Freshwater shoreline management

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Freshwater Shoreline Management involves assessing and protecting lakes, rivers, and other freshwater shorelines from excessive development or other anthropogenic disturbances.

Contents

Shoreline management involves the long-term monitoring of watershed and shoreline revitalisation projects. [1] Freshwater shoreline management is frequently run by local conservation authorities through state, provincial, and federal lake partner programs. These programs have been used as a method of tracking shoreline change over time, determining areas of concern, and educating shoreline property owners.

History

The concept of Freshwater Shoreline Management evolved from ideas developed for the Integrated Coastal Zone Management (ICZM), which emerged from the 1992 United Nations Conference on Environment and Development. [2] In Canada, a coastal zone management plan was completed by 1996 using the ICZM framework. [3] Freshwater management programs utilized the coastal zone management plan to create freshwater management plans to address the growing concerns for the environment that had been aired since the 1960s in Canadian society. [4]

Anthropogenic effects on watersheds were increasing globally in the 1900s, with nutrient loading of phosphorus, nitrogen, and sulfur causing eutrophication and acidification of water bodies. [4] These effects are primarily caused by the human development of shorelines, agricultural runoff of chemicals and fertilizers, human litter, and sewage/wastewater. [1] To manage these impacts, local and regional organizations began conducting watershed monitoring programs to detect long-term environmental changes and establish their causes. [4]

Usage

Anthropogenic effects on lakes, such as freshwater usage, shoreline development, recreational use, [5] agriculture, [6] and retaining walls, [7] can negatively impact aquatic and terrestrial organisms that rely on the shoreline of a lake for habitat. [8] The anthropogenic effects can also cause eutrophication and acidification of lakes, which impacts organisms within the water itself and can also cause harm to human health. It can have the added effect of decreasing property values and tourism in the lake communities due to some beaches being unsafe to swim in because of pollutants. [6] [9]

Since it may be modified to match the needs of the watershed and be applied to the current land use nearby, freshwater shoreline management is useful for community-based monitoring. The Lake Ontario Shoreline Management Plan is an example of how communities can use freshwater shoreline management. [10] Programs such as this were developed by conservation authorities and citizens alongside regional and provincial governments to perform shoreline mapping and assessment, public consultation/education, and implement long-term monitoring of the watershed and shoreline. [11]

The Muskoka Watershed Council has also performed shoreline assessments using the Love Your Lakes Program [12] to survey the shoreline of Lake Bella in the Muskoka District. It showed that the natural shoreline decreased from 96% in 2002 to 80% in 2007, impacting the overall water quality as it allows for increased nutrient runoff, negatively impacting biodiversity as it decreases habitat for fish, insects, and birds. [11] This program has increased local education on lake health and stewardship of revitalizing shorelines. [11]

Climate Change Impacts

Climate change has been found to affect freshwater shoreline communities. Effects such as increased warming of the water bodies, increased storm runoff, the quickening of yearly ice melt and limited amounts of winter ice, and increased wave height during storms, which increases the potential of erosion, were all found to potentially affect lake shorelines. [13]

Shoreline management has been identified as a method to mitigate climate change impacts such as potential flooding and nutrient loading from frequent and higher-intensity storms. That can occur as shorelines naturalize, which can increase filtration and decrease sediment and nutrient runoff. [14]

Example: Love Your Lakes Program

The Love Your Lakes Program is an example of a Shoreline Assessment and Revitalization program used in Canada. [15] It was developed under the Canadian Ministry of Environment and Climate Change (MECC) Lake Partner Program as a joint effort between Watersheds Canada, MECC, and the Canadian Wildlife Federation. [15]

The program allows lake owners and organizations to apply to have their shorelines assessed and discusses methods that individuals and the community can use to revitalize their shorelines. Naturalization, using native plant species along the shoreline to create a buffer, it is often recommended as this limits erosion from wake action and can decrease nutrient runoff from lawn maintenance or farming activities. [16] To this date, almost 200 lakes have been assessed by the program. [15] This has led to increased community awareness and shoreline naturalization, which has transformed up to 300 shoreline properties. [17]

Related Research Articles

<span class="mw-page-title-main">Eutrophication</span> Excessive plant growth in response to excess nutrient availability

Eutrophication is the process by which an entire body of water, or parts of it, becomes progressively enriched with minerals and nutrients, particularly nitrogen and phosphorus. It has also been defined as "nutrient-induced increase in phytoplankton productivity". Water bodies with very low nutrient levels are termed oligotrophic and those with moderate nutrient levels are termed mesotrophic. Advanced eutrophication may also be referred to as dystrophic and hypertrophic conditions. Eutrophication can affect freshwater or salt water systems. In freshwater ecosystems it is almost always caused by excess phosphorus. In coastal waters on the other hand, the main contributing nutrient is more likely to be nitrogen, or nitrogen and phosphorus together. This depends on the location and other factors.

<span class="mw-page-title-main">Wetland</span> Land area that is permanently, or seasonally saturated with water

Wetlands, or simply a wetland, is a distinct ecosystem that is flooded or saturated by water, either permanently or seasonally. Flooding results in oxygen-free (anoxic) processes prevailing, especially in the soils. The primary factor that distinguishes wetlands from terrestrial land forms or water bodies is the characteristic vegetation of aquatic plants, adapted to the unique anoxic hydric soils. Wetlands are considered among the most biologically diverse of all ecosystems, serving as home to a wide range of plant and animal species. Methods for assessing wetland functions, wetland ecological health, and general wetland condition have been developed for many regions of the world. These methods have contributed to wetland conservation partly by raising public awareness of the functions some wetlands provide. Constructed wetlands are designed and built to treat municipal and industrial wastewater as well as to divert stormwater runoff. Constructed wetlands may also play a role in water-sensitive urban design.

<span class="mw-page-title-main">Water pollution</span> Contamination of water bodies

Water pollution is the contamination of water bodies, usually as a result of human activities, so that it negatively affects its uses. Water bodies include lakes, rivers, oceans, aquifers, reservoirs and groundwater. Water pollution results when contaminants mix with these water bodies. Contaminants can come from one of four main sources: sewage discharges, industrial activities, agricultural activities, and urban runoff including stormwater. Water pollution is either surface water pollution or groundwater pollution. This form of pollution can lead to many problems, such as the degradation of aquatic ecosystems or spreading water-borne diseases when people use polluted water for drinking or irrigation. Another problem is that water pollution reduces the ecosystem services that the water resource would otherwise provide.

<span class="mw-page-title-main">Dead zone (ecology)</span> Low-oxygen areas in coastal zones and lakes caused by eutrophication

Dead zones are hypoxic (low-oxygen) areas in the world's oceans and large lakes. Hypoxia occurs when dissolved oxygen (DO) concentration falls to or below 2 mg of O2/liter. When a body of water experiences hypoxic conditions, aquatic flora and fauna begin to change behavior in order to reach sections of water with higher oxygen levels. Once DO declines below 0.5 ml O2/liter in a body of water, mass mortality occurs. With such a low concentration of DO, these bodies of water fail to support the aquatic life living there. Historically, many of these sites were naturally occurring. However, in the 1970s, oceanographers began noting increased instances and expanses of dead zones. These occur near inhabited coastlines, where aquatic life is most concentrated.

<span class="mw-page-title-main">Bayou</span> Body of water in flat, low-lying areas

In usage in the Southern United States, a bayou is a body of water typically found in a flat, low-lying area. It may refer to an extremely slow-moving stream, river, marshy lake, wetland, or creek. They typically contain brackish water highly conducive to fish life and plankton. Bayous are commonly found in the Gulf Coast region of the southern United States, especially in the Mississippi River Delta, though they also exist elsewhere.

<span class="mw-page-title-main">Thermal pollution</span> Water temperature changes resulting in degraded water quality

Thermal pollution, sometimes called "thermal enrichment", is the degradation of water quality by any process that changes ambient water temperature. Thermal pollution is the rise or drop in the temperature of a natural body of water caused by human influence. Thermal pollution, unlike chemical pollution, results in a change in the physical properties of water. A common cause of thermal pollution is the use of water as a coolant by power plants and industrial manufacturers. Urban runoff—stormwater discharged to surface waters from rooftops, roads, and parking lots—and reservoirs can also be a source of thermal pollution. Thermal pollution can also be caused by the release of very cold water from the base of reservoirs into warmer rivers.

<span class="mw-page-title-main">Tidal marsh</span> Marsh subject to tidal change in water

A tidal marsh is a marsh found along rivers, coasts and estuaries which floods and drains by the tidal movement of the adjacent estuary, sea or ocean. Tidal marshes experience many overlapping persistent cycles, including diurnal and semi-diurnal tides, day-night temperature fluctuations, spring-neap tides, seasonal vegetation growth and decay, upland runoff, decadal climate variations, and centennial to millennial trends in sea level and climate.

<span class="mw-page-title-main">Surface runoff</span> Flow of excess rainwater not infiltrating in the ground over its surface

Surface runoff is the unconfined flow of water over the ground surface, in contrast to channel runoff. It occurs when excess rainwater, stormwater, meltwater, or other sources, can no longer sufficiently rapidly infiltrate in the soil. This can occur when the soil is saturated by water to its full capacity, and the rain arrives more quickly than the soil can absorb it. Surface runoff often occurs because impervious areas do not allow water to soak into the ground. Furthermore, runoff can occur either through natural or human-made processes.

<span class="mw-page-title-main">Orangespotted sunfish</span> Species of fish

The orangespotted sunfish is a North American species of freshwater fish in the sunfish family (Centrarchidae) of order Perciformes. These fish are widely distributed across the middle and eastern United States, from the Rocky Mountains to the east, from the Great Lakes south into the Gulf Coast. The orangespotted sunfish is ecologically unique and thrives in turbid, shallow systems that have few predators and low oxygen contents. The species prefers vegetated areas in sluggish backwaters or lakes, and can also be found in turbid rivers. The orangespotted sunfish can extend its range in lower-quality waters, which is not characteristic to other sunfish. Orangespotted sunfish vary in total length and age for different river basin originations, but can be found to live four to seven years, and recorded lengths are up to 15 cm (5.9 in).

Hard engineering involves the construction of hydraulic structures to protect coasts from erosion. Such structures include seawalls, gabions, breakwaters, groynes and tetrapods.

<span class="mw-page-title-main">Human impact on the nitrogen cycle</span>

Human impact on the nitrogen cycle is diverse. Agricultural and industrial nitrogen (N) inputs to the environment currently exceed inputs from natural N fixation. As a consequence of anthropogenic inputs, the global nitrogen cycle (Fig. 1) has been significantly altered over the past century. Global atmospheric nitrous oxide (N2O) mole fractions have increased from a pre-industrial value of ~270 nmol/mol to ~319 nmol/mol in 2005. Human activities account for over one-third of N2O emissions, most of which are due to the agricultural sector. This article is intended to give a brief review of the history of anthropogenic N inputs, and reported impacts of nitrogen inputs on selected terrestrial and aquatic ecosystems.

<span class="mw-page-title-main">Trophic state index</span> Measure of the ability of water to sustain biological productivity

The Trophic State Index (TSI) is a classification system designed to rate water bodies based on the amount of biological productivity they sustain. Although the term "trophic index" is commonly applied to lakes, any surface water body may be indexed.

<span class="mw-page-title-main">Wild fisheries</span> Area containing fish that are harvested commercially

A wild fishery is a natural body of water with a sizeable free-ranging fish or other aquatic animal population that can be harvested for its commercial value. Wild fisheries can be marine (saltwater) or lacustrine/riverine (freshwater), and rely heavily on the carrying capacity of the local aquatic ecosystem.

Landscape limnology is the spatially explicit study of lakes, streams, and wetlands as they interact with freshwater, terrestrial, and human landscapes to determine the effects of pattern on ecosystem processes across temporal and spatial scales. Limnology is the study of inland water bodies inclusive of rivers, lakes, and wetlands; landscape limnology seeks to integrate all of these ecosystem types.

<span class="mw-page-title-main">Nutrient pollution</span> Contamination of water by excessive inputs of nutrients

Nutrient pollution, a form of water pollution, refers to contamination by excessive inputs of nutrients. It is a primary cause of eutrophication of surface waters, in which excess nutrients, usually nitrogen or phosphorus, stimulate algal growth. Sources of nutrient pollution include surface runoff from farm fields and pastures, discharges from septic tanks and feedlots, and emissions from combustion. Raw sewage is a large contributor to cultural eutrophication since sewage is high in nutrients. Releasing raw sewage into a large water body is referred to as sewage dumping, and still occurs all over the world. Excess reactive nitrogen compounds in the environment are associated with many large-scale environmental concerns. These include eutrophication of surface waters, harmful algal blooms, hypoxia, acid rain, nitrogen saturation in forests, and climate change.

<span class="mw-page-title-main">Freshwater acidification</span>

Freshwater acidification occurs when acidic inputs enter a body of fresh water through the weathering of rocks, invasion of acidifying gas, or by the reduction of acid anions, like sulfate and nitrate within a lake. Freshwater acidification is primarily caused by sulfur oxides (SOx) and nitrogen oxides (NOx) entering the water from atmospheric depositions and soil leaching. Carbonic acid and dissolved carbon dioxide can also enter freshwaters, in a similar manner associated with runoff, through carbon dioxide-rich soils. Runoff that contains these compounds may incorporate acidifying hydrogen ions and inorganic aluminum, which can be toxic to marine organisms. Acid rain is also a contributor to freshwater acidification. It is created when SOx and NOx react with water, oxygen, and other oxidants within the clouds.

Nutrient cycling in the Columbia River Basin involves the transport of nutrients through the system, as well as transformations from among dissolved, solid, and gaseous phases, depending on the element. The elements that constitute important nutrient cycles include macronutrients such as nitrogen, silicate, phosphorus, and micronutrients, which are found in trace amounts, such as iron. Their cycling within a system is controlled by many biological, chemical, and physical processes.

<span class="mw-page-title-main">Freshwater salinization</span>

Freshwater salinization is the process of salty runoff contaminating freshwater ecosystems, which can harm aquatic species in certain quantities and contaminate drinking water. It is often measured by the increased amount of dissolved minerals than what is considered usual for the area being observed. Naturally occurring salinization is referred to as primary salinization; this includes rainfall, rock weathering, seawater intrusion, and aerosol deposits. Human-induced salinization is termed as secondary salinization, with the use of de-icing road salts as the most common form of runoff. Approximately 37% of the drainage in the United States has been effected by salinization in the past century. The EPA has defined two thresholds for healthy salinity levels in freshwater ecosystems: 230 mg/L Cl for average salinity levels and 860 mg/L Cl for acute inputs.

Many river systems are shaped by human activity and through anthropogenic forces. The process of human influence on nature, including rivers, is stated with the beginning of the Anthropocene, which has replaced the Holocene. This long-term impact is analyzed and explained by a wide range of sciences and stands in an interdisciplinary context. The natural water cycle and stream flow is globally influenced and linked to global interconnections. Rivers are an essential component of the terrestrial realm and have been a preferable location for human settlements during history. River is the main expression used for river channels themselves, riparian zones, floodplains and terraces, adjoining uplands dissected by lower channels and river deltas.

Harp Lake is an oligotrophic, single basin lake in Ontario, Canada. The lake covers over 710,000 m2 and has a depth of 37.5 m. Harp Lake does have dimitic stratification and is a temperate lake. Additionally, Harp Lake does not have anaerobic conditions in the water column because it is a relatively deep lake. The water in Harp Lake has a pH of 6.3. This pH is caused by the presence of acids and the lack of alkaline bases.[3] Slightly acidic lakes normally have a granite or siliceous bedrock and they are poorly buffered. Also, these lakes commonly have calcium-poor soils or thin soils.

References

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  10. The Lake Ontario Shoreline Management Plan
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  12. Love Your Lakes Program
  13. Zuzek, Peter (2020). "Lake Ontario Shoreline Management Plan" (PDF).
  14. Borre, Lisa; Smyth, Robyn L.; Howe, Eric A. (2016). "At the Forefront of Shoreline Management" (PDF).
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