Harp Lake, Ontario

Last updated
Harp Lake
LocationOntario, Canada
Coordinates 45°22′46″N79°08′06″W / 45.37944°N 79.13500°W / 45.37944; -79.13500
Type Oligotrophic lake
Catchment area 4.7 km² (1.12 mi²)
Basin  countriesCanada
Surface area710,000 m² (7,657,690 ft²)
Average depth37.5 m (123.03 ft)
SettlementsNear Dorset, Ontario

Harp Lake is an oligotrophic, single-basin lake in Ontario, Canada. [1] The lake covers over 710,000 m2 and has a depth of 37.5 m. [2] Harp Lake does have dimitic stratification and is a temperate lake. [2] Additionally, Harp Lake does not have anaerobic conditions in the water column because it is a relatively deep lake. [1] The water in Harp Lake has a pH of 6.3 (slightly acidic). [2] 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. [3]

Contents

It is one of the "Dorset lakes" near Dorset, Ontario, a small community located on the boundary between the Algonquin Highlands Township in Haliburton County, Ontario and Lake of Bays Municipality in Muskoka District, Canada.

Ecology

Nutrient levels

The forested watershed area around Harp Lake is around 4.7 km2 and comprises six streams and shoreline runoff. [4] There has been evidence that the total discharge of these six streams has decreased by 24.9% from 1978-2006. [5] Four different concentrations of cations (Ca, K, Mg and Na) were observed in Harp Lake from 1978-2006. There was found to be a negative trend with the nutrients Ca, K and Mg concentrations while Na was found to increase over time. [5] These two trends were correlated with stream base cation concentration, stream discharge and shoreline load. With each cation stream concentration and discharge were a key player with the trends while shoreline load (road salt) played a key role in the increase of Na. [5] Specifically, Na increased between 250% and 350% as a result of road salt contamination. [6]

Not only did Na concentrations increase because of road salt contamination but Cl concentrations also increased. Cl concentrations increased from 0.6 mg*L−1 to 2.7 mg*L−1. [6] While the increased levels of Na and Cl concentrations have caused localized impacts to occur near stream crossing there is a large dilution factor which has caused there to be little impact on the lake ecosystem. The Na and Cl concentrations are predicted to have little to no effect on soft-water organisms even though their tolerance to salt is low. [6]

Oxygen levels

From 1975 to 1995 research was conducted to measure summer hypolimnetic oxygen levels. The hypolimnetic oxygen levels stayed persistently over 4 mg L−1 . [1] Additionally, in 2010, researchers measured total mercury, methyl mercury, total organic carbon, sediment bulk density, redox potential and percent fines on a sediment core. [1] The sediment core was collected from littoral to profundal depths along transects. Total mercury, total organic carbon, and total mercury:methyl mercury ratio decrease with sediment depth. [1]

Muskoka River, Ontario Canada View from the dock, Muskoka River (21007916808).jpg
Muskoka River, Ontario Canada

Geographic features

Harp Lake has been studied by the Dorset Environmental Science Centre since the 1970's. The Dorset Environmental Science Centre includes tributary sampling and a meteorological station. [2] The Dorset Environmental Science Centre have found that the drainage from Harp Lake flows into the Muskoka River and then straight into Lake Huron. [4] There has been an increased thermal stability since 1970 that is caused by the high temperature extremities that occur during summer and fall rather than the length of time Harp Lake has no ice on the surface. During the summer and spring months Harp Lake is known to have significant chrysophyte algae levels that cause a decrease in the amount of light that can penetrate the water which then causes temperature levels to drop in the metalimnion. [2]

The forested watershed is composed of mixed deciduous-conifer forest and the soil is composed of weak developed Spodosols. The weak developed Spodosols are formed from glacial till deposits and the groundwater is located within these glacial till deposits. Within the watershed dissolved organic carbon (DOC) data has been collected since the 1970's. The total DOC within Harp Lake can be estimated from the annual rate of new organic carbon to liter and soil layers, steady state of carbon, and the fragment of decomposition that produces DOC. In the litter layers of Harp Lake the production rate of DOC is between 5 and 750 g C m−2 yr−1. [7] The DOC found in the Harp Lake watershed has three outcomes of remineralization, sorption on mineral surfaces and transport out of the watershed through streams. [7]

Research that was completed in 1996 found that Harp Lake has a high gross settling of steady-state total phosphorus. [8] The cause of the high levels may have been cause by thick glacial tills in the Harp catchment. Also, there have been high septic total phosphorus level that have reach the littoral zone in Harp Lake. It is predicted that septic total phosphorus export will increase if the sorption sites between the lakeshore and the septic fields are not saturated because the available site will become scarce. [8]

Ecosystems

Invasive species

In 1993 Harp Lake was found to have an invasion of Bythotrephes, a type of cladoceran crustacean. There was a high abundance of Bythotrephes in the months of July and August. The invasion of Bythotrephes was shown to decrease zooplankton species richness by 17%. [9] Medium-size cladocerans specifically had a large decline with the presence of Bythotrephes. In contrast to the decrease in zooplankton species richness Bythotrephes have been known to increase the densities of rotifer populations specifically the Conochilus unicornis. [9]

Native species

Harp Lake contains the species Coregonus artedi (cisco) which is a cold-water planktivorous fish. Planktivorous fish ability to hunt is impacted by light availability and the frequency of encounter. [10] Coregonus artedi are normally located in the hypolimnion during the day because they are so dependent on light availability. Coregonus artedi is important when it comes to the regulation of the invasive species Bythotrephes because C. artedi highly prey on them. [10] This relationship has a direct effect on the zooplankton species richness because as Bythotrephes decrease the zooplankton species richness will increase. However, there is evidence that was found in 2003 to refute this argument. Researchers found that in the spring the peak daytime refuge thickness was negative and did not show any correlation to the relationship between C. artedi and Bythotrephes death rates. [10] However in the summer months Coregonus artedi is responsible for 50% of the Bythotrephes mortality. [11]

Perca flavescens (yellow perch) is a warm water planktivorous fish that is found in Harp Lake. Perca flavescens is found to be also responsible for 50% of the Bythotrephes mortality. [11]

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">Limnology</span> Science of inland aquatic ecosystems

Limnology is the study of inland aquatic ecosystems. The study of limnology includes aspects of the biological, chemical, physical, and geological characteristics of fresh and saline, natural and man-made bodies of water. This includes the study of lakes, reservoirs, ponds, rivers, springs, streams, wetlands, and groundwater. Water systems are often categorized as either running (lotic) or standing (lentic).

The pedosphere is the outermost layer of the Earth that is composed of soil and subject to soil formation processes. It exists at the interface of the lithosphere, atmosphere, hydrosphere and biosphere. The pedosphere is the skin of the Earth and only develops when there is a dynamic interaction between the atmosphere, biosphere, lithosphere and the hydrosphere. The pedosphere is the foundation of terrestrial life on Earth.

<span class="mw-page-title-main">Ward Creek (Lake Tahoe)</span> River in California, United States

Ward Creek is a 6.1-mile (9.8 km) eastward-flowing stream in Placer County, California, United States. The creek flows into Lake Tahoe 2.7 miles (4.3 km) south of Tahoe City, California, and has undergone extensive restoration to reduce sediment and surface run-off to maintain the purity of Lake Tahoe.

<span class="mw-page-title-main">Lake ecosystem</span> Type of ecosystem

A lake ecosystem or lacustrine ecosystem includes biotic (living) plants, animals and micro-organisms, as well as abiotic (non-living) physical and chemical interactions. Lake ecosystems are a prime example of lentic ecosystems, which include ponds, lakes and wetlands, and much of this article applies to lentic ecosystems in general. Lentic ecosystems can be compared with lotic ecosystems, which involve flowing terrestrial waters such as rivers and streams. Together, these two ecosystems are examples of freshwater ecosystems.

<i>Coregonus hoyi</i> Species of fish

Coregonus hoyi, also known as the bloater, is a species or form of freshwater whitefish in the family Salmonidae. It is a silvery-coloured herring-like fish, 25.5 centimetres (10.0 in) long. It is found in most of the Great Lakes and in Lake Nipigon, and inhabits underwater slopes. This fish is not to be confused with the extinct deepwater cisco, a large fish that shared a common name with the bloater.

<span class="mw-page-title-main">Shortjaw cisco</span> Species of fish

The shortjaw cisco is a North-American freshwater whitefish in the salmon family. Adult fish range to about 30 cm (12 in) in length and are silver, tinged with green above and paler below. One of the members of the broader Coregonus artedi complex of ciscoes, it is distributed widely in the deeper lakes of Canada, but populations in the Great Lakes have been declining and it is no longer present in Lakes Michigan, Huron, and Erie. It feeds mainly on crustaceans and insect larvae and spawns in the autumn on the lake bed. It is part of the important cisco (chub) fishery in the Great Lakes. The International Union for Conservation of Nature has rated its conservation status as "vulnerable". Shortjaw cisco have however evolved from the cisco Coregonus artedi independently in different lakes and different parts of the range, and conservation assessments therefore should be made on a lake-wise rather than range-wide basis.

<i>Coregonus artedi</i> Species of fish

Coregonus artedi, commonly known as the cisco, is a North American species of freshwater whitefish in the family Salmonidae. The number of species and definition of species limits in North American ciscoes is a matter of debate. Accordingly, Coregonus artedi may refer either in a narrow sense to one of the several types of cisco found e.g. in the Great Lakes, or in a broad sense to the complex of all ciscoes in continental North American lakes, Coregonus artedi sensu lato.

<span class="mw-page-title-main">American gizzard shad</span> Species of fish

The American gizzard shad, also known as the mud shad, is a member of the herring family of fish and is native to large swaths of fresh and brackish waters in the United States of America, as well as portions of Quebec, Canada, and Mexico. The adult has a deep body, with a silvery-green coloration above fading to plain silver below. The gizzard shad commonly resides in freshwater lakes, reservoirs, rivers, and streams but can also reside in brackish waters, as it does on the Atlantic coast of the United States. Their range is across most of the continental United States, although they typically go no further north than New York and no further west than New Mexico. They are a large part of many of the ecosystems they inhabit and can drive changes in phyto- and zooplankton, thereby indirectly affecting other planktivorous fishes. The gizzard shad has been widely used as a food source for game fish, with varied success in management and effectiveness.

<span class="mw-page-title-main">Phosphorus cycle</span> Biogeochemical movement

The phosphorus cycle is the biogeochemical cycle that describes the movement of phosphorus through the lithosphere, hydrosphere, and biosphere. Unlike many other biogeochemical cycles, the atmosphere does not play a significant role in the movement of phosphorus, because phosphorus and phosphorus-based compounds are usually solids at the typical ranges of temperature and pressure found on Earth. The production of phosphine gas occurs in only specialized, local conditions. Therefore, the phosphorus cycle should be viewed from whole Earth system and then specifically focused on the cycle in terrestrial and aquatic systems.

<i>Bythotrephes longimanus</i> Spiny water flea

Bythotrephes longimanus, or the spiny water flea, is a planktonic crustacean less than 15 millimetres (0.6 in) long. It is native to fresh waters of Northern Europe and Asia, but has been accidentally introduced and widely distributed in the Great Lakes area of North America since the 1980s. Bythotrephes is typified by a long abdominal spine with several barbs which protect it from predators.

Biodilution, sometimes referred to as bloom dilution, is the decrease in concentration of an element or pollutant with an increase in trophic level. This effect is primarily observed during algal blooms whereby an increase in algal biomass reduces the concentration of pollutants in organisms higher up in the food chain, like zooplankton or daphnia.

<span class="mw-page-title-main">Trout Creek (Lake Tahoe)</span> River in California, United States

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<span class="mw-page-title-main">Hypoxia (environmental)</span> Low oxygen conditions or levels

Hypoxia refers to low oxygen conditions. Normally, 20.9% of the gas in the atmosphere is oxygen. The partial pressure of oxygen in the atmosphere is 20.9% of the total barometric pressure. In water, oxygen levels are much lower, approximately 7 ppm or 0.0007% in good quality water, and fluctuate locally depending on the presence of photosynthetic organisms and relative distance to the surface.

<span class="mw-page-title-main">Planktivore</span> Aquatic organism that feeds on planktonic food

A planktivore is an aquatic organism that feeds on planktonic food, including zooplankton and phytoplankton. Planktivorous organisms encompass a range of some of the planet's smallest to largest multicellular animals in both the present day and in the past billion years; basking sharks and copepods are just two examples of giant and microscopic organisms that feed upon plankton. Planktivory can be an important mechanism of top-down control that contributes to trophic cascades in aquatic and marine systems. There is a tremendous diversity of feeding strategies and behaviors that planktivores utilize to capture prey. Some planktivores utilize tides and currents to migrate between estuaries and coastal waters; other aquatic planktivores reside in lakes or reservoirs where diverse assemblages of plankton are present, or migrate vertically in the water column searching for prey. Planktivore populations can impact the abundance and community composition of planktonic species through their predation pressure, and planktivore migrations facilitate nutrient transport between benthic and pelagic habitats.

Legacy sediment (LS) is depositional bodies of sediment inherited from the increase of human activities since the Neolithic. These include a broad range of land use and land cover changes, such as agricultural clearance, lumbering and clearance of native vegetation, mining, road building, urbanization, as well as alterations brought to river systems in the form of dams and other engineering structures meant to control and regulate natural fluvial processes (erosion, deposition, lateral migration, meandering). The concept of LS is used in geomorphology, ecology, as well as in water quality and toxicological studies.

<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.

Lake 226 is one lake in Canada's Experimental Lakes Area (ELA) in Ontario. The ELA is a freshwater and fisheries research facility that operated these experiments alongside Fisheries and Oceans Canada and Environment Canada. In 1968 this area in northwest Ontario was set aside for limnological research, aiming to study the watershed of the 58 small lakes in this area. The ELA projects began as a response to the claim that carbon was the limiting agent causing eutrophication of lakes rather than phosphorus, and that monitoring phosphorus in the water would be a waste of money. This claim was made by soap and detergent companies, as these products do not biodegrade and can cause buildup of phosphates in water supplies that lead to eutrophication. The theory that carbon was the limiting agent was quickly debunked by the ELA Lake 227 experiment that began in 1969, which found that carbon could be drawn from the atmosphere to remain proportional to the input of phosphorus in the water. Experimental Lake 226 was then created to test phosphorus' impact on eutrophication by itself.

<span class="mw-page-title-main">Peter and Paul Lakes</span> Lake in Michigan

Paul and Peter are two connected lakes located in Michigan's upper peninsula near the Wisconsin border in Vilas County (WI) and Gogebic County (MI). Paul and Peter are kettle lakes, which is a type of lake formed by glaciers. Peter Lake is larger with an area of 6.24 acres and a maximum depth of 19.6 meters while Paul Lake has an area of 4.12 acres and a maximum depth of 15 meters. The lakes are a part of the University of Notre Dame Environmental Research Center (UNDERC). The lakes, bogs, streams, and marshes of the UNDERC are located within deciduous and coniferous forests. The surrounding forest is made up mostly of sugar maple, yellow birch, and balsam fir. The two lakes are ideal for performing whole lake experiments since one lake can receive treatments while the other can remain a control. No fishing is allowed making the two connected lakes ideal for studying their fish populations. The lakes' basins are also located within the UNDERC meaning that no outside interference can occur. The lakes are dimictic, freezing in November and mixing in the fall and again partially mixing in the spring.

<span class="mw-page-title-main">Lake 227</span> Lake in Ontario, Canada

References

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