Researchers from Simon Fraser University Burnaby, BC studied the effects of spawning salmon species on fruiting of salmonberries, Rubus spectabilis. No surprise to anyone who has used fish guts, fish eggs and carcasses as fertilizer, the remnants of spawning salmon dragged or floated up on the banks of streams, adds a big fertilizer boost to salmonberries. These researchers studied 14 salmon streams and found that all that organic waste product promoted fruiting, and the density of chum salmon was correlated with increased fruit production. Pinks didn’t measure up. Seed count, fruit weight and sugar content were not correlated with salmon density. I’ll bet those traits are more related to bumble bee and other pollinator activity. Conclusion? Fish fertilizer makes great fertilizer!
SIEMENS, L.D., A.M. DENNERT, D. S. OBRIST, J. D. REYNOLDS. Spawning salmon density influences fruit production ofsalmonberry (Rubus spectabilis). Ecosphere 11(11):e03282. 10.1002/ecs2.3282
Abstract. Annual spawning migrations by Pacific salmon can provide substantial subsidies to nutrientlimited
Annual spawning migrations by Pacific salmon can provide substantial subsidies to nutrient-limited freshwater and riparian ecosystems, which can affect the abundance, diversity, and physical characteristics of plant and animal species in these habitats. Here, we provide the first investigation of how salmon subsidies affect reproductive output in plants, focusing on a common riparian shrub, salmonberry (Rubus spectabilis). We studied 14 streams with a range of spawning salmon densities on the central coast of British Columbia, Canada. We determined the effects of chum (Oncorhynchus keta), pink (O. gorbuscha), and total salmon spawning density on the number of fruits per shrub, number of seeds per fruit, fruit weight, and estimated sugar content (° Brix) of salmonberry fruits. We found that the number of fruits per salmonberry shrub increased with increasing salmon density. However, we found no effect of salmon density on the number of seeds per fruit, fruit weight, or sugar content. The effect of salmon density was species-dependent; the number of fruits per shrub increased with chum salmon density but was not affected by pink salmon density. This could be because chum salmon occur at higher densities and are transferred from water to land at higher rates than pink salmon in our study area. Higher salmonberry fruit production could lead to a larger input of salmonberry fruits to coastal food webs. These results demonstrate how salmon can cross ecological boundaries and influence reproductive output of terrestrial species.
2019. Victoria Rawn Wyllie de Echeverria , Thomas F. Thornton Ambio https://doi.org/10.1007/s13280-019-01218-6
2019. Wyllie de Echeverria, Thornton
The authors tackle one of the most complex issues in climate change science and ecology – how to include a human element in identifying change including traditional knowledge of plants and animals. How can human experiences, languages and traditions be used to verify change, and how can the importance of these traditions be included in ecological studies of climate change. One main goal, of course, is to identify ways indigenous people can maintain customary uses of their region, in this case, coastal areas in Southeast Alaska, while adapting to broader ecological changes that occur in an ecosystem. Participants in a survey noted weather pattern shifts in their lifetime such as more snow, more rainfall, as well as shifts in the seasons. The researchers also examined language patterns to learn about traditional words used for weather or activities related to weather such as “foods being dried in the sun”. They indicated that changes in plant use in the region was most likely because of land use changes (logging, land development) rather than specific climate change.
One case study examined changes to salmonberry and blueberry species that are considered keystone species because they are used heavily by locals and have a long tradition of use. The authors tried to make connections between people’s recollections, historical knowledge and current practices compared to ecological knowledge of berry picking sites, yields, berry quality and more. I think back to some of the experiments in ecology I have been involved with over the years. They are so complex, it is difficult to isolate a single or even a handful of biological causes for a particular observation. For instance, there are so many reasons why berries might not appear in a season (frost during spring, drought, too much rain, poor soil nutrition, predation, and on and on. Recollections might be due to any or a combination of these factors. Attributing them to climate change is tricky and challenging. Human knowledge might just add to the evidence, but as climate scientists will agree, it takes many, many years and a lot of data points to begin to draw conclusions.
Posted in Berry Harvesting, Blueberries (Vaccinium), Ecology, Ethnobotany, Salmonberry (Rubus spectabilis)
Tagged climate change, ethnoborany, Rubus spectabilis, Vaccinium alaskense, Vaccinium caespitosum, Vaccinium parvifolium, Vaccinium uliginosum
Gardeners often apply extra fertilizer to their wild berry patches to increase yields in wild stands. This paper summarizes research on the effects of applying nitrogen fertilizer on large and small animals as well as plants. It is an interesting survey of forest systems and not just the wild berry we have in mind.
Influence of nitrogen fertilization on abundance and diversity of plants and animals in temperate and boreal forests
Published on the web 26 July 2017.
Environmental Reviews, https://doi.org/10.1139/er-2017-0026
Aerial and land-based applications of nitrogen-based fertilizers to enhance forest growth makes nutrients potentially available to all trees, plants, and wildlife in a given ecosystem, and therefore may have direct and indirect effects on wildlife and biodiversity. A scientific review of these potential effects was conducted with 106 published studies covering vascular and non-vascular plants, amphibians, birds, mammals, terrestrial invertebrates, and soil animals associated with fertilization in temperate and boreal forests, primarily in North America and Scandinavia. In terms of direct effects, amphibians and domestic mammals appear to be the most sensitive to urea used in fertilization programs. The avoidance behaviour and/or mortality of amphibians in laboratory studies was species-dependent. Ruminant animals, including wild ungulates, rapidly convert urea to ammonia and are susceptible to toxicity following ingestion of large amounts of urea. Feeding on urea pellets by small mammals or gallinaceous birds appears to be minimal as granules are unpalatable. In terms of indirect effects, the majority of responses of understory herbs to nitrogen fertilization showed an increase in abundance. Some shrubs in repeatedly fertilized stands eventually increased in abundance in long-term studies, whereas dwarf shrubs and abundance of bryophytes (mosses and terrestrial lichens) declined. In general, species richness and diversity of understory herbs and shrubs declined, or were unaffected, in fertilized stands. Response in abundance and species richness-diversity of vascular plants to a single application of nitrogen showed either an increase or no change. Repeated applications (2-5 and > 5) usually resulted in declines in these responses. Relative abundance of mule deer (Odocoileus Rafinesque spp.), moose (Alces alces L.), and hares (Lepus L. spp.), and forage quantity and quality were usually increased by fertilization. Small mammal species generally showed increases or no change in abundance; decreases may be related to fertilizer-induced changes in food sources. Forest fertilization may provide winter feeding habitat for coniferous foliage-gleaning insectivorous birds in some cases. Six species of forest grouse showed no response to fertilizer treatments. Responses of soil animals to nitrogen fertilization appeared to be species- and dose-specific and ameliorated by surrounding micro- and macro-habitat characteristics.
Here is a thesis that explores climate change through berries near Kugluktuk, Nunavut, Canada. The program is part citizen science as well as documenting the ethnobotany of the region. It includes great summaries of the most important berries and even some recipes!
Posted in Bearberry (Arctostaphylos), Berry Harvesting, Blueberries (Vaccinium), Cloudberries (Rubus chamaemorus), Crowberry (Empetrum nigrum), Ecology, Ethnobotany, Foraging, Lingonberry, Lowbush cranberry, (Vaccinium vitis-idaea), Recipes, Wild harvesting
Occasionally, native plants, wildflowers, berries and others, bloom in fall. I have seen it on high bush cranberries, red osier dogwood, willows. wild iris, wild roses and more. This year it is lingonberries. I have noticed a lot of flowers appearing at the same time as berry harvesting. Considering the season, this second bloom is not surprising. Spring warm temperatures came early, and in my garden, Oct 1, the temperatures reached 60F! Despite the cool, rainy summer, the lingonberry grew, bloomed, matured fruit, and went dormant. The dormancy period is very short for lingonberries- about 4 weeks of chilling temperatures (40F or lower). With the long season, it is no surprise that flower buds broke dormancy and started to bloom again. Of course, it is wasted genes. No fruit will form. This fall flowering definitely impacts next season’s flowering and fruiting.
Here is a link to an article by Canadian Researchers who are interested in following the growth, flowering and fruiting of two of the most important wild berries, cloudberry and lingonberry. They followed phenological sequences of flowering and fruiting and documented potential pollinators in their region. It is interesting to compare their cycles with Alaska. It was published in:
Canadian. Journal. of Plant Science. 96: 329–338 (2016)
Cloudberry and Lingon phenology
Abstract: Plant habitat, growth, fruit yield and occurrence of pollinators in cloudberry and lingonberry fields/bogs were monitored and analyzed at three locations in southern Labrador: Lanse’au Clair (51°41’ N, 57°08’ W), Red Bay (51°43’ N, 56°26’ W), and Cartwright (53°42’ N, 57°0’ W) over the two growing seasons, 2011 and 2012. The length of the growing seasons was 100–120 d (DFRA 2014) with 600–700 growing degree days (GDD) (AAFC 2014). The 2012 season was warmer than 2011. The plants recorded in belt transects belong to six families: Rosaceae, Ericaceae, Pottiaceae, Juncaeae, Equisetaceae, and Sphagnaceae. In the Ericaeae family, Vaccinium vitis-idaea, Arctostaphylos alpina, Empetrum nigrum, and Vaccinium angustifolium were found. In both seasons, the cloudberry was the first to bloom, followed by wild blueberry, lingonberry, and Labrador tea. The fruit yields of cloudberry and partridgeberry in southern Labrador were higher than those recorded in Finland, Norway, and in the USA. Pollinators were present in large numbers. Most of the specimens were from three orders: Hymenoptera, Diptera, and Lepidoptera. Temperature, precipitation, wind, and sunlight affected plant growth and the occurrence of pollinators. To our knowledge this is the most comprehensive study of plant growth, yield, and pollinators’ activity in cloudberry/partridgeberry fields conducted in Southern Labrador, Canada.