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By Saskatchewan Pulse Growers (SPG), Saskatchewan Canola Development Commission (SaskCanola), and Saskatchewan Wheat Development Commission (SaskWheat)

Drought Conditions Increase Herbicide Carryover Risk

Figure 1. Herbicide Degredation Curve
Source: Adapted from Persistence of Herbicides in Soil. Penn State University

Herbicide carryover becomes a concern after dry conditions because soil moisture largely dictates the rate of soil residual herbicide breakdown due to its influence on two of the major degradation mechanisms: microbial activity and chemical hydrolysis. Although soil parameters such as pH and organic matter can also influence degradation pathways, soil moisture is often the dominant factor. Soil microbes are most active in moist soils (50-100% field capacity) so a decrease in microbial activity in response to dry soil conditions reduces the amount of herbicide degradation that would typically be expected in the same time frame. Degradation through hydrolysis is also highly influenced by soil moisture as water breaks down herbicides by dividing the larger molecules into smaller, less active pieces.

The effect of drought conditions on soil temperature also influences the rate of herbicide degradation via microbial activity and chemical hydrolysis. Microbial activity is also dependent on soil temperature. It generally increases in warmer soils (up to 30°C) and decreases in cold soils (below 10°C). Therefore, in-season (June 1 to August 31) accumulation of precipitation is often used to inform risk assessments of herbicide carryover and guide recropping restrictions as the bulk of degradation through microbial activity will happen during these months with anticipated drop-off once soils cool down in September and into the fall.

Figure 2. Effect of temperature on herbicide breakdown1
Source: Adapted from Persistence of Herbicides in Soil. Penn State University.
1 Cessna, A. J., Knight, J. D., Ngombe, D., and Wolf T. M. (2017). Effect of temperature on the dissipation of seven herbicides in a biobed matrix. Canadian Journal of Soil Science
“Soil microbes thrive in warm, moist soils, which results in faster degradation. It is estimated that there is a two to three-fold increase in chemical half-life with a 10°C decrease in temperature and a one and one-half to two-fold increase in chemical half-life if soil moisture content is reduced by a factor of two.”
— Eric Johnson, University of Saskatchewan, Factors Affecting Herbicide Residue: Impact of a dry year

Herbicide degradation via chemical hydrolysis will also occur more slowly at lower soil temperatures but continues to increase linearly with soil temperature, even past a point of inhibition to microbial activity. Although microbial degradation is often the greatest contributor to herbicide breakdown, chemical hydrolysis may partially compensate for lower amounts of microbial activity during a drought where soil temperatures may be high.

Drought conditions may also influence the soil solution concentration and favour a temporal increase in the concentration of H+ ions in the soil solution (i.e. a decrease in pH). Depending on the specific herbicide’s ability to persist under a given pH range, this effect may increase or decrease the degree of herbicide degradation via chemical hydrolysis. Increased levels of degradation via photolysis pathways may also occur under drought conditions through increased temperatures (indirect photolysis) or increased sunlight exposure (direct photolysis). It is important to note that photolysis is generally considered a minor mechanism of degradation for soil residual herbicides and it should not be expected that photolysis would override impacts of major degradation pathways such as through microbial degradation or chemical hydrolysis.

Herbicide residues in the soil are deactivated in various ways including:

Differences in Residual Herbicides Degradation

In-season moisture and environmental conditions are the dominant factors influencing herbicide carryover, but not all herbicides break down in exactly the same way, regardless of if they belong to the same group. Even within a specific herbicide group, some actives may have varying susceptibility to different degradation pathways and may have alternate interactions with soil properties. For instance, mechanisms of breakdown and relative persistence differs among Group 2 herbicides depending on environmental and soil factors:

In addition to precipitation levels after activation, soil parameters such as organic matter, texture classification, pH, and soil zone are also considered when determining guidelines for recropping intervals. Due to landscape variability, degradation is not uniform within a specific field and soil properties can be highly variable within a field and between neighbouring fields. Soil and environmental condition criteria are outlined on manufacturer labels to further guide instances of increased risk of herbicide carryover.

Table 1. Soil and environmental factors influencing risk of carryover and recommendations for recropping intervals of different active ingredients(2)

Active Ingredient Group Associated Product(s) Primary mechanism(s) of degradation and factors impacting typical re-cropping restrictions
Flucarbazone 2 Batalium™, Everest® 3.0 AG, Sierra® 3.0 AG, MPOWER® Himalaya™, Inferno® Trio, MPOWER® Himalaya™ Trio, Inferno® Duo, MPOWER® Himalaya™ Extra Microbial: Field pea may be grown in the grey-wooded, black, and dark brown soil zones the year following application providing the following conditions are met: soil pH must be below 7.5; organic matter must be above 4%; precipitation must be equal to or above 10-year average (minimum 100 mm within 60 days of application in year of application). Prolonged drought and/or cold temperatures within the year of application cropping season, as well as soils with both low organic matter (less than 2%) and high pH (greater than 7.5) may have decreased microbial activity and, therefore, flucarbazone degradation may be reduced, these factors must be consider when making rotational crop decisions. DO NOT plant crops other than those listed on the label in the year following application.
Imazamox 2 Solo® ADV, Solo® Ultra, Davai®80 SL, Amity™ WDG, Samurai®, and Next 70 Microbial: Where less than 125 mm of accumulated rainfall is received between June 1 and September 1 in the year of application, or additionally for the brown soil zone where less than 15 mm is received in any single month through June, July and August, regardless of total rainfall during that time, delay planting canaryseed, canola (non-CLEARFIELD), flax, tame oats or non-CLEARFIELD wheat (durum or winter), by an additional year. If the same drought conditions as described above occur in either the year of application or the year following, delay planting tame mustard by an additional year. Additional conditions that may slow breakdown and increase the risk of follow crop injury are soil pH of less than 6.5, organic matter of less than 3 percent, very sandy soils and prolonged cold.
Imazamoz/Bentazon 2 + 6 Viper® ADV, Python TM, Boa® Pro, Benz
Imazapyr/Imazamox 2 Ares™ SN Microbial: If rainfall was less than 125 mm during the growing season (June 1 to August 31) the company recommends growing field peas, chickpeas, lentils, Clearfiled® (CL®) lentils, or CL® wheat
Imazethapyr 2 Pursuit® 240, Kamikaze®, Phantom® Microbial: Breakdown may be slowed or delayed by environmental conditions such as drought, excessive cold and/or acid soils (pH less than 6.5) resulting in an increased risk of injury to rotational crops. The most tolerant crops are CLEARFIELD canola and legume crops, then cereals.
Imazethapyr/Imazamox 2 Odyssey® NXT, Duet®, MPOWER® Ninja®, Quasar®, Pursuit® 240, MPOWER® Kamikaze®, Phantom® Microbial: Where less than 125 mm of accumulated rainfall is received between June 1 and September 1 in the year of application, or additionally for the brown soil zone where less than 15 mm is received in any single month through June, July and August, regardlessof total rainfall during that time, delay planting tame oats by an additional year. If the same drought conditions as described above occur in either the year of application or the year following, delay planting non-CLEARFIELD canola by an additional year. Breakdown may be slowed or delayed by environmental conditions such as drought, excessive cold and/or acid soils (pH less than 6.5) resulting in an increased risk of injury to rotational crops. The most tolerant crops are CLEARFIELD canola and legume crops, then cereals.
Metsulfuron 2 Ally® Microbial /Chemical Hydrolysis: Add 12 months to standard label recommendations if less than 130 mm of rainfall in brown and dark brown soils or less than 250 mm rainfall in black or grey-wooded soils in any year following application
Ethalfluralin 3 Edge® MicroActiv® Microbial: Thinning of crop may occur in areas that have received abnormally low amounts of precipitation or in crops that are emerging slowly.
Trifluralin 3 Treflan® Liquid EC, Treflan® MicroActiv®, Rival®, Bonanza® Microbial: Damage to wheat can occur if crop is seeded into land that has been treated during the previous 21 months with trifluralin products and has received abnormally low amounts of precipitation.
Clopyralid 4 Akito™, Curtail® M, Eclipse® Brands, Cirpreme™ XC, MPOWER® Clobber M, Prestige® Brands, Esteem®, MPOWER® Foxxy CM, MPOWER® Clobber G, Lontrel™ XC, Prominex™ , Spectrum™ Microbial: DO NOT seed to field peas or soybean for at least 10 months following treatment. Very dry soil conditions following application (less than 140 mm from June 1- August 31 AND less than 175 mm for the entire year) can result in a risk of injury to field peas grown in rotation. If severe drought conditions are experienced during the months of June to August inclusive in the year of application delay seeding field peas or soybean an additional 12 months (22 months following application). Lentils and chickpeas are never recommended the year after the use of clopyralid. Contact the manufacturer for more information before seeding field peas following drought conditions in the previous year.
Dicamba 4 Engenia™, Banvel®, Oracle®, XtendiMax®, FeXapan®, Disha 480 Microbial: If applications are made after September 1, or if dry weather persists after application, crop injury may occur the following spring.
Sulfentrazone 14 Authority® 480, Authority Supreme® Microbial: Moisture is required for breakdown; therefore, for each year where in-season rainfall is extremely low, the re-cropping interval must be extended by a year and a field bioassay (conducted under normal moisture conditions) must indicate it is safe to plant a sensitive crop.
Quinclorac 4 + 26 Facet® L, Clever®, Ingenious, MasterLine Quinclorac Microbial: On low organic matter soils or under dry conditions, flax and lentils should not be grown until third year after application.
Pyrasulfotole 27 Infinity®, Infinity® FX, Tundra® Microbial: DO NOT plant field peas the season following application in the brown soil zone where organic matter content is below 2.5 percent and where soil pH is above 7.5

2 Saskatchewan Ministry of Agriculture. (2022). Guide to Crop Protection.
Note: use this table as a guideline only. Always refer to the product manufacturer or label.
If there is any uncertainty regarding these or other products, consult with each individual herbicide manufacturer. In response to the increased risk of imidazoline herbicide carryover as a result of the extreme drought and heat conditions experienced during the 2021 growing season, BASF, Adama, and Corteva also announced further recropping restrictions in addition to current label recommendations (see next page).

Table 2. Summary of herbicide carryover risk warning issued by BASF(3), Adama, and Corteva initially issued during the fall of 2021.

Soil & Moisture Parameters Product Season of Application DO NOT Plant in 2022
Dark brown, black, grey, or grey wooded soil zones, less than 125 mm of accumulated rainfall between June 1 and September 1, 2021 Solo® ADV, Solo® Ultra, or Viper® ADV 2021 non-Clearfield® Canola, Durum, Canary
Odyssey® NXT, Odyssey® Ultra, or Odyssey® Ultra NXT 2021 non-Clearfield® Canola, Durum, Canary
2020 non-Clearfield® Canola
All soil zones, less than 125 mm of accumulated rainfall between date of application and August 31, 2021 Davai®80 SL, PythonTM 2021 non-Clearfield® Canola
Ares™, Ares™ SN 2021 Spring Wheat, Barley, Canary, Field Corn, Oats, and Durum Wheat
Quasar® 2020 non-Clearfield® Canola
All soil zones, experiencing severe drought (less than 125 mm of rainfall) during both the 2020 and 2021 growing seasons Ares™, Ares™ SN 2020 non-Clearfield® Canola, Oats, or Mustard
All soil zones, less than 140 mm of accumulated rainfall between June 1 and August 31, 2021 Eclipse® Brands, Cirpreme™ XC, Prestige® Brands, Lontrel™ XC, Prominex™, Spectrum™ 2021 Peas, Soybean
Brown soil zone, less than 125 mm of accumulated rainfall between June 1 and September 1, 2021 AND less than 15 mm of rainfall in any of the months of June, July or August 2021 (regardless of total accumulated rainfall between June 1 and September 1, 2021) Solo® ADV, Solo® Ultra, or Viper® ADV 2021 non-Clearfield® Canola, Durum, Canary
Odyssey® NXT, Odyssey® Ultra, or Odyssey® Ultra NXT 2021 non-Clearfield® Canola, Durum, Canary
2020 non-Clearfield® Canola
Brown soil zone (<3% organic matter) or in low pH soils (pH < 5.5) and receiving less than 125 mm of accumulated rainfall between date of application and August 31, 2021 AND less than 15 mm of rainfall in any of the months of June, July, or August 2021 (regardless of total accumulated rainfall between June 1 and August 31, 2021) Davai®80 SL, PythonTM 2021 non-Clearfield® Canola, Durum, Canary
Quasar® 2020 non-Clearfield® Canola

3 Bertholet, J. (2021). Urgent Notice to Growers. BASF.
4 BASF will utilize Environment Canada weather data to determine total accumulated and monthly rainfall.
5 Corteva does not recommend oats and durum wheat to be grown in rotation after Ares™/Ares™ SN.

Impact of Herbicide Carryover

Potential yield reductions associated with herbicide carryover injury are difficult to predict. Although there have been studies to assess yield impacts on sensitive crops, results may only be relevant to the specific environmental conditions during the period of research. Some products may not have been tested in environmental conditions as extreme as the province experienced during the 2021 growing season. Environmental extremes may result in more crop damage but favourable environmental conditions during the season of injury may also help crops withstand the stress of herbicide carryover injury and allow for a certain extent of crop recovery.

Evaluating Herbicide Carryover Risk

In-season precipitation accumulated after herbicide application generally provides the most reliable indicator of potential risk associated with herbicide carryover. Herbicide carryover risk maps generated by the Saskatchewan Ministry of Agriculture or publicly accessible weather station data provide guidelines for regions potentially at increased risk for herbicide carryover. However, localized field precipitation records are often more beneficial in assessing individual field risk because precipitation events within a season may be sporadic and variable across a relatively small distance.

Table 3. Herbicide carryover risk based on in-season precipitation (June 1 to August 31, 2022) received at Environment Canada weather stations

Environment Canada Weather Station Name RM No. Monthly In-Season Precipitation (mm) Accumulated In-Season Precipitation (mm) General Risk Category5 Imidazoline Herbicide Recropping6
June July August
Brown Soil Zone
Assiniboia 72 21.5 73.6 8.7 103.8 High Restricted
Coronach 11 32.2 77.6 7.5 117.3 High Restricted
Eastend 49 77.2 46.6 4.6 128.4 Moderate Restricted
Kindersley 290 102.4 58.5 12.2 173.1 Normal Typical Use
Leader 231 52.5 29.7 8.3 90.5 Very High Restricted
Lucky Lake 225 48.5 70.6 10.0 129.1 Moderate Restricted
Mankota 45 48.5 89.8 3.8 142.1 Moderate Restricted
Maple Creek 111 123.2 46.5 17.4 187.1 Normal Typical Use
Rockglen 12 36.7 49.3 4.7 90.7 Very High Restricted
Swift Current 137 31.2 27.2 6.7 65.1 Extreme Restricted
Val Marie 17 41.0 42.4 15.9 99.3 Very High Restricted
Dark Brown Soil Zone
Bratt’s Lake 129 37.0 148.0 31.0 216.0 Normal Typical Use
Elbow 254 25.4 96.5 19.6 141.5 Moderate Typical Use
Estevan 5 51.7 83.6 51.5 186.8 Normal Typical Use
Indian Head 156 27.5 114.5 45.9 187.9 Normal Typical Use
Last Mountain 250 40.7 37.1 58.8 136.6 Moderate Typical Use
Moose Jaw 161 24.9 68.2 26.3 119.4 High Restricted
Outlook 284 75.2 53.4 6.9 135.5 Moderate Typical Use
Regina 159 13.1 92.8 18.9 124.8 Moderate Typical Use
Rosetown 288 84.3 54.8 14.5 153.6 Normal Typical Use
Saskatoon 344 38.0 46.5 25.6 110.1 High Restricted
Scott 380 57.1 86.5 32.1 175.7 Normal Typical Use
Watrous 312 9.2 34.8 30.7 74.7 Very High Restricted
Weyburn 67 125.9 14.3 45.2 185.4 Normal Typical Use
Yellow Grass 98 85.0 58.8 48.7 192.5 Normal Typical Use
Black-Grey Soil Zone
Broadview 154 58.8 72.3 38.0 169.1 Normal Typical Use
Hudson Bay 394 52.3 22.7 52.9 127.9 Moderate Typical Use
Loon Lake 561 167.3 28.8 36.1 232.2 Normal Typical Use
Meadow Lake 588 174.2 32.6 43.1 249.9 Normal Typical Use
Melfort 429 78.1 34.9 36.5 149.5 Moderate Typical Use
Nipawin 487 27.2 86.3 78.5 192.0 Normal Typical Use
North Battleford 437 133.1 49.1 30.5 212.7 Normal Typical Use
Pilger 400 49.1 34.7 9.2 93.0 Very High Restricted
Prince Albert 461 63.4 45.7 42.2 151.3 Normal Typical Use
Spiritwood 496 272.4 74.7 46.7 393.8 Normal Typical Use
Waseca 471 107.5 101.8 41.6 250.9 Normal Typical Use
Wynyard 308 49.4 8.3 48.2 105.9 High Restricted
Yorkton 244 57.9 38.4 90.8 187.1 Normal Typical Use

5 Rainfall-based crop rotation recommendations from the Saskatchewan Ministry of Agriculture include. Normal risk areas (>150 mm): follow label directions to determine what crops may be planted following the application of a residual herbicide; Moderate risk areas (150-125 mm): if soil also has low organic matter or soil pH less than 6.5 or greater than 7.5, contact the manufacturer of the residual herbicide; Extreme (less than 75 mm), very high (less than 100 mm), and high (less than 125 mm) risk areas: contact the manufacturer of that residual herbicide for rotational crops supported by the company.
6 Manufacturers of imidazoline-based herbicides may extend additional recropping warning (restricted) if in-season precipitation accumulation from June 1-September 1 is less than 125 mm. When in-season precipitation levels exceed 125 mm the label standard recropping restriction applies. See Tables 1 & 2 for additional information.

Soil Testing

It is possible to have soil samples sent to a lab to be tested for chemical residues. However, this process is expensive and beyond confirmation if the herbicide is present, cannot provide sufficient information to accurately predict if crop injury will result in response to levels extracted by test. Just as detection does not guarantee injury, certain herbicides may be active and initiate a crop injury response below the level of detection by the laboratory analysis. Soil testing for herbicide residues does not account for the interactions of the herbicide with soil properties, therefore cannot be used as an indicator of the bioavailability of that herbicide. Residual carryover can also be highly variable across the field due to differences in soil properties at different landscape positions and these differences cannot be represented in the lab setting with traditional extraction methods.

Soil testing can also provide additional information to assess herbicide carryover risk, by revealing different soil properties that affect herbicide breakdown, within a field. Analysis of soil texture, soil organic matter, and pH can help identify relative risk between fields if soil characteristics are categorically different across regions of the farm. Because individual fields cannot be considered a homogenous unit, site-specific soil sampling protocols may be needed to better capture variability across the field. Unless two fields distinctly represent two contrasting soil types it will be difficult to use a single soil sample to represent the characteristics of the entire field. Even then, general soil testing can help inform relative risk of herbicide carryover but cannot predict it and its extent entirely.

Areas with higher organic matter are generally at a lower risk for herbicide carryover. Soil organic matter acts as a buffer by increasing binding capacity for herbicides in the soil, keeping them away from plant roots. Additionally, higher organic matter soils generally have higher microbial and better water holding capacity activity to assist with herbicide breakdown. Soil texture can also be used to determine herbicide carryover risk. Lighter, or sandier soils, have less binding or adsorption capacity, which significantly increases the risk of herbicide carryover. Herbicide carryover risk increases as organic matter and clay content decrease. Soil pH can also be used to identify herbicide carryover risk.


Field bioassays are often recommended on herbicide labels as a method of evaluating possible herbicide carryover tolerance of sensitive rotational crops. These in-field test strips provide a preview of the rotational crop’s growth and development in the field with suspected herbicide carryover. Because landscape variability impacts herbicide carryover, field bioassays need to be large enough to indicate crop response representative of the entire field. Insights gained from field bioassays are generally not timely enough to inform a cropping decision until the second season after application.

Plant bioassays can be used as a shortcut to growing rotational crops out in the field. This method brings the soil from the field into a greenhouse and grows out susceptible plants in pots to evaluate if they will be impacted by herbicide carryover. Similar to soil testing for residue levels, plant bioassays may not be a reliable indicator of crop response in the field due to soil sampling limitations and under-representation of field variability.

A control, with soil collected from or strips planted into an untreated area of the field, should ideally be included in both bioassay methods as it provides a reference for subtle differences in visual injury. However, this is not always possible and presents a major limitation for using them to consistently predict injury. Bioassays can help provide insights into the impact of herbicide residues present in the soil; however, neither methodology is foolproof nor should they be used in isolation to make recropping decisions.

Mitigating Herbicide Carryover Risk

Figure 3. Relative differences in crop sensitivity to imidazoline based herbicide carryover

Crop Selection
Crop rotation serves as the most significant tool to mitigate risk in fields anticipating a high level of herbicide carryover. Although large changes to a crop rotation can be a challenge, it is important to consider substituting highly sensitive crops for lower risk alternatives that still have agronomic suitability. For instance, pulse crops have the highest tolerance to imidazoline-based herbicide residues and chickpeas, faba beans, field peas, and lentils can all be grown safely the year following imidazoline application according to labels; however, care should be taken to avoid back-to-back seasons of pulses to mitigate risks associated with disease, soil erosion, and weed management.

After pulse crops, cereals exhibit the next best tolerance to residual carryover of imidazoline-based herbicides. However, tolerance among cereal species is not equal as spring wheat is substantially more tolerant to imidazoline residues compared to oats, canaryseed, durum, and barley. Oilseed crops are generally the most sensitive to imidazoline herbicide injury, and among them, mustard and canola rank the highest insensitivity followed by flax. With the exception of tolerance gained through CL® crops, differences in varietal tolerance within a specific crop type have not been identified.

Agronomic Practice

Crop injury caused by the carryover of residual herbicides can be further aggravated by other abiotic and biotic stresses imposed on the crop. Aside from rotation, there is no single agronomic intervention that can fully eliminate herbicide injury. However, following the best management practices for the crop to ensure its vigorous establishment and growth remains an important recommendation to lessen additional stress factors imposed on the crop.

Increasing seeding rates to achieve higher than optimal plant population targets is not recommended because most active ingredients associated with residual herbicide injury do not act as a germination inhibitor. In fact, herbicide carryover injuries are most likely to reveal themselves after a rainfall event that allows an active ingredient to be washed into the root zone once it has been desorbed from soil particles. Although it is still important to target plant populations optimal for specific crops, inflating stand densities will not increase the crop’s tolerance to herbicide residues and may be a costly way to end up with a higher number of injured plants across the field.

Delayed seeding may be another strategy to help buffer negative crop responses associated with herbicide carryover. Establishment in cold soils can be stressful on crops and a reduced growth rate is often observed which can exacerbate the impacts of herbicide carryover injury. Furthermore, delays in seeding to allow for crops to germinate in warm soils can also provide a wider window for herbicide degradation, especially if moisture from spring snowmelt or rainfall has been received and microbial activity is increasing in response to improvements in soil moisture and temperature. Due to cool soils in the spring, herbicide breakdown will be negligible until soils are warmer than 5-7°C. Although delayed seeding can be helpful, it is not a standalone strategy that can guarantee full protection agains injury associated with herbicide carryover. There is no precise recommendation for how much additional time or moisture is needed in the spring if in-season herbicide degradation was expected to be below average.

Compounding Herbicide Carryover

CL® crops (i.e. lentil or wheat) can safely be recropped on fields with Imidazoline (Imi) herbicide carryover. However, when growing CL® tolerant crops on land that has been impacted by Imi herbicide carryover, the crop should be managed conventionally without the use of Imi herbicides in-crop. Applying Imi products, such as Ares™ on CL® tolerant crops is common practice, however in the case of carryover it can lead to crop damage and a further increase of herbicide residue in the soil. Research conducted in the early 2000s found that under some environmental conditions, “back-to-back” application of residual Group 2 herbicides could result in additive or synergistic injury. This can occur with persistent group 2 herbicides such as imazethapyr and sulfosulfuron (Sundance-no longer available). This is known as herbicide stacking. Some Group 2 residual herbicides can accumulate in the soil over multiple growing seasons, if herbicide breakdown is slowed, and result in significant damages to sensitive crops. Not all Group 2 herbicides have the same residual properties.

Small amounts of different residual herbicides can accumulate over several growing seasons to contribute to the injury of a sensitive crop. Areas where drier conditions have been observed over multiple seasons are at a higher risk for herbicide stacking, which occurs when multiple applications of residual herbicides from the same group are sprayed in rotation. Group 2 herbicides are more likely to carry over at levels that can damage plants because they can maintain herbicidal activity at low doses. There are areas of the province that have seen repeated drought for more than one year. These areas in particular need to be aware of possible carryover from previous years and take herbicides applied in the past into consideration also when planning for next year. To see these areas, view Saskatchewan Agriculture’s Herbicide Carryover Risk Maps from the previous season.


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