Wisconsin BMP

9 - Responsible Pesticide Management

Wisconsin BMP
9 - Responsible Pesticide Management


Pesticides contain active ingredients (the component that targets the pest) and inert ingredients such as solvents, surfactants, and carriers. Both the active and inert ingredients are regulated by federal, state, and local laws because of environmental and health concerns. 

When a pesticide application is deemed necessary, its selection should be based on:

  • Effectiveness

  • Method and frequency of application

  • Potential toxicity to non-target species

  • Cost

  • Site characteristics

  • Pesticide solubility 

  • Persistence  

  • Packaging and labeled for the site it will be used at

  • Safety of the applicator

  • Equipment available for application


liquid chemical storage.jpg

Pesticides may be used as one element in an integrated pest management (IPM) strategy, alongside biological controls, cultural methods, pest monitoring, and other applicable practice. 

 
 
 

Wisconsin Pesticide Regulations

A restricted use pesticide (RUP) is a pesticide that is designated as such due to potential adverse effects on the environment, the applicator, or bystanders, which warrants added restrictions. Anyone who wants to purchase and use a RUP must be a certified applicator. 

In addition, in Wisconsin, no person may distribute, sell, offer for sale or use any pesticide product containing any of the following active ingredients:

  • 2,4,5-trichlorophenoxyacetic acid (2,4,5-T)

  • 2-(2,4,5-trichlorophenoxy) propionic acid (Silvex)

  • Aldrin

  • Chlordane

  • Dieldrin

  • Heptachlor

 It is the joint responsibility of the person in control of golf course maintenance and the applicator to ensure the application complies with regulations and that correct recordkeeping is maintained. 

There are also regulations concerning the required signage and communications when pesticides are used in golf course settings. All pesticide applications on golf courses must be posted. Permanent warning signs may be used, but golf course superintendents must also post restricted entry interval (REI) warning signs when a defined REI time is listed on the pesticide label. Note that an REI of ‘when dry’ is not considered a defined interval and does not require an REI warning sign.

Permanent warning signs must be conspicuously posted at each of the following locations: 

  • At or near the place where golfers register to play the course 

  • At or near the first tee of every nine holes 

  • At every point on the golf course boundary at which the non-golfing public is permitted to enter the golf course by means of a road, sidewalk, path or other established thoroughfare


Best Management Practices

  • Comply with all Federal, Environmental Protection Agency (EPA) and Wisconsin State laws and regulations

  • Select the least toxic pesticide with the lowest exposure potential and use reduced risk pesticides where appropriate

  • Follow all directions on pesticide’s labeling

  • Follow all instructions on the pesticide label – including sprayer calibration, mixing, and use of Personal Protective Equipment (PPE)

  • Ensure facilities for storing, handling and mixing are properly sited, designed, constructed, and operated

  • Develop an emergency response plan including procedures to control, contain, collect, and store spilled materials

  • Create a record for each application of a RUP; maintain record for two years

More information specific to golf courses:
https://datcp.wi.gov/Documents/HTCLandscapeApplications.pdf

A full list of pesticides registered in Wisconsin, including RUPs:
http://www.kellysolutions.com/wi/

In the case of a pest control treatment project with a pollutant discharge to a water of the state specific permits are required from the WDNR. More information:
https://dnr.wisconsin.gov/topic/Wastewater/AquaticPesticides.html

Wisconsin State Legislature on pesticide use: 
https://docs.legis.wisconsin.gov/statutes/statutes/94/68
https://docs.legis.wisconsin.gov/code/admin_code/atcp/020/29.pdf

 

Personal Protective Equipment (PPE) & Human Health Risk

Pesticides belong to numerous chemical classes that vary greatly in toxicity. The degree of potential risk to human health depends on both the pesticide toxicity and the level of exposure- i.e., the amount of product and length of time involved with any contact. PPE is used for protection against chemicals contacting the person loading, mixing, and spraying the chemical. The pesticide label will provide guidance on the minimum required PPE, it is important to read the label thoroughly before any use. Users must always use at least the minimum PPE required but may also choose to use more PPE than required on the label.

There are four toxicity levels, indicated by pesticide signal words that help provide indicators for what level of risk is present when applying:


Best Management Practices

  • Employers are legally responsible for supplying applicators with the PPE as listed on the label

  • Clearly post landscape warning signs when applying pesticides. Follow the landscape pesticide applications to golf courses guidance from WDATCP: https://datcp.wi.gov/Documents/HTCLandscapeApplications.pdf

  • Ensure that PPE is sized appropriately for each person using it

  • Make certain that PPE is appropriate for the chemicals used

  • Choose PPE based on standards, not just the least expensive

  • Store PPE where it is easily accessible, but not in the pesticide storage area

  • Employees who apply pesticides should not wear facility uniforms home where they may come into contact with children

  • Provide laundering facilities or uniform service for employee uniforms; employees will need to wash clothes that may have pesticide residues on them; washing requires the use of hot water with clothes that are suspected to have pesticide residues; run another empty load once the clothes are washed

  • The federal Occupational Safety and Health Administration (OSHA) requires employers to fit-test workers annually who must wear tight-fitting respirators

  • When using respiratory protects ensure compliance with Occupational Safety and Health Administration (OSHA) 1910.134 Respiratory Protection Program

  • Provide employees access to Safety Data Sheets (SDS) of the products being used

 

Application, Storage & Transport, Emergency Response, Record-Keeping

Responsibilities of Pesticide Owners, Users, or Handlers

Pesticide owners, users and handlers all have a responsibility to fully understand the risks and guidance around any pesticide being used. It is important that anybody involved with pesticide use or management is appropriately trained and certified where required. The Wisconsin Pesticide Law mandates that any person using RUPs, and all commercial applicators, complete training and certification through the UW-Pesticide Applicator Training (PAT) program. 

Training and certification are separate and different entities are involved. The PAT program provides training and educational materials for people to become certified: https://fyi.extension.wisc.edu/pat/

Certification (passing an exam) is overseen and regulated by the DATCP. 

There are several different certification categories, including Turf and Landscape. 

 

Sprayer Calibration

Calibration of sprayer equipment is critical to good pesticide management. Pesticide application equipment must be properly calibrated to mitigate environmental and human health risks relating to pesticide use and spray technicians must always be experienced, licensed, and properly trained. 


Best Management Practices

  • Use an appropriately sized applicator for the size of area being treated 

  • Minimize off-target movement by using properly configured application equipment 

  • Calibrate all application equipment at the beginning of each season (at a minimum) or after equipment modifications 

  • Check equipment daily when in use 

  • Walk-behind applicators should be re-calibrated for each person making the application to take into consideration their walking speed, etc. 

  • Always use recommended spray volumes for the targeted pest to maximize efficacy

  • Keep pressure at the setting recommended by the nozzle manufacturer

  • Use low-volatility herbicides when possible

 
 
 

Environmental Fate and Transport

‘Environmental fate’ refers to the destiny of any chemical, biological substance or pollutant after release into the environment. Pesticides, wherever they are applied, have the potential to interact with wildlife or migrate into surface and subsurface waters. Environmental fate information is included on pesticide labels and indicates where a pesticide travels following introduction and likely exposure levels for non-target organisms (soil, water, air, plants, and animals).  

A key environmental consideration concerns the runoff and leaching potential of a selected pesticide – i.e., the extent and direction of any likely cross contamination from the application site to nearby areas. Prior to application, it is therefore important to consider the specific characteristics of each site. 

Key issues include:

  • Proximity to surface water

  • The water table and well-heads

  • Soil type

  • Prevailing winds

  • Presence of endangered species

Environmental hazards related to a pesticide are listed on pesticide product labels. “Environmental Hazards” are found under the general heading “Precautionary Statements,” which provides language advising the user of the potential hazards to the environment and off target organisms – found under three headings: general environmental hazards, non-target toxicity, and endangered species protection.

 
 

Best Management Practices

  • Select pesticides that have a low drift, runoff, and leaching potential; labels provide warnings about these potential issues with each product

  • Before applying a pesticide, evaluate site-specific characteristics, particularly relating to water sources, surface water, water table, and well-heads, soil type and wind direction

  • Understand site characteristics that are prone to leaching losses (for example, sand-based putting greens, coarse-textured soils, shallow water tables)

  • Select pesticides with reduced impact on pollinators and natural pest predators

  • Select pesticides that, when applied according to the label, have no known effect on endangered species present on the facility

Wisconsin’s Groundwater law (ATCP 31) created two guidelines to limit pesticides in groundwater which include enforcement standards (maximum chemical levels allowed in groundwater) and preventive action limits (set as a percentage of the enforcement standard). The DATCP provides monitoring for pesticides including groundwater from private wells and surface water.

Additional information: https://datcp.wi.gov/Pages/Programs_Services/SurfaceGroundwaterMonitoring.aspx

 

Pesticide Transportation, Storage, and Handling

As pesticides pose their greatest risk when in concentrated form it is essential to follow all storage, transportation, and handling guidance on product labels. The location, design and operation of storage facilities all have a role in minimizing risks related to pesticides. Improper storage of pesticides is a form of misuse and it is therefore important to carefully review and comply with storage information on labels.

The key risks to human health and the environment when considering pesticide storage and transportation are focused on potential spills, contaminated run off or fire. Storage facilities must be properly sited, designed, constructed, and operated in order to minimize these risks. To mitigate water contamination risks pesticide storage facilities should be at least 400 feet downhill from drinking water supplies; 200 feet from surface water and should not be placed within the 100-year floodplain.

 
 

Best Management Practices

  • Storage facilities should be a lockable concrete or metal building with sufficient access to allow fire department approach

  • Storage facilities should facilitate the secure, dry, and temperature-controlled storage of pesticides, in line with label guidance

  • Personnel should have easy access to PPE, stored outside of the pesticide area

  • Snow cover in storage areas should be considered in terms of run-off risk

  • Store, mix, and load pesticides away from sites that directly link to surface water or groundwater 

  • Storage facility floors should be watertight and sealed with a chemical resistant paint; the floors should have a continuous sill to retain spilled materials and no drains, although a sump may be included

  • Sloped ramps should be provided at the entrance of storage facilities to allow the use of wheeled handcarts for moving material in and out of the storage area safely

  • Shelving and surfaces in the pesticide storage and transportation should never be made of wood as wood surfaces can absorb spilled pesticides; all shelving should be made of sturdy plastic or reinforced metal, painted to avoid corrosion 

  • Automatic exhaust fans and an emergency wash area are recommended 

  • Light and fan switches should be located outside the building, so that both can be turned on before staff enter the building and turned off after they leave the building 

  • Avoid temperatures less than 40°F or greater than 100°F inside the pesticide storage facility

  • Do not transport pesticides in the passenger section of a vehicle and never leave pesticides unattended during transport 

  • Place a spill containment kit in the storage area, in the mix/load area, and on the spray rig

  • Fire extinguishers suitable for chemical fires should be readily available

  • The local fire department should be informed about the storage unit, what it contains, and where it is located

 

Pesticide Inventory 

Pesticides degrade over time, so it is important to only mix the amount required for use at any time and to avoid storing large quantities of pesticides for long periods. When bringing in new product, date the labels to be able to identify the oldest in inventory. Adopt the “first in–first out” principle, using the oldest products first to ensure that the product shelf life does not expire. This will reduce the amount of pesticide waste product which needs to be disposed of.

 
 

Best Management Practices

  • Do not purchase pesticides in greater quantities than needed and avoid purchasing large quantities of pesticides that require storage for greater than six months

  • Following the “first in–first out” principle to ensure oldest products are used first and minimize quantities of expired stock

  • Utilize computer software systems to record inventory and use, when possible 

  • Consult inventory when planning and before making purchases

  • Store flammable pesticides separate from those that are non-flammable

  • Store liquid materials below dry materials to prevent leaks from contaminating dry products 

  • SDS and copies of labels for all pesticides on hand should be kept in an easily identifiable location, outside the pesticide storage facility

  • Make sure all containers are labelled correctly and arranged so the labels are clearly visible Immediately replace any damaged or missing labels

  • Maintain inventory copies off site for review in case of fire to help containment issues

 

Pesticide Mixing/Loading/Washing 

Handling open pesticide containers, measuring pesticide materials, or working with pesticide application equipment presents an exposure risk to the handlers and the environment. PPE is an important part of minimizing this risk and must be worn, in line with label guidance, prior to opening of pesticide packages.

Pesticide leaks or spills, if contained, will not percolate down through the soil into groundwater or run off the surface to contaminate streams, ditches, ponds, and other waterbodies. One of the best ways to manage this issue is to ensure the chemical mixing center (CMC) is properly designed and constructed.

Mixing is an important part of proper spraying application. It is essential that all staff involved fully understand what is being sprayed and which chemicals can be mixed. The specific mixing and sequence of mixing instructions on the label should be followed - the most common accidents occur due to staff misunderstanding mixing rates, becoming distracted and/or mixing the wrong materials. If uncertain, a jar test should be prepared to make sure the chemicals are compatible. A jar test is a simple method of using small samples of the mixture and mixing in a small jar. This will allow observation of the reaction and make sure a complete mixture can be achieved.


 Best Management Practices

  • Loading pesticidesand mixing them with water or oil diluents is recommended over an impermeable (watertight) surface, so that spills can be collected and managed

  • The mixing station surface should offer easy cleaning and the recovery of spilled materials

  • Mixing and loading sites should have secondary containment

  • Pump the sump dry and clean it at the end of each day 

  • Liquids and sediments should be removed from the sump and properly managed and disposed of 

  • Apply liquids and sediments from the sump the same as a pesticide, strictly following label instructions

  • Sweep up solid materials and use as intended

  • Rinsate may be applied as a pesticide (preferred) or stored for use as makeup water for the next compatible application - caution: do not mix herbicide rinsate with other products

  • Collect wash water (from both inside and outside the application equipment) and use it as a pesticide in accordance with the label instructions

 
 
 

Pesticide Container Disposal

Pesticide containers, if not rinsed and disposed of properly, can cause a risk to human health and environment. As such federal law (FIFRA) considers that a pesticide container is not legally empty until properly triple rinsed and requires pesticide applicators to rinse all empty pesticide containers before taking other container disposal steps. Containers for non-liquid pesticides (bags, drums, bottles) need to be triple-rinsed or have the ends removed and all product removed from the container before disposal. Unrinsed pesticide containers are considered hazardous waste and improper disposal can result in fines and/or criminal penalties. Once properly rinsed, however, pesticide containers can be handled and disposed of as non-hazardous waste.

DATCP manages an annual grant program for counties and municipalities wishing to collect unwanted pesticides. Businesses with agricultural pesticides may be eligible for up to 50 percent subsidy on disposal costs. More information: https://datcp.wi.gov/Pages/Programs_Services/CleanSweep.aspx

 
 

Best Management Practices

  • It is illegal to dispose of excess pesticides by dumping them on the ground; while pesticides are broken down to non-toxic compounds by microorganisms, excessive amounts applied to the soil can “overload” this natural system and contaminate drinking water

  • Refer to the label for disposal requirements 

  • Rinse containers during the mixing and loading process and add rinsate water to the finished spray mix

  • When a pesticide container is empty fill it up with water three times, each time pouring the rinse water into the spray tank when preparing the solution for final application; this is called triple rinsing and is important to remove chemical residues

  • Puncture or crush empty and rinsed pesticide containers and dispose of according to the label 

  • It is against the law to use empty pesticide containers for another function

 
 

Emergency Preparedness and Spill Response

It is essential to have an emergency preparedness plan in place to ensure that if an accident occurs it is clear which steps to take to mitigate human health effects and environmental impact. Emergency preparedness plans should have copies stored close to pesticide storage facilities and should be shared with local police and fire departments. 

Anyone who spills fertilizers or pesticides is legally responsible for cleaning up the spill if it harms or threatens to harm public health or the environment, regardless of the amount of the spill.

Report pesticide or fertilizer spills immediately to the WDATCP Spills Hotline if the amount is:

  • 250 pounds or more of dry fertilizer

  • 25 gallons or more of liquid fertilizer

  • Enough pesticide to cover one acre or more if applied at label rates

Additional information on spills and the Wisconsin Spill Law: https://cdn.shopify.com/s/files/1/0145/8808/4272/files/A3714.pdf

Contact the DATCP Agricultural Chemical Cleanup Council at (608) 224-4500 or email datcpaccp@wisco​ns​in.gov​.


Best Management Practices

  • Develop a golf course facility emergency preparedness plan that includes procedures to control, contain, collect, and store spilled materials

  • Maintain copies in English and any other language commonly used by employees

  • Ensure an adequately sized spill containment kit is readily available

  • Designate a spokesperson who will speak on behalf of the facility should an emergency occur

  • Seek advice from local authorities – policy and fire departments - on ways to improve the plan

  • Have emergency contact information clearly visible at the storage facility and offsite

 

Pesticide Record-Keeping

Pesticide-specific record-keeping can be required by Federal or state rule, in addition to the pesticide label. Pesticide applicators who have a private applicator license or certificate are required to maintain records of their applications of RUPs under the Food, Agriculture, Conservation and Trade Act of 1990: https://www.ams.usda.gov/rules-regulations/pesticide-records/understanding.

Anyone using a RUP, or anyone required to be licensed as a commercial applicator must maintain records of their pesticide applications under Wisconsin State Law ATCP 29.

Records must contain:

  1. Product name 

  2. EPA registration number 

  3. Concentration or amount applied per area and total quantity applied

  4. Date and time of application (time application began, and time application ended)

  5. Location of land/legal property description 

  6. Site treated 

  7. Total acres or volume of area treated 

  8. Location of mix/load site

  9. Applicator name and license number and/or person supervising the application 

  10.  Who the application was made on behalf of (if applicable)

Records should also contain:

  1. Pest treated 

  2. Wind direction and velocity and air temperature 

  3. ID number of application equipment 

  4. Spray permit number for regulated herbicides applied in a regulated county 

  5. Documentation to verify training of persons working under the supervision of a licensed pesticide applicator

A Wisconsin record-keeping form may be accessed at: https://fyi.extension.wisc.edu/pat/files/2018/01/recordkeeping-form.pdf

Additional information:
https://fyi.extension.wisc.edu/pat/pat-tools/
https://datcp.wi.gov/Documents/HTCLandscape.pdf


Best Management Practices

  • Records must be recorded within 14 days of application and maintained for two years for RUP applications per Federal requirements

  • Records must be kept accessible and available for copying and must be maintained at the applicator’s primary place of business as designated on the applicator’s pesticide license 

  • Records of application must be made available for inspection upon request

  • Keep a backup set of records in a safe, but separate storage area

  • Use records to monitor pest control efforts and to plan future management actions

There are several resources available to assist with record-keeping, covering everything from inventory through to planning and reporting. Examples include: