Herbicide residues
Herbicides residues
Many herbicides have some level of persistence and have the potential to damage future crops. No matter which product is used most will end up in the soil and may bind to clay particles and organic matter. For this reason heavy clay soils bind more chemical than sandy soils.
Herbicides also differ in how strongly they bind to the soil. Strongly bound chemicals will tend to break down more slowly.
Sandy soils will bind herbicide less strongly and the herbicide present is more available for plant uptake, hence lower rates of residual herbicides such as atrazine are used on sandy soils.
Dry conditions will also slow the breakdown of residual herbicides and may damage future crops.
Breakdown pathways
Microbial breakdown in which the action of soil microbes and fungi deactivate the herbicide. Microbes may use herbicides as a source Nitrogen, Sulphur and/or Carbon. For most products microbial action is the more important breakdown pathway and will occur more quickly under conditions of greater moisture and warm temperatures.
Chemical breakdown through hydrolysis is also an important pathway and involves a reaction with water that deactivates the herbicide. The speed of this reaction is strongly influenced by soil pH.
Other breakdown pathways includes volatilization (the active component evaporates), photolysis (breakdown by sunlight), or leaching further down the soil profile.
The breakdown process varies according to the herbicide group.
Group B
The group B sulfonylurea such as Atlantis®, Ally® undergo breakdown by hydrolysis which slows at higher pH, hence the longer residual action on vertosols (cracking clay soils). The group B Imidazolinones (“imis”) eg Spinnaker® Intervix®, undergo microbial breakdown which is slowed by low pH as the herbicide is more tightly bound at lower pH. Most of these herbicides will leach down the profile which means susceptible crops may not “find” these herbicides until later in the season.
Group C
Breakdown of group C herbicides occurs mostly via microbial action at higher pH and occurs relatively slowly leading to persistence. Persistence may be shorter in paddocks where group triazines have been used previously due to a buildup of microbes responsible for breakdown. At lower pH chemical hydrolysis proceeds more quickly leading to shorter residual action. Simazine has shorter persistence than atrazine.
Group D
Includes trifuralin, these have moderate to high soil binding and are broken down by microbial action and also photo degradation from sunlight if not incorporated. These products are also volatile and can be lost to the atmosphere if not incorporated.
Group H
Isoxaflutole commonly used on chickpea in northern NSW needs to undergo an initial breakdown to produce the active herbicide component. Further microbial break down occurs to degrade the active component and this occurs faster at higher pH, significant plantback periods apply for some crops.
Group I
Some pyridine herbicides belonging to Group I eg Tordon® have significant persistence and the main pathway for breakdown is via microbial action which will be slowed by dry conditions. The active in Tordon® picloram is soluble and may be leached down the profile. Other group I herbicides such as 2,4-D have short persistence but can cause issues when used shortly before sowing without follow up rain.
Group K
Metolachlor (Dual®) has moderate soil binding and does not persist for long periods in the soil, breakdown is mostly by microbial action but some photo degradation may occur if the product is not incorporated.
Avoiding damage from residual herbicides
Herbicide labels may detail plantback periods and a minimum rainfall amount prior to plantback. The length of time that soil remains moist is more important than the total rainfall received. Remember your legal obligation to read and follow the label instructions.
If you are concerned, consider hand sowing a small plot of the intended crop in the paddock several months prior to the main sowing and watch for any signs of herbicide damage. This test can also be carried out in pots. Note that these tests may not reveal residues deeper in the soil profile.
Also take note of weed species emerging or not emerging in the paddock as this may indicate herbicides that are still active.
Herbicide resistant crops can be used if residues are suspected. Avoid using the same herbicide group on these crops as this may increase residue levels further.
Laboratory analysis of soil is relatively expensive and may not be available for particular herbicides and may not detect those applied at very low rates such as some Group B chemicals.
Good spray application records (which are a legal requirement) will help plan rotations and avoid residues.
Contact Local Land Services NSW
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