
Cow-berry or Lingon-berry

Vaccinium vitis-idea
Family: Ericaceae
Fire effect on plant
Fire usually burns above ground biomass of lingonberry, but its underground regenerative structures generally survive low to moderate severity fires (Viereck et al. 1980). Although moderate to heavy duff consuming fires may kill the plants.
Key traits
Resprouting in lingonberry occurs from rhizomes and adventitious root crown and buds. This species has abundant branched underground stems buried 2 to 3 cm deep in the soil humus (Viereck et al. 1980) and the rhizomes of lingonberry have been observed to survive in soil where the surface temperature reached 438oC (Uggla 1959).
The seeds of lingonberry are considered to be heat-sensitive and are usually destroyed by fire (Viereck et al. 1980), although other evidence suggests that heating improves germination (Mallik and Gimingham 1985). Lingonberry seed germination has been shown to improve upon heating with 98% of seeds germinating following heat treatment at 100oC for 30s within 9 weeks of heating (Mallik and Gimingham 1985). Seeds are animal dispersed. Seedbank longevity is unknown.
Plant response to fire
Lingonberry is known to persist in regimes with frequent fires and in areas that rarely burn (Tirmentein 1991). However, despite this it is reported as a fire-prone species requiring repeated fire for its maintenance (Engelmark 1987). Following fire, lingonberry has been noted to grow vigorously and can increases cover after fire by resprouting from rhizomes and adventitious roots and buds on charred stems (Engelmark 1987). This is supported by burning experiments that looked at regrowth of lingonberry where vegetative regrowth occurred even though the tops of the plants were heated and burned in series of experiments at 400, 600 and 800oC for 2 mins (Mallik and Gimingham 1985). Remaining stem material can resprout following fire and buried rhizomes resprout within a year, with abundance recovered after a few growing seasons (Wein and Bliss 1973).
Timing of life history
Perennial species. Seeds likely produced from third or fourth growing season (Fernqvist 1977). Flowering May to July.
Conservation status
None.
References
Fernqvist, I. 1977. Results of experiments with cowberries and blueberries in Sweden. Acta Horticulturae 61: 295-300 [Empirical evidence; Academic literature]
Mallik, A. U., Gimingham, C. H. 1985. Ecological effects of heather burning. II. Effects on seed germination and vegetative regeneration. Journal of Ecology 73: 633-644 [Empirical evidence; Academic literature]
Tirmenstein, D. 1991. Vaccinium vitis-idaea. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station,
Fire Sciences Laboratory (Producer). Available: https://www.fs.usda.gov/database/feis/plants/shrub/vacvit/all.html [Expert opinion; Grey literature]
Uggla, Evald. 1959. Ecological effects of fire on north Swedish forests. Stockholm, Sweden: Almqvist and Wiksells. 18 p. [Empirical evidence; Academic literature]
Viereck, L.A.; Schandelmeier, L.A. 1980. Effects of fire in Alaska and adjacent Canada--a literature review. BLM-Alaska Tech. Rep. 6. Anchorage, AK: U.S. Department of the Interior, Bureau of Land Mangement, Alaska State Office. 124 p. [Empirical evidence; Grey literature]
Wein, R. W.; Bliss, L. C. 1973. Changes in Arctic Eriophorum tussock communities following fire. Ecology 54: 845-852. [Empirical evidence; Academic literature]