Using a periphyton sampler to collect material for algal biomass assessment
Superior Streams Algal Assessment
Duluth’s high-quality trout streams are sensitive to urbanization and rural
development. These streams are subject to increasing water temperatures, decreasing
aquifer recharge, and increasing water, sediment and nutrient runoff. Climate change
predictions for the Great Lakes region indicate the potential for these impacts to be
exacerbated via an increase in the frequency of intense storm events and decreased
precipitation in the summer. Understanding how these changes affect stream health is key
in developing protection and restoration activities. Stream health is evaluated using
physical, chemical, and biological measures. The aquatic biological community, primarily
aquatic macroinvertebrates and fish, is most often used to determine stream health, but
algae (aka periphyton) are also used. Periphyton, the algae that
grow on surfaces such as rocks, wood and plants, are useful indicators of stream health
because they are sensitive to many environmental stressors and respond rapidly to
changes in nutrient concentration. The ability of periphyton to grow rapidly in
response to nutrient inputs offers the potential to use this community as a relatively
low-cost, sensitive early-indicator of localized differences in nutrient loading.
2018 Field Sampling
Our 2018 project will measure periphyton in several Duluth trout streams using two methods. The first uses traditional quantitative methods that involve scraping algae off rocks and measuring the chlorophyll and organic content of the material.
The second method will use a visual assessment (VA) technique to estimate percent coverage of algae along the stream bottom as well as the thickness or length of the algal film or mat. The VA method is much quicker and cheaper and has been used successfully in many areas (California and New Zealand to name a few.) to measure algal biomass. We will be working on comparing the two techniques in June and July. We will then perform statistical tests to determine if the VA method can be useful in estimating algal biomass for Duluth-area trout streams.
Volunteer Involvement
We are also interested in locating areas within the streams experiencing dense algal growth. This is where our volunteers can help us. We do not have the resources to walk all the streams throughout the Duluth-area. What we would like volunteers to do is walk sections of their favorite (or assigned) stream, and record images and locations where they observe dense algal growth as seen in the image below. This image was taken in Amity Creek on June 14, 2018.
We would also like them to record some basic habitat observations including water
temperature, recent and current weather, substrate type, approximate stream width and
depth, primary riparian vegetation, and percent canopy cover. Nutrient availability,
substrate type and available sunlight are probably the most important habitat components
controlling algal biomass in streams. Also any other pertinent observations
including fish, aquatic vegetation or insects/hatches observed. It is also helpful
to note any stormwater outlets in the area or any other potential runoff
issues. We will provide maps of the entire watershed, data sheets, and
thermometers, as well as bottles for algal samples.
The best time to look for these areas of dense algal growth is late July through
mid-August, barring any rip-roaring rain events.
Background
Learn more about primary producers - algae - and periphyton, click here.
Contact Elaine Ruzycki for more information and to sign up as a volunteer.
Collaborators
This page was prepared by NRRI using Federal funds under award NA17NOS4190062 from the Coastal Zone Management Act of 1972, as amended, administered by the Office for Coastal Management, National Oceanic and Atmospheric Administration (NOAA), U.S. Department of Commerce provided to the Minnesota Department of Natural Resources (DNR) for Minnesota’s Lake Superior Coastal Program. The statements, findings, conclusions, and recommendations are those of the author(s) and do not necessarily reflect the views of NOAA’s Office of Coastal Management, the U.S. Department of Commerce, or the Minnesota DNR.