Risks for surface runoff and leaching of fungicides from golf greens varying in rootzone composition and amount of thatch

Summary

According to IPM principles, pesticides should be used only when other measures do not provide sufficient control of the harmful organism. One situation where adequate control is difficult is when golf courses are infected with Microdochium nivale. In such cases, it is important to use efficient fungicides with few environmental impacts. This project focused on leaching and surface runoff of fungicides and their metabolites from greens after application in late autumn. A field trial was conducted during winter 2016-17 and 2017-18 at Landvik, Norway. The plots had 5% slope and a turf cover of creeping bentgrass. The trial had four blocks and two factors, each with two levels:

Factor 1: Type of organic amendment to the sand-based (USGA) rootzone:

Factor 2: Turf age/thatch thickness

1.     Sphagnum peat, ignition loss 1.1%, pH 5.5

A.      Green sown in May 2016

2.     Garden compost, ignition loss 1.0%, pH 6.5

B.      Green established in May 2016 using sand-based sod, thatch layer 20 mm

In both years, Delaro SC 325 (prothioconazole + trifloxystrobin) and Signum (boscalid + pyraclostrobin) were sprayed in mid/late October and Medallion TL (fludioxonil) was sprayed in early/mid-November, followed by collection of leachate and runoff until the last snow or ice melt in late March/early April.  

During winter 2016-17, the mostly unfrozen greens had high infiltration rates: 91% of 601 mm precipitation from the first fungicide application to the last sampling was collected as drainage water and only 3 % as runoff. Winter 2017-18 had 948 mm precipitation, and
freeze/thaw cycles on frozen greens resulted in ice cover. In this case, 55 and 33 % of precipitation was collected as drainage water and surface runoff, respectively. Fungicide detections in drainage water were mostly very low; the Norwegian Environmental Risk Level (ERL) was exceeded slightly only for prothioconazole-desthio.

In contrast, the ERL for many fungicides and/or their metabolites was exceeded up to 1000 times in surface water, notably in 2017-18. The highest concentrations were found during the first week after spraying and after snowmelt/soil thaw. Because of the thatch layer, concentrations in runoff were usually higher, but concentrations in drainage lower, on sodded than on seeded greens.

The project highlights the importance of keeping wide buffer zones to open water and avoiding surface runoff by maintaining high infiltration rates. This was communicated to more than 70 industry representatives at the project’s final international seminar in Oslo on
7 March 2019.

 

FACTS
Category: Disease control
Status: Ongoing
Project period: 2016 -2019

Fundings (kSEK)

 

kSEK

 

2016

2017

2018

2019

Sum

STERF

303

294

86

75

758

Other sources 518 422 259 94 1292

TOTAL FUNDING

821

716


345

169

2052

 

Project objectives

Main objective: To minimise fungicide losses from golf courses.

Subgoals:

  • To determine sorption coefficients and thus the risk of leaching of prothioconazole, trifloxystrobin, fludioxonil, boscalid, pyraclostrobin and their metabolites
  • To determine the effect of organic matter type (peat or compost) and turf age/thatch accumulation on the risk of leaching and surface runoff of these fungicides and their metabolites
  • To provide data for modelling leaching and runoff of fungicides from golf greens
  • To publish the results in ‘Journal of Environmental Technology’ or a similar peer-reviewed journal and to disseminate the findings to the environmental authorities and the golf industry in the Nordic countries and Germany.

Project participants

Trygve S. Aamlid

Head of Research

Norwegian Institute for Bioeconomy (NIBIO), Department for Urban Greening and Environmental Technology, Turfgrass Research Group, Landvik, Reddalsveien 215, 4886 Grimstad, Norway.

+47 90 52 83 78

+47 90528378

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