In years following extended drought, several agronomic issues often arise, including that of potential herbicide carryover. This article discusses herbicide degradation in soils, how it is affected by droughty conditions, and the primary pathways by which some specific herbicide chemistries degrade. This information is helpful to growers who need to diagnose herbicide carryover issues.
1. Degradation of Herbicides
under Dry Conditions
Stephen Strachan and Kevin Hahn
Herbicide Product Support and Renewal and Field Development
2. Introduction
• Much of the Midwest encountered severe drought
throughout the summer of 2012.
• In years following extended
drought, several agronomic
issues often arise, including
that of potential herbicide
carryover.
• Herbicides break down
through microbial and/or
chemical degradation in the Corn grown in 2012 exhibiting
presence of soil moisture. severe drought symptoms.
• When soils are very dry, herbicide breakdown via
microbiological activity is diminished.
3. Introduction
• This presentation will help growers who suspect and need to
diagnose herbicide carryover issues arising from the severe
drought conditions of 2012 by addressing:
– herbicide degradation in soils,
– how it is affected by droughty conditions, and the
– primary pathways by which some specific herbicide chemistries
degrade.
• To understand herbicide degradation in dry soils, it is
important to understand
– how drought affects soil water and microbiological activity,
– herbicide degradation pathways, and
– the interaction between microorganisms and herbicides.
4. Characteristics of Water in Soil
Macropore
Micropores
Water of
Adhesion
(gray shaded area
around each soil
Saturated Soil colloid)
Macropores filled with air Soil Under Drought Conditions
Micropores filled with water Water still present only in the
smallest micropores and as a film
Thin film of water (water of adhesion) around the soil colloids
surrounds each soil colloid
5. Characteristics of Microorganisms in Soil
Microorganisms
(red dots)
•Require water
to survive
•Reduce
populations
as soil water
content decreases
•Are relatively large
(a few microns in
length) and require
Saturated Soil small pools of water Soil Under Drought
for maximum activity Conditions
6. Characteristics of Herbicides in Soil
Herbicides
(green dots)
• Exist as single
molecules (a few
angstroms in length)
• Tend to accumulate
in the film of soil
water next to the
soil colloids
• Some percent of
molecules remain
in the water held
Saturated Soil in micropores Soil Under Drought
• Herbicide molecules Conditions
move between the
two water phases
7. Microbial Degradation of Herbicides in Moist Soil
• Microbes must either ingest or be closely
associated with herbicide molecules for
herbicide degradation to occur
• Microbes are relatively large and require
ample water and space to live
• Micropores filled with water best support
microbial growth
• Herbicide molecules move from the
water film on the soil colloid into the
micropores as microbes degrade
molecules in the micropores
Saturated Soil
8. Rate of Microbial Degradation of
Herbicides Decreases in Drier Soils
•Less available water to support
microbial populations (fewer micro-
organisms present to degrade
herbicide molecules)
•Microorganisms are about 10,000
times larger than herbicide molecules
and cannot enter all locations in the
film of water where the herbicide
molecules are located (limited
access to the herbicide molecules)
Soil Under Drought
Conditions
9. Chemical Degradation of Herbicides in Moist Soil
• Chemical degradation can occur
wherever water is present in the soil
• Herbicide molecules associated
with the thin film of water near the
soil colloids and in water contained in
soil micropores are susceptible to
chemical degradation
Saturated Soil
10. Chemical Degradation of Herbicides
Continues in Drier Soils
• Even very dry soils contain a thin film
of water surrounding the soil colloids
• Herbicide molecules are either attached
to soil colloids or located in the thin film
of water surrounding the soil colloids
and are susceptible to chemical attack
• As long as water is present, chemical
degradation continues to occur
•Rate of chemical degradation may increase
because drier soils tend to have higher
temperatures (rates of chemical reactions
increase as the temperature increases) Soil Under Drought
Conditions
11. Degradation Pathways of Herbicides*
Typically based on chemical class (not Mode of Action)
Combination of Chemical
Primarily Microbial Activity
and Microbial Activity
References:
Atrazine 1 Isoxaflutole Herbicide
Handbook, Weed
Flumetsulam Pyroxasulfone
Science Society of
Flumioxazin America, 9th
Saflufenacil
- Not persistent edition, 2007, and
Fomesafen Simazine 2 EPA-published
documents.
Imidazolinones Sulfonylureas
1 Greater concern
Mesotrione Chlorimuron ethyl if followed by
Metolachlor metribuzin ahead
Rimsulfuron of soybeans.
- Safe to most crops
2 HighpH:
Metribuzin Tribenuron
microbial only.
Sulfentrazone Thiencarbazone
Low pH: chemical
Flumetsulam and microbial.
Flumioxazin
Notas del editor
Much of the Midwest encountered severe drought throughout the summer of 2012. In years following extended drought, several agronomic issues often arise, including that of potential herbicide carryover. Herbicides break down through microbial and/or chemical degradation in the presence of soil moisture. When soils are very dry, herbicide breakdown via microbiological activity is diminished. This article discusses herbicide degradation in soils, how it is affected by droughty conditions, and the primary pathways by which some specific herbicide chemistries degrade. This information should be helpful to growers who suspect and need to diagnose herbicide carryover issues arising from the severe drought conditions of 2012.
Much of the Midwest encountered severe drought throughout the summer of 2012. In years following extended drought, several agronomic issues often arise, including that of potential herbicide carryover. Herbicides break down through microbial and/or chemical degradation in the presence of soil moisture. When soils are very dry, herbicide breakdown via microbiological activity is diminished. This article discusses herbicide degradation in soils, how it is affected by droughty conditions, and the primary pathways by which some specific herbicide chemistries degrade. This information should be helpful to growers who suspect and need to diagnose herbicide carryover issues arising from the severe drought conditions of 2012.
This table contains a few examples of how some of the more common herbicides degrade in soil. Note that the chemical class is more important than the mode of action in determining primary pathways for herbicide degradation. As an example, imidazolinone and sulfonylurea herbicides both affect the ALS binding site. However, imidazolinone herbicides degrade primarily via microbiological degradation, whereas sulfonylurea herbicides (e.g., chlorimuron ethyl, rimsulfuron, and tribenuron) degrade via both microbiological and chemical pathways.Many of the active ingredients listed in this table have been used for many years. These herbicides have been applied during drought years (e.g., 1988) and in very wet years (e.g., 1993). Product labels commonly have a “safety buffer” built into the label guidelines. If there is a concern about planting a sensitive crop into soil that was treated with a herbicide that degrades via only microbial activity, carefully check the “following crop” or “rotational crop” portion of the label guidelines, and plant the crop according to these guidelines.