Date Reviewed: May 2015
Please cite as: Hanson, B.; Bond, C.; Buhl, K.; Stone, D. 2015.
Pesticide Half-life Fact Sheet;
National Pesticide Information Center, Oregon State University Extension Services. http://npic.orst.edu/factsheets/half-life.html.
References:
Hornsby, A. G.; Wauchope, R. D.; Herner, A. E. Pesticide Properties in the Environment;
Springer:
New York, 1996, pp 1-3, 7-15.
Mackay, D.; Shiu, W-Y.; Ma, K-C. Physical-Chemical Properties. Illustrated handbook of
physical-chemical properties and
environmental fate for organic chemicals; CRC Press: Boca Raton, FL, 1997, pp 3-9.
Newman, M. C.; Unger, M. A. Environmental Contaminants. Fundamentals of Ecotoxicology, 2nd
ed.;
CRC Press: Boca
Raton, FL, 2002, pp 24-27, 34-35, 42-43.
Ney Jr., R. E. Fate and Transport of Organic Chemicals in the Environment: A Practical
Guide,
2nd
ed.; Government
Institutes, Inc.: Rockville, MD, 1995, Chapters 1-3.
Environmental Persistence. Design for the Environment Program Alternatives Assessment Criteria for
Hazard Evaluation
Version 2.0; U.S. Environmental Protection Agency, Office of Pollution Prevention and
Toxics,
U.S. Government Printing
Office: Washington, DC, 2011, Chapter 4, Table 12.
Ingredient Statement. Label Review Manual; U.S. Environmental Protection Agency, Office of
Prevention, Pesticides and
Toxic Substances, Office of Pesticide Programs, U.S. Government Printing Office: Washington, DC, 2012,
Chapter 5.
Data Requirements for Pesticides, Product Chemistry. Code of Federal Regulations, Part
158,
Title
40, 2015.
Gervais, J. A.; Luukinen, B.; Buhl, K.; Stone, D. 2008. 2,4-D Technical Fact Sheet;
National
Pesticide Information Center,
Oregon State University Extension Services. http://npic.orst.edu/factsheets/2,4-DTech.html.
Gervais, J. A.; Luukinen, B.; Buhl, K.; Stone, D. 2008. Capsaicin Technical Fact Sheet;
National
Pesticide
Information Center, Oregon State University Extension Services.
http://npic.orst.edu/factsheets/Capsaicintech.html.
Boone, C.; Jervais, G.; Luukinen, B.; Buhl, K.; Stone, D. 2012. Copper Sulfate Technical Fact
Sheet;
National Pesticide Information Center, Oregon State University Extension Services.
http://npic.orst.edu/factsheets/cuso4tech.html.
Bunch, T. R; Gervais, J. A.; Buhl, K.; Stone, D. 2012. Dicamba Technical Fact Sheet;
National
Pesticide
Information Center, Oregon State University Extension Services.
http://npic.orst.edu/factsheets/dicamba_tech.html.
Buhl, K.; Bond, C.; Stone, D. 2013. Iron Phosphate General Fact Sheet; National Pesticide
Information Center, Oregon State University Extension Services.
http://npic.orst.edu/factsheets/ironphosphategen.html.
Wick, K.; Bond, C.; Buhl, K.; Stone, D. 2012. Methoprene General Fact Sheet; National
Pesticide
Information Center, Oregon State University Extension Services.
http://npic.orst.edu/factsheets/methogen.html.
Toynton, K.; Luukinen, B.; Buhl, K.; Stone, D. 2009. Permethrin Technical Fact Sheet;
National
Pesticide Information Center,
Oregon State University Extension Services. http://npic.orst.edu/factsheets/Permtech.html.
Bond, C.; Buhl, K.; Stone, D. 2014. Pyrethrins General Fact Sheet; National Pesticide
Information
Center, Oregon State
University Extension Services. http://npic.orst.edu/factsheets/pyrethrins.html.
NPIC fact sheets are designed to answer questions
that
are
commonly
asked by the general public about pesticides that are regulated by the
U.S. Environmental Protection Agency (US EPA). This document is
intended to be educational in nature and helpful to consumers for
making decisions about pesticide use.