Posts in Herbicides
Understanding herbicides for vineyard weed control

Australian wine is well known for its quality and reliability and the Australian wine industry are world leaders in innovation and quality control. The maintenance of its reputation increases pressure on the vineyard managers to stay well within the allowed limits for the use of pesticides. As such weed control in vineyards becomes relatively complicated with a limited range of herbicides being used.

Current management strategies have led to increasing levels of herbicide resistance and incidence of hard-to-kill-weeds.

Glyphosate resistant annual ryegrass in vine row

Glyphosate resistant annual ryegrass in vine row

Adding to the limited number of herbicides that are acceptable, under-vine spraying is often left until spring when weeds are large with healthy root systems. Good spray coverage then becomes difficult. Adding issues with sprayer setup then leads to highly variable weed control.

Another complication with wine grape production is the encroachment of suburbia as towns expand and get closer to areas of agricultural production. Residential developments in wine growing areas are also popular, with a mandatory golf course attached. This increases the pressure on Vineyard managers to reduce the risks of pesticides going where they should not.

Close proximity of houses limits vine management options

Close proximity of houses limits vine management options

To put all this in perspective wine grape growers have their fungicide applications well sorted which is understandable because fungal disease has the greatest effect on grape yield and fruit quality in wine grapes. Weeds on the other hand have a much smaller effect on the production of high-quality grapes.

Important factors in high levels of weed control are understanding how different herbicide modes of action work which then determines how they need to be applied to optimise their effectiveness. The questions we need to ask are:

  • What kind of target are we aiming at?

  • What kind of droplets are most appropriate to hit this target?

  • What does the product do once it deposits on the target?

Source: SyngentaTable 1  the number of spray droplets per square centimetre and per cent area coverage for different pesticide types.

Source: Syngenta

Table 1 the number of spray droplets per square centimetre and per cent area coverage for different pesticide types.

The per cent area coverage is most easily measured using water sensitive paper and the SnapCard® app.

To check what pesticides can be used in wine grape production get the Australian Wine research Institute “Agrochemicals registered for use in Australian viticulture” or commonly known as “the dog book” which is also available as app. https://www.awri.com.au/industry_support/viticulture/agrochemicals/agrochemical_booklet/

 Knockdown herbicides that are permitted for use in wine grape production are listed in Table 2. This table shows the behaviours of the different herbicide modes of action. Glyphosate is highly translocated and therefore very forgiving in application technique whereas paraquat is the opposite. Products like paraquat that are translocated need much higher levels of coverage therefore product rate and application volume are critical for high levels of weed control.

Seedling grasses smaller than 3 leaf make a challenging target so it is important to keep the application volume up to ensure there are enough droplets to hit the target.

Table 2 Knockdown / Non-selective herbicides

Table 2 Knockdown / Non-selective herbicides

A small number of selective herbicides are allowed and often used in the inter row area. Most of these herbicides are poorly translocated and also need good coverage to be effective.

Table 3 Selective herbicides

Table 3 Selective herbicides

Soil active (residual) herbicides (Table 4) have a set of characteristics which must be understood the get optimum weed control. For example they work poorly if the soil is dry. Sufficient soil moisture is needed to allow the weeds to absorb the herbicide from the soil water. Also due they work poorly or not at all on emerged plants so need to be applied to bare ground or tank-mixed with a compatible knockdown herbicide. Some managers tend to minimise the use of residuals for these reasons and because there is often a lot of dead plant material under the vine row which will intercept the herbicide.

Table 4 Soil active herbicides

Table 4 Soil active herbicides

Lower levels of trash under the vines opens options for using soil active herbicides

Lower levels of trash under the vines opens options for using soil active herbicides

Because of the limited number of herbicides available for use in vineyards and the increase in herbicide resistance it is essential for vineyard managers to understand the characteristics of these herbicides when developing their weed management plans.

Is it safe to plant that next crop? Testing for Damaging Herbicide Residues

With the growing resistance to post emergent herbicides in many weed populations the message going to farmers is that they need to use more pre-emergent herbicides in their farming system.

The problem with pre-emergent herbicides is that they are dependent on activation by soil moisture. Droughts and increasingly variable rainfall patterns can result in insufficient soil moisture to activate the herbicide which leads to poor weed control. The other concern is that herbicides remain active in the soil because they have not been broken down by bacterial activity or hydrolysis.

In many parts of the country, the 2018 winter crop season saw large areas of crop damaged by soil herbicide residues, due to the dry conditions between spraying in 2017 and crop emergence in 2018.

Sulfonylurea residues suppressing chickpea growth (right) compared with plant from area of paddock with no residues. Plants are the same age. Image: AGRONOMO

Sulfonylurea residues suppressing chickpea growth (right) compared with plant from area of paddock with no residues. Plants are the same age. Image: AGRONOMO


The level of herbicide remaining in the soil will be determined by:

  • initial application rate and herbicide type

  • soil pH - most herbicides last longer in alkaline soils while Group B imidazolinones become more water soluble and can move down the soil profile

  • the amount of rainfall received between application and sowing

  • soil temperature - warm, damp soil speeds herbicide breakdown

  • soil texture, that is, the proportion of clay to sand and silt - sandy soils are more likely to have herbicide damage problems than clay soils

  • amount of cultivation - cultivation usually speeds herbicide loss and can dilute it by soil mixing

  • crop type and variety

  • soil organic matter content - high soil organic matter levels reduce the effect of soil active herbicides. However most Australian soils are classed as low in organic matter

  • microbial activity for some herbicides - most of the above factors affect microbial activity

As can be seen from the factors which affect herbicide persistence in the soil, and many of these are out of the farmer’s control.

Most labels will give crop plant back periods based on the amount of rain received since application, soil characteristics and herbicide rate. If you are on the borderline for these characteristics can you safely sow the next crop?

HOW TO DETERMINE IF RESIDUES ARE PRESENT

 1. Susceptible weeds damaged or dying

If there are weeds susceptible to the herbicide present and they show no damage symptoms, it is likely there are no damaging herbicide residues.

However, care must be taken to check whether the particular weeds have not germinated from below or above the possible herbicide band. This prevents weeds absorbing the herbicide.

If it hasn’t rained, you will be none the wiser.

2. Laboratory testing

Laboratory soil testing will cost approximately over $400 per herbicide group and the herbicides to be tested must be specified. The technique most often used is the Gas-Liquid Mass Spectrometer.

Laboratory testing can tell how much herbicide is remaining, but how this relates to crop sensitivity under different conditions can be difficult to interpret.

3. Pot Test (Bioassay)

The simple pot test outlined here does not give an exact measure of the amount of residue present but does indicate whether there is enough herbicide remaining to damage sensitive crops.

The test will take at least 3-4 weeks to perform, so forward planning is essential if sowing and marketing windows are not to be put at risk.

The ‘pot test’ was developed by the late KP Buchholtz for testing of atrazine residues, however it can be used for most soil active herbicides.

1.      Take samples from several locations around the field. Remember that a test is only as good as the sample collected. Sample enough areas to prevent missing any possible high residue areas such as headlands. It may be useful to take separate samples from areas you suspect of being abnormally high. Take samples to the normal cultivation depth, or to 10 cm in non-cultivated fields. It is advisable to take samples from deeper in the profile as well if you have used a highly water-soluble herbicide. If there are any hard pans or restrictions to water flow down the profile also collect soil samples from above these.
See the University of Hertfordshire Pesticide Properties database for the properties of herbicides in question.
Collect about 5 kg per test.

2.      If samples can’t be tested within two weeks of sampling, freeze them. Allowing samples to get hot can reduce the amount of herbicide residue present.

3.      Air dry samples that are wet by spreading out on a tarp. Cloddy soils should be crushed to produce even, pea-sized clods.

4.      Heavy-textured (clay) soils can be improved by adding an equal quantity of clean sand and then mixing thoroughly when dry.

Pot test using oats as the test species to check for Group C (terbuthylazine) and Group D (propyzamide) residues in 2018 after they were applied to a lupin crop in 2017. Very dry conditions in 2017-18 meant there was sufficient herbicide remaining t…

Pot test using oats as the test species to check for Group C (terbuthylazine) and Group D (propyzamide) residues in 2018 after they were applied to a lupin crop in 2017. Very dry conditions in 2017-18 meant there was sufficient herbicide remaining to damage a cereal crop. Left pot has the carbon added. Image: C. Roche

5.      Add the contents of two capsules (0.5 g) of activated carbon (powdered charcoal) to half the soil or sand-soil, mixing thoroughly. The carbon inactivates (binds) the herbicide. Soil treated with carbon should behave in the same manner as soil which contains no herbicide residues. Activated carbon is readily available from pharmacies.

6.      Partially fill two 1-litre containers with soil, but without the carbon and the two containers with the soil-carbon mix. Plant pots or ice cream and drink containers with drainage holes in the base can be used.

7.      Plant about 15 seeds of the crop in question and a known-sensitive species (see Table 1) in each container and cover the seeds with 1-2 cm of soil and lightly water.

8.      Place the containers in a warm place (20-24 degrees C) where they will get plenty of sunlight. Sunlight is necessary for many herbicide symptoms to develop.

9.      Symptoms should appear within 2-4 weeks of planting. Plants in pots exposed to lower temperatures will take longer to show symptoms.

10.   If there are differences in growth between the soil with carbon and soil without carbon pots, it is advisable to only sow crops tolerant of the herbicide in question or go to a fallow.