Browsing by Subject "Taking Stock - Habitat"

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Activities of the Grand Portage Reservation (Minnesota) to Protect and Restore the Aquatic Habitat in Lake Superior
(2006) Frazier, Brad; Watkins, Margaret; Nelson, Ryan
This is a 30-slide Powerpoint presentation summarizing the Grand Portage natural resources, wetlands, air quality, energy, solid waste and water quality program details; the cooperative agreement between the Grand Portage tribal authority and Minnesota Pollution Control Agency; the no discharge zone; and nonpoint source pollution efforts. Also briefly summarizes activities of the 1854 Treaty Authority.
Breeding Bird Communities Across an Upland Disturbance Gradient in the Western Lake Superior Region
(2007) Miller, Christina; Niemi, Gerald J; Hanowski, JoAnn M; Regal, Ronald R
The coastal region of western Lake Superior to examine relationships to human land use. Eighty-four species were detected and 50 were abundant enough to be included in data analysis. Monotonic quadratic regression models were constructed for these 50 species by using species counts as the dependent variable and the proportion of human conversion of the landscape (residential, agriculture, and commercial/industrial land uses) within each study area as the independent variable. Twenty-seven bird species had significant regressions (P < 0.05), 18 of which generally avoided areas developed by humans and 9 of which were attracted to development. De-trended correspondence analysis using counts of these 27 bird species was used to investigate multivariate, community responses to development. The first DCA axis was interpreted as a gradient from urban avoiding to urban exploiting bird species and was strongly correlated with land cover variables related to human development. Our results advance the idea that breeding bird communities can be used as indicators of ecological condition and can diagnose potential causes for changes in these conditions. Further, our study points out the usefulness of bird monitoring data in regional planning efforts that incorporate goals for maintaining native biological diversity.
Evaluating Minnesota's Historic Dams: A Framework for Management
(Archaeo-Physics, LLC, 2013) Arnott, Sigrid; Birk, Douglas A; Maki, David
This study assessed 31 historic mill dam sites in Minnesota. Of these, one was located in the Sea Grant coastal area. The study discusses broader impacts of dams on tribal, cultural and environmental resources generally, which are relevant to the SG study area.
Fond du Lac Resource Management: 2008 Integrated Resource Management Plan
(2008) Fond du Lac Band of Lake Superior Chippewa
This very comprehensive document was reviewed and is felt to have significant content and analysis relevant to Minnesota’s coastal area and water resources. It also contains biophysical and watershed-related content directly relevant to Native communities in Minnesota’s coastal communities. Key content is reproduced below: Executive summary: “This Integrated Resource Management Plan contains information about the Band’s past and current management activities and identifies resources that need additional management. The Integrated Resource Management Plan contains alternatives to resource management, as required by the National Environmental Policy Act, which are based on the management objectives. Management activities range from no action to full implementation, and the alternatives presented reflect that range. The objectives that can be completed under each alternative are displayed in a table located at the end of discussion on alternatives. Public input was solicited on the draft document, which included a variety of management alternatives. Comments obtained from the community and tribal government were incorporated into the final document, and the hearing process provided a basis for the formulation and selection of the preferred alternative. The preferred alternative is officially approved by Resolution # 1183/08. Each resource is described in a narrative that was developed in the following format: o Description of the affected environment o Background for that resource o Issues, concerns, and opportunities for that resource o Goals and objectives for that program, with different management alternatives The final chapter is a summary of the alternatives. The preferred alternative is identified for each resource.” Approximately 15 pages of this report are dedicated specifically to water-based resources, including chapters on wild rice, wetlands and water, and fisheries. Some sections are reproduced below. Wild Rice There are five primary wild rice lakes on the Fond du Lac Reservation. The total area on which wild rice is currently present on these lakes is 843 acres. The wild rice areas on the individual lakes are: Perch Lake, 411 acres; Mud Lake, 151 acres; Rice Portage Lake, 131 acres; Jaskari Lake, 79 acres; and Deadfish Lake, 71 acres. These lakes are all within the Stoney Brook Watershed, which is tributary to the St. Louis River. Wild rice is also present in Side Lake, Cedar Lake, Wild Rice Lake, Simian Lake, and Hardwood Lake. Side Lake and Hardwood Lake are within the Stoney Brook Watershed. Cedar Lake and Simian Lake are within the Simian Creek Watershed. Wild Rice Lake is the headwaters of the Moosehorn River, a tributary of the Kettle River. The density of mature wild rice varies from season to season, as the ecology of wild rice growth is related to cycles of plant decomposition, the number of growing days, and available nutrients. In addition, wild rice is easily lost as a result of natural events, such as high winds, flooding, and hail. The majority of the wild rice resource on the Fond du Lac Reservation is in the Stoney Brook Watershed. Beginning in 1916, the Stoney Brook Watershed was adversely affected by the creation of a network of judicial ditches. These judicial ditches drastically altered the hydrology of the watershed, resulting in the loss of over 500 acres of wild rice habitat. The lower water levels that resulted from the judicial ditching allowed competing vegetation to encroach on areas that at one time supported wild rice. Besides the Stoney Brook Watershed, wild rice resources in other areas of the Fond du Lac Reservation are in decline as well. The reason for this decline is primarily due to higher water levels, caused by road building and beaver activity. The Fond du Lac Natural Resources Program is responsible for the wild rice management and restoration activities on the Fond du Lac Reservation. The primary method of wild rice lake management consists of utilizing water control structures (dams) to stabilize water levels, ditch maintenance, and beaver dam management. The restoration of the major wild rice lakes on Fond du Lac is dependent on restoring the lakes to their historical elevation and a more natural annual hydrological cycle. The implementation of the Rice Portage Wild Rice and Wetland Restoration Project resulted in the construction of four water control structures. These four structures are located at the outlet of Perch Lake, the outlet of Rice Portage Lake, an impoundment that is upstream of Deadfish Lake (commonly known as “Upper Deadfish”), and at the outlet of Deadfish Lake. These structures are used to restore the lake elevations and improve hydrologic function. Issues: The ineffectiveness of current mechanical methods for the restoration project on Rice Portage Lake. Mud Lake continues to produce a thin crop of wild rice, despite its potential for higher yields. Concerns: Invasive species–both invasive and exotic plant species–are of great concern due to their persistence once introduced. While there are no know exotic species in our wild rice lakes, the risk is high given the uses of these lakes by waterfowl hunters and wild rice harvesters. Climate change–weather pattern changes, annual precipitation, and temperature changes–all may impact the viability of our wild rice lakes. Opportunities The Stoney Brook Watershed Study will provide a model that will allow for more effective water level management, and identify opportunities for restoration of the original river system, and abandonment of unnecessary ditch segments. The current trend of land purchasing, land use planning, and increased resource management capabilities affords long term protection for portions of the wild rice lake watershed that were unavailable in the past. Increased Resource Management Division staff and capabilities may allow for opportunities to partner with other agencies and organizations to restore, protect, and enhance wild rice growth throughout the Ceded Territories. Goals & Objectives At a minimum, maintain the current program and management. Increase vegetation treatment acreage per annum. Surface water resources The Fond du Lac Reservation includes abundant freshwater resources, with over 3,000 acres of lakes (828 acres of wild rice waters), nearly 44,000 acres of wetlands, and 96 miles of rivers and streams. The St. Louis River, the largest U.S. tributary to Lake Superior, borders the Reservation to the north and east, and approximately 95% of the waters of the Reservation lie within its watershed. All of the waters within the Reservation are believed to be relatively pristine. There are no known or permitted industrial or municipal discharges to the waters, except to the St. Louis River. Historical hydrological modifications to many of the Reservation’s wild rice lakes occurred with the development of the judicial ditch drainage system early in the twentieth century. Currently, a restoration project is underway to gradually restore Rice Portage Lake, one of the most productive rice lakes, to its historical water levels, and to minimize water level fluctuations on Deadfish Lake, thereby enhancing its stands of rice. Shoreline development and the accompanying potential for increased nutrient inputs (septic discharge and lawn chemicals) and erosion are factors that could affect the water quality of several Reservation lakes. By 1998, the Fond du Lac Environmental Program developed and the Reservation Business Committee adopted a set of Water Quality Standards for the surface water resources of the Reservation, setting contaminant criteria and designating uses for 24 lakes and eight streams within the boundaries, and identifying Outstanding Reservation Resource Waters. More recently, the Band has been granted “Treatment as a State” authority by the U.S. Environmental Protection Agency, under the federal Clean Water Act, enabling it to enact and enforce such standards. As a critical tool for implementing these standards, the Environmental Program designed a comprehensive Water Quality Monitoring Plan. Initially a rigorous three-year monitoring project measuring the physical, chemical and biological quality of 24 lakes and eight streams located within the exterior boundaries of the Reservation, it has since been modified to reflect an ongoing status and trends program. This comprehensive database on Fond du Lac surface waters will also permit the Office of Water Protection to develop numerical biocriteria to replace the narrative biocriteria currently in the tribal Water Quality Standards. The data is also utilized to assess and report on the condition of these water bodies and their attainment of designated and aquatic life uses. Protecting human health requires monitoring for indicators that measure the safety of eating fish or other aquatic wildlife, or of swimming and boating. Conserving ecosystems requires indicators of diverse, healthy aquatic plant and animal communities, and indicators are also needed to assure that water quality and sediment conditions can maintain those biological communities. The Water Quality Monitoring Plan was designed to assess indicators for both human health and aquatic life. Atmospheric deposition of mercury is of particular concern in this boreal forest and wetland ecoregion, as biochemical processes enhance mercury availability to the aquatic food chain, bioaccumulating to levels that are hazardous to top predators and humans. Consequently, fish caught in Reservation waters can be dangerously high in tissue mercury content. Criteria for the Water Quality Standards were calculated under an assumed fish consumption rate that is much higher than the state of Minnesota or the Great Lakes region assumes for the general population, as some Band members rely upon fish at a subsistence level in their diet. The Environmental Program has completed several projects that assessed contaminant levels (mercury, PCBs and lead) and characterized sediments of twelve Reservation lakes and the St. Louis River. In 2001, Fond du Lac partnered with the Minnesota Department of Health to collect and analyze fish tissue from lakes and the St. Louis River (preferred fishing waters), using the data to develop specific fish consumption advisories. Groundwater In 2004, Fond du Lac completed its first Nonpoint Source Assessment Report and applied for Treatment as a State for non-point source authority. The Office of Water Protection received its first base program funding in 2005 and is using that support to implement several projects under the following categories: hydro modification, timber harvesting, roads and urban development. The Resource Management Division is also engaged in a major hydrologic study of the Stoney Brook watershed in partnership with Natural Resources Conservation Service and the U.S. Geological Survey. Ultimately, a Stoney Brook Watershed Management Plan will be developed to account for multiple resource management objectives, including wild rice production and stream and wetland restoration. The Office of Water Protection also has identified aquatic invasive species as a major concern for protecting the Reservation’s water resources. The nonpoint source program provides for broad education and outreach to the Reservation community and affected stakeholders, in order to minimize nonpoint source impacts to Fond du Lac water resources. The primary objectives of the Environmental Program are to ensure the protection of valuable ground water resources through the continued closures of abandoned wells, the delineation of protection zones for wells contributing to community water systems, and the development of a wellhead protection plan for the Reservation. The Fond du Lac Reservation boundary encompasses 101,153 acres, of which 43,264 (43%) are wetlands. These wetlands consist of forested (67% – black spruce, tamarack, or black ash dominant; includes bogs), scrub shrub (29% – alder or willow dominant), emergent (3% – sedge, reed canary grass, or cattail dominant; includes wild rice lakes), and open water (< 1% – coontail dominant). Many wetlands on the Reservation have been degraded due to human activities, particularly by ditching, road construction, agricultural and silvicultural runoff, and commercial and residential development. The Environmental Program has a Wetlands Conservation and Protection program that has been active since October of 1998. A Wetlands Protection and Conservation Plan was adopted by the Reservation Business Committee in October 2000. The plan was expanded, updated and adopted by the Reservation Business Committee in February 2006 to become the Fond du Lac Joint Comprehensive Wetlands Protection and Management Plan. The adoption of this plan led to the development and adoption by the Reservation Business Committee of the Fond du Lac Wetlands Protection and Management Ordinance in June 2006. Erosion and sedimentation resulting from storm water can cause significant impact to surface waters. On the Reservation, construction activities have the potential to be a major contributor to these impacts. Since March 2003, the Office of Water Protection has been providing erosion and sedimentation control best management practices oversight of construction projects on the Reservation. This is the result of the Environmental Protection Agency’s National Pollutant Discharge Elimination System Phase II Construction Storm Water regulations as part of Section 402 of the Clean Water Act. In addition to this voluntary oversight, the Office of Water Protection has also entered into a Storm Water Direct Implementation Tribal Cooperative Agreement to conduct inspections of construction sites impacting one acre or more. Two tribal inspectors have been trained and credentialed by Environmental Protection Agency to conduct inspections on the Reservation. More than 13 projects are scheduled for inspection during the construction seasons of 2007 and 2008. In addition, the Office of Water Protection has been developing the required Storm Water Pollution Prevention Plans for nearly all projects conducted by the Reservation, as well as occasional projects conducted by individual Band members.” A long list of concerns and threats to water resources is included in the report. These related to taconite and sulfide mining operations, mercury deposition, nonpoint source pollution and other causes. “Fisheries The majority of the lakes on the Fond du Lac Reservation are small, shallow bodies of water, more suitable for growing wild rice than for the management of any significant fisheries. Many of these lakes do have fish, however, with populations consisting primarily of northern pike), largemouth bass, panfish, yellow perch), and bullhead. Due to relatively shallow water, high abundance of aquatic macrophytes, and substrates composed predominantly of decaying organic matter, many of these Reservation lakes are incapable of supporting any naturally reproducing populations of walleye (Sander vitreus). These lakes are, however, conducive to the production of northern pike, panfish, largemouth bass, and bullhead but are also subject to frequent winterkill. Most of the lakes on the Reservation do have some type of public access, though most are strictly carry-in accesses. The fishery of the St. Louis River is by far the most important one for residents of the Reservation. At least four game fish species can be found in appreciable numbers; northern pike, walleye, smallmouth bass, and channel catfish. The channel catfish fishery remains the highest priority of Fond du Lac Band members who regularly use the St. Louis River’s fishery resources. Much can be done to improve the trout populations on the Reservation. Stream improvements and the removal of beaver and their lodges and dams may improve habitat for resident trout populations. Stocking may need to be a part of future management activity, but shouldn’t be random and haphazard as past stocking activities appear to have been. In addition, regular assessments need to be performed following any stocking efforts. The fisheries in the 1854 and 1837 Ceded Territories are numerous and diverse, from small trout streams in the Superior National Forest, to lakes such as Mille Lacs that are capable of sustaining large walleye populations, to the salmon and trout of Lake Superior. Walleye and northern pike appear to be the most important species to Band members, and are relatively abundant throughout both of the Ceded Territories. A high priority for Band members is a concentrated subsistence harvest at Mille Lacs Lake, where a regular spring harvest season occurs.”
Grand Portage Band of Lake Superior Chippewa: Creative Solutions for a Changing Environment
(2012) Grand Portage Bank of Lake Superior Chippewa
This report summarizes several environmental initiatives and climate change adaptation strategies including wind, community gardens, moose collaring, introduction of bison, etc. Some points are relevant to water resources and are extracted below: Summary: "The Grand Portage Band of Lake Superior Chippewa Indians resides in the northeast corner of Minnesota along Lake Superior. The dynamic environs of the region host a wide array of birds, fish, mammals, amphibians and reptiles. Unprecedented warming of Lake Superior in recent years suggests that climate change is taking effect around Grand Portage and is threatening local wildlife species. One of the Grand Portage Band’s major concerns is that climate change may lead to the loss of culturally significant subsistence species including moose and brook trout in the Lake Superior region. The tribe hopes that by investing in mitigation projects it can accomplish environmental and natural resources goals, achieve energy and food independence, contribute to carbon solutions, and reduce expenses to community members. In addition to existing mitigation projects and initiatives, the tribe is currently developing a comprehensive climate change adaptation and mitigation plan for tribal lands and resources. The plan addresses water quality, air quality, sustainable forestry, adaptation to shifts in fisheries and wildlife, sustainable food ventures, alternative energy development, and energy conservation programs. "Fisheries: To adapt to climate change, the tribe has shifted management of a 61-acre inland lake from a cold water (brook trout) fishery to a cool water fishery (yellow perch and walleye) through fish propagation and stocking. This occurred because warming temperatures in the lake reached critical lethal levels for brook trout causing complete collapse of the population. The Grand Portage Natural Resources Department adapted to the fishery collapse by choosing to develop a cool water fishery using yellow perch and walleye. The Grand Portage Native Fish Hatchery is now using re-circulating water systems to achieve the water temperatures needed for rearing cool water native fish species like walleye and lake sturgeon, in addition to rearing cold water brook trout for Lake Superior. This allows for better utilization and flexibility of the hatchery and stocking operations, while also providing higher growth rates for fish. The Grand Portage Band is also revising legacy contaminant (mercury) concentrations in fish tissue for consumption advisories for the Grand Portage Community. "Invasive Species Management: Aquatic invasive species (AIS) assessments for plants, fish, and invertebrates have been planned for water bodies in Grand Portage. The additional AIS surveys have stemmed from the climate change adaptation plan which noted that warmer water temperatures may increase or aid dispersal of AIS."
An Integrated Approach to Assessing Multiple Stressors for Coastal Lake Superior
(2011) Niemi, Gerald J; Reavie, Euan; Peterson, Gregory S; Kelly, John R; Johnston, Carol A; Johnson, Lucinda B; Howe, Robert W; Host, George; Hollenhorst, Thomas; Danz, Nick; Ciborowski, Jan H; Brown, Terry; Brady, Valerie; Axler, Richard P
This peer-reviewed article summarizes research conducted under the Great Lakes Environmental Indicators (GLEI) project initiated by the authors in 2001. The authors assessed the status of Lake Superior’s coastal ecosystem relative to over 200 environmental variables collected from GIS data sets for the enture US Great Lakes basin. These were assessed using gradients including atmosphereic deposition, agriculture, human population and development, land cover, point source pollution, soils and a cumulative stress index. Relationships of biological assemblages of birds, diatoms, fish and invertebrates, wetland plants, soils and stable isotopes to these gradients were then assessed. Key findings are extracted and reproduced below. Biological indicators can be used both to estimate ecological condition and to suggest plausible causes of ecosystem degradation across the U.S. Great Lakes coastal region. Here we use data on breeding bird, diatom, fish, invertebrate, and wetland plant communities to develop robust indicators of ecological condition of the U.S. Lake Superior coastal zone. Sites were selected as part of a larger, stratified random design for the entire U.S. Great Lakes coastal region, covering gradients of anthropogenic stress defined by over 200 stressor variables (e.g. agriculture, altered land cover, human populations, and point source pollution). A total of 89 locations in Lake Superior were sampled between 2001 and 2004 including 31 sites for stable isotope analysis of benthic macroinvertebrates, 62 sites for birds, 35 for diatoms, 32 for fish and macroinvertebrates, and 26 for wetland vegetation. A relationship between watershed disturbance metrics and 15N levels in coastal macroinvertebrates confirmed that watershed-based stressor gradients are expressed across Lake Superior’s coastal ecosystems, increasing confidence in ascribing causes of biological responses to some landscape activities. Several landscape metrics in particular—agriculture, urbanization, human population density, and road density—strongly influenced the responses of indicator species assemblages. Conditions were generally good in Lake Superior, but in some areas watershed stressors produced degraded conditions that were similar to those in the southern and eastern U.S. Great Lakes. The following indicators were developed based on biotic responses to stress in Lake Superior in the context of all the Great Lakes: (1) an index of ecological condition for breeding bird communities, (2) diatom-based nutrient and solids indicators, (3) fish and macroinvertebrate indicators for coastal wetlands, and (4) a non-metric multidimensional scaling for wetland plants corresponding to a cumulative stress index. These biotic measures serve as useful indicators of the ecological condition of the Lake Superior coast; collectively, they provide a baseline assessment of selected biological conditions for the U.S. Lake Superior coastal region and prescribe a means to detect change over time.” Key points: “In general, the U.S. Great Lakes coastal region of Lake Superior shows greater overall stress in the southern regions compared with relatively low overall stress in the northern regions. These patterns are primarily due to agricultural land use, higher human population densities, and point sources in the eastern and western portions on the south shore, while the north shore at the western end of Lake Superior is primarily forested with relatively sparse human population densities. Coastal regions of Lake Superior can be found at each of the extremes of the disturbance gradients. This includes relatively pristine watersheds in the northern regions with low human population densities and little agriculture that contrast with regions of relatively high populations with industrial activity such as Duluth-Superior in Minnesota-Wisconsin and Sault Ste. Marie Michigan at the other end of the gradient. The U.S. Lake Superior coastal region varies widely in the degree of human-related stress; generally, levels of stress decrease from south to north but with considerable variation, especially along the southern shore due to local agricultural activity and the presence of several population and industrial centers. In spite of a lack of latitudinal variation, there is human-induced, watershed scale variability across the Lake Superior coast. Compared to the other Great Lakes, Lake Superior coastal fish communities had more generally intolerant fish and more turbidity intolerant fish. Coastal fish community composition reflected the higher levels of suspended solids associated with human alteration to watersheds. The most disturbed sites on Lake Superior had greater proportions of non-native species and fewer bottom-feeding taxa.
Lake Superior Aquatic Invasive Species Complete Prevention Plan
(2014) Lake Superior Binational Program
This report summarizes a team effort to identify methods and actions to prevent new exotic species from entering Lake Superior. The plan seems to acknowledge that introduction of AIS is a result of generally unintentional human behavior, and is therefore preventable. Key contents of the report are extracted and reproduced below. Abstract: “Situated at the head of the Great Lakes St. Lawrence Seaway system, a 2,342 mile long (3,700 km) water navigation system connected to global trade, Lake Superior is at risk for continued invasion by aquatic invasive species (AIS), including plants, animals, and microscopic organisms. As of April 2010, 89 non-native aquatic species have been found in Lake Superior. These include Eurasian watermilfoil, sea lamprey, and most recently, the fish disease Viral Hemorrhagic Septicemia (VHS). AIS have caused devastating economic and ecosystem effects that impart significant losses to the region in the form of damage and control costs, degraded water quality, job losses, declining property values, compromised native species, decreased biodiversity, and other negative impacts. “This Lake Superior Aquatic Invasive Species Complete Prevention Plan outlines recommended actions that need to be newly implemented, in addition to existing efforts, to prevent new aquatic invasive species from entering and becoming established in the Lake Superior ecosystem. Through the process of developing this plan, Canadian and U.S. government agencies involved in the Lake Superior Lakewide Action and Management Plan (LAMP) have consulted broadly and have developed recommendations for consideration by each jurisdiction. However, citizens, organizations and government agencies in both Canada and the United States need to work together to implement the recommended actions and ensure that protecting Lake Superior from new invasive species is a top priority for all. The Lake Superior LAMP will utilize an adaptive management approach to monitoring implementation progress and overall effectiveness of this prevention plan. “Key recommended actions for the United States and Canada include: ● Implement compatible, federal regulatory regimes for ballast water discharge that are protective of the Great Lakes for both the U.S. and Canada. ● Support the development, testing and implementation of effective ballast treatment systems that meet the operational characteristics of Great Lakes ships. ● Establish federal screening processes for organisms in trade to classify species into three lists: prohibited, permitted, and conditionally prohibited/permitted. ● Establish an immediate moratorium on the trade of prohibited species. ● Consider the concept of a “Certified Pathogen-Free through Raising from Seed” category for plants sold through garden centers and nurseries. ● Expand or implement education programs to increase consumer awareness of the risk of AIS. ● Require permits for shoreline restoration projects, which identify AIS introduction issues and include best management practices and restrictions that minimize the potential for introducing invasive species. ● Implement education programs to raise awareness of the issue and promote compliance with prevention actions among contractors and residents. ● Ensure that existing laws prohibiting the sale of invasive species are enforced for on-line and mail order purchases of aquatic plants. ● To prevent the illegal transport of bait across the U.S./Canadian border and on shared waters, ensure effective education and prevention efforts at border crossings and at retail bait shops, and conduct monitoring to gauge the effectiveness of such efforts. ● Make AIS prevention education, regulation, and enforcement a priority in all Lake Superior jurisdictions, and implement prevention approaches that target specific audiences (e.g., boaters, anglers, professional fishing guides, plant nurseries). ● Build capacity for education and enforcement efforts within local communities by providing outreach products that can be tailored for local use, and coordinate consistent messaging across jurisdictions. ● Explore options for a broad range of prevention measures at public boat launches. ● Review and adjust policies for the operation of the locks at Sault Ste. Marie to include best management practices that effectively prevent fish from passing through the locks, including closing the upper and lower gates when not in use and the use of in-stream barriers or deterrent technologies, if necessary. ● Investigate options to achieve ecological separation of the Great Lakes and Mississippi River watersheds to protect the Great Lakes from the invasion of Asian carp. ● Until ecological separation is achieved, maintain the electric barriers in the Chicago Sanitary and Ship Canal at optimum conditions and ensure their continued operation. ● Establish structural measures to prevent the inadvertent introduction of Asian carp from floodwaters of the Des Plaines River into the Chicago Sanitary and Ship Canal. ● Adapt invasive species management to the challenge of a changing climate – monitor ecosystem changes, coordinate information resources, and engage in further research.”
Lake Superior Climate Change Impacts and Adaptation
(2014) Huff, A; Thomas, A
This is a recent and comprehensive report that summarizes expected and cross-cutting impacts of climate change on all biophysical aspects of Lake Superior (fisheries, bird migration, pollutants, flooding, etc.). It is based on a review of other studies, and proposes a framework for monitoring changes in the Lake Superior basin.
Lake Superior Lakewide Action and Management Plan Annual Report 2013
(2013) Minnesota Sea Grant
This pdf summarizes progress made toward achieving the goals of the Lakewide Action and Management Plan (LAMP). In 2013, LAMP will focus on invasive species, land use change, biodiversity, chemicals of concern and potential effects of climate change. The findings and recommendations included in the International Joint Commission’s March 2012 summary of findings and recommendations on regulation of water levels in Lake Superior will also be considered. The report lists seven specific sites were progress has been made on clean-ups of contamination in Areas of Concern (AoCs). The report lists ongoing challenges including stressors (contaminants, climate change, chemicals, and the need to monitor these stressors), including the 2012 floods on US and Canadian areas of Lake Superior. The report briefly lists next steps (implementing projects; prevention of invasive species; working with mining and power companies; protecting and restoring habitat, etc.).
Mercury in Streams at Grand Portage National Monument: Evidence of Ecosystem Sensitivity and Ecological Risk
(2012) Wiener, James G
This is a 4-page pdf, which apparently has not been published although the paper reviewers are named. The origin of the paper is unclear, and it should be regarded as “gray” literature. Key points are extracted and reproduced below. “In 2008, the University of Wisconsin-La Crosse began quantifying mercury in aquatic food webs in six national park units in the western Great Lakes region, including Grand Portage National Monument (GRPO). Principal objectives are (1) to identify parks and water bodies where concentrations of methylmercury are high enough to adversely affect fish and wildlife, and (2) to assess spatiotemporal patterns in methylmercury contamination of aquatic food webs. Methylmercury is a highly toxic compound that readily bioaccumulates in exposed organisms and can biomagnify to harmful concentrations in organisms in upper trophic levels of aquatic food webs. Study sites at GRPO include Snow Creek (beaver pond in upper reaches and lower reaches), Poplar Creek (south branch), and Grand Portage Creek (lower reach). Analytical results reveal elevated concentrations of both total mercury and methylmercury in these stream systems... Concentrations of total mercury and methylmercury in streamwater from GRPO are substantially higher than concentrations typically found in lakes and streams in the western Great Lakes region. “Bioaccumulation and ecological risk. In 2010, prey fish were sampled from three streams in the park and analyzed whole for total mercury, which accumulates in fish as methylmercury. Mean concentrations were highest, exceeding 100 ng/g wet weight (nanograms per gram, equivalent to parts per billion) in blacknose dace (Rhinichthys atratulus) and longnose dace (Rhinichthys cataractae) from Poplar Creek. These mean concentrations in dace substantially exceed the estimated dietary threshold (40 ng/g wet weight in prey fish) associated with reproductive effects of mercury on piscivorous fish that feed on prey fish (Depew et al. in press). Mean concentrations of mercury in most of the other prey fishes analyzed also exceeded the 40 ng/g threshold for reproductive effects on piscivorous fish; these included creek chub (43 ng/g) and central mudminnow (56 ng/g) from Poplar Creek, fathead minnow (58 ng/g) and central mudminnow (55 ng/g) from Snow Creek, and longnose dace from Grand Portage Creek (67 ng/g). The maximal concentrations in individual fish were 242 ng/g in blacknose dace and 211 ng/g in longnose dace. These maximal values exceed dietary thresholds associated with adverse effects of methylmercury on the health and reproduction of fish-eating birds. “The high concentrations of methylmercury in larval dragonflies may indicate significant risks for insectivorous songbirds that forage and nest near streams at GRPO. Studies in eastern North America have documented unexpectedly high concentrations of mercury (present as methylmercury) in certain terrestrial invertivores, including passerine songbirds. Most songbirds with elevated concentrations of mercury are linked trophically to mercury-methylating environments—such as wetlands, streams, or lakes—and feed on spiders or emergent insects with aquatic larval stages. Methylmercury in the diet of reproducing female birds is transferred rapidly to the developing egg, and the embryo is the most sensitive life stage. Methylmercury exposure and its potential effects on reproductive success of invertivorous songbirds at GRPO has not been assessed but merits critical evaluation.”
Regional, Watershed, and Site-Specific Environmental Influences on Fish Assemblage Structure and Function in Western Lake Superior Tributaries
(2005) Brazner, John; Tanner, Danny K; Detenbeck, Naomi E; Batterman, Sharon L; Stark, Stacey L; Jagger, Leslie A; Snarski, Virginia M
This report assesses the impact of human activities and forest fragmentation on fish communities in the western Lake Superior basin. Human-induced activities noted in the report included temperature changes, siltation, erosion, forest cover and forest manipulation, and invasive species. Specific results are reproduced below. “The relative importance of regional, watershed, and in-stream environmental factors on fish assemblage structure and function was investigated in western Lake Superior tributaries. We selected 48 second- and third-order watersheds from two hydrogeomorphic regions to examine fish assemblage response to differences in forest fragmentation, watershed storage, and a number of other watershed, riparian, and in-stream habitat conditions. Although a variety of regional, fragmentation, and storage-related factors had significant influences on the fish assemblages, water temperature appeared to be the single most important environmental factor. We found lower water temperatures and trout–sculpin assemblages at lower fragmentation sites and higher temperatures and minnow–sucker–darter assemblages as storage increased. Factors related to riparian shading and flow separated brook trout streams from brown trout (Salmo trutta) – rainbow trout (Oncorhynchus mykiss) streams. Functionally, fish assemblages at lower fragmentation sites were dominated by cold-water fishes that had low silt tolerance and preferred moderate current speeds, while fishes with higher silt tolerances, warmer temperature preferences, and weaker sustained swimming capabilities were most common at higher storage sites. Our results suggest that site-specific environmental conditions are highly dependent on regional- and watershed-scale characters and that a combination of these factors operates in concert to influence the structure and function of stream fish assemblages. Key points: This study was completed within 160 km of Duluth, Minnesota, in the Northern Lakes and Forests Ecoregion and within two ecological units, the North Shore Highlands (north shore streams) and the Lake Superior Clay Plain (south shore streams)which provided excellent contrast in hydrogeomorphic types. Functionally, south shore fishes tended to be silt-dwelling, trophic generalists with slow current preferences and a tendency towards nest-guarding spawning behavior. North shore fishes tended to be single-bout spawners with fast current preferences. From a management perspective, our results suggest that both timber management and wetland restoration or degradation decisions will need to be considered by resource managers when fish community health is a concern. For example, increasing percentages of mature forest cover should allow for salmonid–sculpin assemblages to become more prevalent in streams with the potential for cool or cold waters. Similarly, increased wetland cover should allow for a greater predominance of healthy warmwater fish assemblages assuming that other landscape features are not too badly degraded. By understanding the species structure and functional character of an assemblage and its relationship to landscape features, managers should be able to make at least a rough assessment of watershed condition. Lacking fish data, it might be easier to simply characterize forest cover and storage as a first step in identifying which watersheds likely contain streams that are degraded. Our results suggest that although in-stream habitat rehabilitation should continue to be used an important tool to improve biological conditions in streams, restoration efforts will have greater success if the potential interactions with landscape conditions are factored into the decision-making process. In some situations, manipulation of forest cover or watershed storage may have a greater impact on fish assemblage integrity than in-stream habitat improvements.”
Scale-dependent Response by Breeding Songbirds to Residential Development Along Lake Superior
(2010) Ford, Michelle T; Flaspohler, David J
This is the first study to examine the influence of Great Lakes shoreline residential development on forest breeding bird communities on any of the Great Lakes. This study took place near Houghton Michigan but may be relevant for Minnesota’s coastal areas given that migrating birds utilize common flyways, and their habitat and movements have trans-boundary characteristics. For these reasons it is included in the study. The abstract and key points are reproduced below. Abstract: “We examined the influence of shoreline residential development on breeding bird communities along forested portions of Lake Superior and hypothesized that anthropogenic changes related to housing development would alter bird community structure compared to areas without human development. We used point counts to compare relative abundance of bird species in relation to residential development at coarse (along 1 km shoreline stretches with and without housing/cottage development) and fine (developed and undeveloped sides of a shoreline access road) spatial scales during the 2005 breeding season. More species had development related differences in abundance at the finer-scale analysis than at the coarse scale. American Crows and American Robins were more abundant on the developed, shoreline side of shoreline access roads. Red-breasted Nuthatches, Blackthroated Green Warblers, and Red-eyed Vireos were more abundant on the undeveloped, inland side of shoreline access roads. Several species were detected exclusively in developed or undeveloped forest areas. The pattern of development-related differences in relative abundance of bird species depended on the scale at which data were analyzed, suggesting that many species may respond to habitat differences within the 100 m scale quite distinct from how they respond to differences at the scale of thousands of meters.”

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