Winter damage to golf greens in the Nordic countries

Survey of causes and economic consequences (part II).

Project start date: January 2017
Projects completion date: July 2018

Facts

Principal investigator (PI):

Tatsiana Espevig, Norwegian Institute of Bioeconomy Research (NIBIO), Dept. Urban Greening and Environmental Engineering, Turfgrass Research Group, Landvik, Reddalsveien 215, 4886 Grimstad.

Phone: +47 406 23 778. E-mail: tatsiana.espevig@nibio.no

Co-applicants:

Trygve S. Aamlid, Inghild Økland and Wendy M. Waalen, NIBIO Turfgrass Research Group.

Project objectives

In 2015, NIBIO and NGF, with the support of STERF, ran a survey regarding winter damage on golf greens. The survey, which consisted of 24 questions, was distributed online, and included the five Nordic countries: Denmark, Finland, Iceland, Norway and Sweden. More than 300 golf courses participated. The results from the survey were analysed in two steps. The first article focused on course geography, size and age, grass species and extent of winter injuries (Kvalbein et al., 2016, 2017). It revealed that total costs of repair of winter-injured greens and fairways, together with lost revenue from players, in the Nordic countries amounted to at least €14 million. In a year with significant winter injuries, the average cost to repair the turf was between €3 000 and €12 000 on 88% of the courses. The revenue loss after a winter with considerable injuries was less than €6 000 on 50% of the courses, while 25% of the courses reported a loss between €6 000 and €12 000 (Kvalbein et al., 2016, 2017). The second article focused on management before winter: autumn fertilisation, fungicide applications and winter maintenance (Økland et al., 2018). The results showed that winter survival of golf greens can be improved and confirmed that the severity of snow mould infection can be reduced by continuing N-fertilisation at low and decreasing rates until growth stops and the greens freeze in late autumn. More research is needed on the effects of late K- and Fe-fertilisation before clear guidelines on this practice can be given. Use of only systemic or systemic and contact fungicides gave the same good control of snow mould infection. There was no overall effect of green topography on winter survival, but there were indications that lower areas may be more susceptible to ice and water damage and higher areas may be more susceptible to snow mould. Due to the low number of respondents who used protective covers in this survey, there was not enough information to conclude whether there is a benefit from using protective covers or not. There are still unanswered questions about the mechanical treatments of golf greens during winter and the respective beneficial effects. A field experiment could be carried out to explore these, in which the survival of greens with different combinations and separate treatments is compared within one location, thereby eliminating the variable of winter stress pressure.

Project summary and status January 2019

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:

In both years, Delaro (prothioconazole+trifloxystrobin) and Signum (boscalid+ pyraclostrobin) were sprayed in late October and Medallion (fludioxonil) in early November. Factor 1: Organic amendment in the sand-based (USGA) rootzone: Factor 2: Turf age / thatch thickness 1.Sphagnum peat, loss on ignition 1.2 % OM, pH 5.5 A. Green seeded in May 2016 2.Garden compost, loss on ignition 1.0 % OM, pH 6.5 B. Green established in May 2016 using sand-based sod, (25 mm thatch) Applications were followed by collection of leachate and runoff until snowmelt/soil thaw around 1 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.

Funding, kSEK

20172018Total
STERF184866
Other sources04343
Total1891109