Aquatic biomonitoring

Last updated
Bodo Creek, Nigeria. An environmental impact assessment and biomonitoring scientist returning from a sampling expedition at an oil spill site on Bodo Creek in the Niger River Delta. Bodo Creek.jpg
Bodo Creek, Nigeria. An environmental impact assessment and biomonitoring scientist returning from a sampling expedition at an oil spill site on Bodo Creek in the Niger River Delta.

Aquatic biomonitoring is the science of inferring the ecological condition of rivers, lakes, streams, and wetlands by examining the organisms (fish, invertebrates, insects, plants, and algae) that live there. While aquatic biomonitoring is the most common form of biomonitoring, any ecosystem can be studied in this manner.

Contents

Purpose

Shasta dam construction, California, U.S.A. Construction and human development can affect many aspects of aquatic ecosystems. Shasta dam under construction new edit.jpg
Shasta dam construction, California, U.S.A. Construction and human development can affect many aspects of aquatic ecosystems.
Champagne, France. Farming and agriculture can greatly affect nearby water sources, both fresh and marine. Vaches dans les champs -Cows in the fields.jpg
Champagne, France. Farming and agriculture can greatly affect nearby water sources, both fresh and marine.

Aquatic biomonitoring is an important tool for assessing aquatic life forms and their habitats. It can reveal the overall health and status of the ecosystem, detect environmental trends and the impacts of different stressors, and can be used to evaluate the effect that various human activities have on the overall health of aquatic environments. [1] [2] Water pollution and general stresses to aquatic life have a major impact on the environment. The main sources of pollution to oceans, rivers, and lakes are human caused events or activities, such as sewage, oil spills, surface runoff, littering, ocean mining, and nuclear waste.

Monitoring aquatic life can also be beneficial in monitoring and understanding adjacent land ecosystems. Rapid changes to an environment, like, pollution, can alter ecosystems and community assemblages, and endanger species that live in or close to water. Many aquatic species serve as food sources for terrestrial species, which are therefore impacted by the size and health of aquatic populations.

Indicator organisms

Scotland, UK. Caddis fly spp. larvae are a common indicator organism in determining a fresh waterbody's health. Caddis fly larva sp - Flickr - S. Rae.jpg
Scotland, UK. Caddis fly spp. larvae are a common indicator organism in determining a fresh waterbody's health.
A well developed wood frog tadpole. Amphibians at all stages of life are significant indicator organisms. Wood frog tadpole.jpg
A well developed wood frog tadpole. Amphibians at all stages of life are significant indicator organisms.

Aquatic invertebrates, most popularly the larvae of the caddis fly sp., are responsive to climate change, low levels of pollution and temperature change. [3] [4] As a result, they have the longest history of use in biomonitoring programs. [5] Additionally, macroscopic species: frogs, fish, and some plant species, as well as, many forms of microscopic life, like bacteria and protozoa are used as indicator organisms in a variety of applications, storm water run-off among them. [6]

Many species of Macroalgae (including Cyanobacteria, though not technically a true algae [7] ) are also used in biomonitoring for both aquatic and marine environments, as their short lifespan makes them very reactive to changes. [8] [9]

Common methods

A biomonitoring assessment requires a baseline dataset which, ideally, defines the environment in its natural or default state. [10] This is then used for comparison against any subsequent measurements, in order to assess potential alterations or trends.

In some cases, these datasets are used to create standardised tools for assessing water quality via biomonitoring data, such as the Specific Pollution Index (SPI) and South African Diatom Index (SADI). [11]

Methods employed in aquatic biomonitoring

Common tools of ecological and biological assessments

Variables considered

Water quality

Water quality is graded both on appearance, for example: clear, cloudy, full of algae, and chemistry. [16] Determining the specific levels of enzymes, bacteria, metals, and minerals found in water is extremely important. Some contaminants, such as metals and certain organic wastes, can be lethal to individual creatures and could thereby ultimately lead to extinction of certain species. [12] This could affect both aquatic and land ecosystems and cause disruption in other biomes and ecosystems.

Water temperature

Water body temperature is one of the most ubiquitous variables collected in aquatic biomonitoring. Temperatures at the water surface, through the water column, and in the lowest levels of the water body (benthic zone) can all provide insight into different aspects of an aquatic ecosystem. Water temperature is directly affected by climate change and can have negative affects on many aquatic species, such as salmon. [17] [18] Salmon spawning is temperature dependant: there is a heat accumulation threshold which must be reached before hatching can occur. Post-hatching, salmon live in water within a critical range in temperature, with exposure to temperatures outside of this being potentially lethal. [19] This sensitivity makes them useful indicators of changes in water temperature, hence their use in climate change studies. Similarly, Daphnia populations have been evidenced as being negatively affected by climate change, as earlier springs have caused hatching periods to de-couple from the peak window of food availability. [20]

Community make-up

Species community assemblages and changes therein can help researchers to infer changes in the health of an ecosystem. In typical unpolluted temperate streams of Europe and North America, certain insect taxa predominate. Mayflies (Ephemeroptera), caddisflies (Trichoptera), and stoneflies (Plecoptera) are the most common insects in these undisturbed streams. In contrast, in rivers disturbed by urbanization, agriculture, forestry, and other perturbations, flies (Diptera), and especially midges (family Chironomidae) predominate.

Local geology

Surface water can be affected by local geology, as minerals leached from sub-surface rocks can enter surface water bodies and influence water chemistry. Examples of this are the Werii River (Tigray, Ethiopia), where elevated concentrations of heavy metals have been linked to the underlying slate, and drinking wells in Indigenous communities near Anchorage, Alaska, where high concentrations of arsenic have been linked to the underlying McHugh Complex rock formation. [21]

Limitations

See also

Related Research Articles

<span class="mw-page-title-main">Water quality</span> Assessment against standards for use

Water quality refers to the chemical, physical, and biological characteristics of water based on the standards of its usage. It is most frequently used by reference to a set of standards against which compliance, generally achieved through treatment of the water, can be assessed. The most common standards used to monitor and assess water quality convey the health of ecosystems, safety of human contact, extent of water pollution and condition of drinking water. Water quality has a significant impact on water supply and oftentimes determines supply options.

<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">Aquatic animal</span> Animal that lives in water for most or all of its lifetime

An aquatic animal is any animal, whether vertebrate or invertebrate, that lives in water for all or most of its lifetime. Many insects such as mosquitoes, mayflies, dragonflies and caddisflies have aquatic larvae, with winged adults. Aquatic animals may breathe air or extract oxygen from water through specialised organs called gills, or directly through the skin. Natural environments and the animals that live in them can be categorized as aquatic (water) or terrestrial (land). This designation is polyphyletic.

Freshwater ecosystems are a subset of Earth's aquatic ecosystems. They include lakes, ponds, rivers, streams, springs, bogs, and wetlands. They can be contrasted with marine ecosystems, which have a larger salt content. Freshwater habitats can be classified by different factors, including temperature, light penetration, nutrients, and vegetation. There are three basic types of freshwater ecosystems: Lentic, lotic and wetlands. Freshwater ecosystems contain 41% of the world's known fish species.

<span class="mw-page-title-main">Aquatic toxicology</span> Study of manufactured products on aquatic organisms

Aquatic toxicology is the study of the effects of manufactured chemicals and other anthropogenic and natural materials and activities on aquatic organisms at various levels of organization, from subcellular through individual organisms to communities and ecosystems. Aquatic toxicology is a multidisciplinary field which integrates toxicology, aquatic ecology and aquatic chemistry.

<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">Bioindicator</span> Species that reveals the status of an environment

A bioindicator is any species or group of species whose function, population, or status can reveal the qualitative status of the environment. The most common indicator species are animals. For example, copepods and other small water crustaceans that are present in many water bodies can be monitored for changes that may indicate a problem within their ecosystem. Bioindicators can tell us about the cumulative effects of different pollutants in the ecosystem and about how long a problem may have been present, which physical and chemical testing cannot.

RIVPACS is an aquatic biomonitoring system for assessing water quality in freshwater rivers in the United Kingdom. It is based on the macroinvertebrate species found at the study site during sampling. Some of these species are tolerant to pollution, low dissolved oxygen, and other stressors, but others are sensitive; organisms vary in their tolerances. Therefore, different species will usually be found, in different proportions, at different river sites of varying quality. Some organisms are especially good indicator species. The species found at the reference sites collectively make up the species assemblage for that site and are the basis for a statistical comparison between reference sites and non-reference sites. The comparison between the expected species and the observed species can then be used to estimate this aspect of the ecological health of a river.

<span class="mw-page-title-main">Aquatic ecosystem</span> Ecosystem in a body of water

An aquatic ecosystem is an ecosystem found in and around a body of water, in contrast to land-based terrestrial ecosystems. Aquatic ecosystems contain communities of organisms—aquatic life—that are dependent on each other and on their environment. The two main types of aquatic ecosystems are marine ecosystems and freshwater ecosystems. Freshwater ecosystems may be lentic ; lotic ; and wetlands.

Biological integrity is associated with how "pristine" an environment is and its function relative to the potential or original state of an ecosystem before human alterations were imposed. Biological integrity is built on the assumption that a decline in the values of an ecosystem's functions are primarily caused by human activity or alterations. The more an environment and its original processes are altered, the less biological integrity it holds for the community as a whole. If these processes were to change over time naturally, without human influence, the integrity of the ecosystem would remain intact. The integrity of the ecosystem relies heavily on the processes that occur within it because those determine what organisms can inhabit an area and the complexities of their interactions. Most of the applications of the notion of biological integrity have addressed aquatic environments, but there have been efforts to apply the concept to terrestrial environments. Determining the pristine condition of the ecosystem is in theory scientifically derived, but deciding which of the many possible states or conditions of an ecosystem is the appropriate or desirable goal is a political or policy decision and is typically the focus of policy and political disagreements. Ecosystem health is a related concept but differs from biological integrity in that the "desired condition" of the ecosystem or environment is explicitly based on the values or priorities of society.

An index of biological integrity (IBI), also called an index of biotic integrity, is a scientific tool typically used to identify and classify water pollution problems, although there have been some efforts to apply the idea to terrestrial environments. An IBI associates anthropogenic influences on a water body with biological activity in the water body, and is formulated using data developed from biosurveys. Biological integrity is associated with how "pristine" an environment is and its function relative to the potential or original state of an ecosystem before human alterations were imposed. Biological integrity is built on the assumption that a decline in the values of an ecosystem's functions are primarily caused by human activity or alterations. The more an environment and its original processes are altered, then by definition, the less biological integrity it holds for the community as a whole. If these processes were to change over time naturally, without human influence, the integrity of the ecosystem would remain intact. Similar to the concept of ecosystem health, the integrity of the ecosystem relies heavily on the processes that occur within it because those determine which organisms can inhabit an area and the complexities of their interactions. Deciding which of the many possible states or conditions of an ecosystem is appropriate or desirable is a political or policy decision.

A biotic index is a scale for showing the quality of an environment by indicating the types and abundances of organisms present in a representative sample of the environment. It is often used to assess the quality of water in marine and freshwater ecosystems. Numerous biotic indices have been created to account for the indicator species found in each region of study. The concept of the biotic index was developed by Cherie Stephens in an effort to provide a simple measurement of stream pollution and its effects on the biology of the stream.

<span class="mw-page-title-main">Freshwater biology</span> The scientific study of freshwater ecosystems and biology

Freshwater biology is the scientific biological study of freshwater ecosystems and is a branch of limnology. This field seeks to understand the relationships between living organisms in their physical environment. These physical environments may include rivers, lakes, streams, ponds, lakes, reservoirs, or wetlands. Knowledge from this discipline is also widely used in industrial processes to make use of biological processes involved with sewage treatment and water purification. Water presence and flow is an essential aspect to species distribution and influences when and where species interact in freshwater environments.

<span class="mw-page-title-main">Biosurvey</span> Scientific study of organisms to assess the condition of an ecological resource

A biosurvey, or biological survey, is a scientific study of organisms to assess the condition of an ecological resource, such as a water body.

<span class="mw-page-title-main">Freshwater environmental quality parameters</span>

Freshwater environmental quality parameters are those chemical, physical or biological parameters that can be used to characterise a freshwater body. Because almost all water bodies are dynamic in their composition, the relevant quality parameters are typically expressed as a range of expected concentrations.

<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.

<span class="mw-page-title-main">Glacial stream</span> Body of liquid water that flows down a channel formed by a glacier

A glacier stream is a channelized area that is formed by a glacier in which liquid water accumulates and flows. Glacial streams are also commonly referred to as "glacier stream" or/and "glacial meltwater stream". The movement of the water is influenced and directed by gravity and the melting of ice. The melting of ice forms different types of glacial streams such as supraglacial, englacial, subglacial and proglacial streams. Water enters supraglacial streams that sit at the top of the glacier via filtering through snow in the accumulation zone and forming slush pools at the FIRN zone. The water accumulates on top of the glacier in supraglacial lakes and into supraglacial stream channels. The meltwater then flows through various different streams either entering inside the glacier into englacial channels or under the glacier into subglacial channels. Finally, the water leaves the glacier through proglacial streams or lakes. Proglacial streams do not only act as the terminus point but can also receive meltwater. Glacial streams can play a significant role in energy exchange and in the transport of meltwater and sediment.

<span class="mw-page-title-main">Macroinvertebrate Community Index</span> An indicator of water quality and overall stream health

Macroinvertebrate Community Index (MCI) is an index used in New Zealand to measure the water quality of fresh water streams. The presence or lack of macroinvertebrates such as insects, worms and snails in a river or stream can give a biological indicator on the health of that waterway. The MCI assigns a number to each species of macroinvertebrate based on the sensitivity of that species to pollution. The index then calculates an average score. A higher score on the MCI generally indicates a more healthy stream.

<span class="mw-page-title-main">Algae DNA barcoding</span> Technique used for species identification and phylogenetic studies

DNA barcoding of algae is commonly used for species identification and phylogenetic studies. Algae form a phylogenetically heterogeneous group, meaning that the application of a single universal barcode/marker for species delimitation is unfeasible, thus different markers/barcodes are applied for this aim in different algal groups.

<span class="mw-page-title-main">Fresh water</span> Naturally occurring water with low amounts of dissolved salts

Fresh water or freshwater is any naturally occurring liquid or frozen water containing low concentrations of dissolved salts and other total dissolved solids. Although the term specifically excludes seawater and brackish water, it does include non-salty mineral-rich waters such as chalybeate springs. Fresh water may encompass frozen and meltwater in ice sheets, ice caps, glaciers, snowfields and icebergs, natural precipitations such as rainfall, snowfall, hail/sleet and graupel, and surface runoffs that form inland bodies of water such as wetlands, ponds, lakes, rivers, streams, as well as groundwater contained in aquifers, subterranean rivers and lakes. Fresh water is the water resource that is of the most and immediate use to humans.

References

  1. Vandewalle1 de Belo2 Berg3, M.1 F.2 M.P.3 (September 2010). "Functional traits as indicators of biodiversity response to land use changes across ecosystems and Organisms" (PDF). Biodivers Conserv. 19 (10): 2921–2947. doi:10.1007/s10531-010-9798-9. S2CID   9567019.{{cite journal}}: CS1 maint: numeric names: authors list (link)
  2. "Why Biological Monitoring?". Monitoring and Assessment. Augusta, ME: Maine Department of Environmental Protection. Retrieved 2020-03-27.
  3. Justin E. Lawrence; Kevin B. Lunde; Raphael D. Mazor; Leah A. Bêche; Eric P. McElravy; Vincent H. Resh. "Long-Term Macroinvertebrate Responses to Climate Change: Implications for Biological Assessment in Mediterranean-Climate Streams". Journal of the North American Benthological Society.
  4. "Vulnerability of stream biota to climate change in mediterraneanclimates: a synthesis of ecological responses and conservation challenges". Hydrobiologia. doi:10.1007/s10750-012-1244-4. hdl: 2445/48186 . S2CID   17658477.
  5. Barbour1 Gerritsen2 Snyder3 Stribling4, M.T.1 J.2 B.D3 J.B4 (1999). "Rapid Bioassessment Protocols for Use in Streams and Wadeable Rivers: Periphyton, Benthic Macroinvertebrates and Fish". U.S. Environmental Protection Agency (EPA); Office of Water.{{cite journal}}: CS1 maint: numeric names: authors list (link)
  6. Jeng1 England2 Bradford3, Hueiwang C.1 Andrew J.2 Henry B.3 (2005). "Indicator Organisms Associated with Stormwater Suspended Particles and Estuarine Sediment". Journal of Environmental Science and Health. 40 (4): 779–791. Bibcode:2005JESHA..40..779J. doi:10.1081/ESE-200048264. PMID   15792299. S2CID   217506461.{{cite journal}}: CS1 maint: numeric names: authors list (link)
  7. Stanier, R Y; Kunisawa, R; Mandel, M; Cohen-Bazire, G (June 1971). "Purification and properties of unicellular blue-green algae (order Chroococcales)". Bacteriological Reviews. 35 (2): 171–205. doi:10.1128/br.35.2.171-205.1971. ISSN   0005-3678. PMC   378380 . PMID   4998365.
  8. "Why Biological Monitoring? -- Monitoring and Assessment, Bureau of Land and Water Quality, Maine Department of Environmental Protection". www.maine.gov. Retrieved 2023-02-24.
  9. Phillips, David J.H. (December 1979). "The Use of Biological Indicator Organisms to Monitor Trace Metal Pollution in Marine and Estuarine Environments--A Review". Environmental Pollution. 20 (4): 281–317. doi:10.1016/0013-9327(77)90047-7.
  10. Burrows, Justin M.; Clawson, Chelsea M. (September 2020). Baseline Aquatic Biomonitoring for the Anarraaq and Aktigiruq Prospects near the Red Dog Mine, 2019 (PDF) (Report). Fairbanks, AK: Alaska Department of Fish and Game. Technical Report No. 20-06.
  11. Harding, W. R. (2011). The South African Diatom Index (SADI) : a preliminary index for indicating water quality in rivers and streams in southern Africa : report to the Water Research Commission. J. C. Taylor, South Africa. Water Research Commission. [Gezina]: Water Research Commission. ISBN   978-1-4312-0172-3. OCLC   802315993.
  12. 1 2 Bartram, Jamie; Ballance, Richard, eds. (1996). Water Quality Monitoring: A Practical Guide to the Design and Implementation of Freshwater Quality Studies and Monitoring Programmes. CRC Press. ISBN   978-0419217305.
  13. Karr, James R. (1981). "Assessment of Biotic Integrity Using Fish Communities". Fisheries. American Fisheries Society. 6 (6): 21–27. doi:10.1577/1548-8446(1981)006<0021:AOBIUF>2.0.CO;2.
  14. Burger, Joanna; Snodgrass, Joel (June 2001). "Metal Levels in Southern Leopard Frogs from the Savannah River Site: Location and Body Compartment Effects". Environmental Research. Elsevier. 86 (2): 157–166. Bibcode:2001ER.....86..157B. doi:10.1006/enrs.2001.4245. PMID   11437462.
  15. "MolluScan Eye". Environnements et Paléoenvironnements Océaniques et Continentaux.
  16. "Biomonitoring". Water Quality Monitoring & Assessment. Troy, NY: New York State Department of Environmental Conservation. Retrieved 2021-03-16.
  17. Van Vliet, Michelle T.H.; Wietse, H.P. Franssen; Yearsley, John R.; Ludwig, Fulco; Haddeland, Ingjerd; Letenmaier, Dennis P.; Kabat, Pavel (April 2013). "Global river discharge and water temperature under climate change". Global Climate Change. Elsevier. 23 (2): 450–464. doi:10.1016/j.gloenvcha.2012.11.002.
  18. Jonsson, B.; Jonsson, N. (January 2010). "A review of the likely effects of climate change on anadromous Atlantic salmon Salmo salar and brown trout Salmo trutta, with particular reference to water temperature and flow". Journal of Fish Biology. The Fisheries Society of the British Isles. 75 (10): 2381–2447. doi:10.1111/j.1095-8649.2009.02380.x. PMID   20738500.
  19. Jonsson, B.; Jonsson, N. (December 2009). "A review of the likely effects of climate change on anadromous Atlantic salmon Salmo salar and brown trout Salmo trutta, with particular reference to water temperature and flow". Journal of Fish Biology. 75 (10): 2381–2447. doi:10.1111/j.1095-8649.2009.02380.x. PMID   20738500.
  20. Winder, Monika; Schindler, Daniel E. (August 2004). "Climate Change Uncouples Trophic Interactions in an Aquatic Ecosystem". Ecology. 85 (8): 2100–2106. doi:10.1890/04-0151. ISSN   0012-9658.
  21. Haftu, Zelealem; Estifanos, Samuel (2020-05-12). "Investigation of physico-chemical Characteristics and Heavy Metals Concentration Implying to the Effect of Local Geology on Surface Water Quality of Werii Catchment, Tigray, Ethiopia". EQA - International Journal of Environmental Quality. 40: 11–18. doi:10.6092/issn.2281-4485/10602. ISSN   2281-4485.
  22. CABIN laboratory methods : processing, taxonomy, and quality control of benthic macroinvertebrate samples. Canada. Environment and Climate Change Canada. Gatineau, QC. 2020. ISBN   978-0-660-37046-0. OCLC   1231735778.{{cite book}}: CS1 maint: location missing publisher (link) CS1 maint: others (link)
  23. Landres, Peter B.; Verner, Jared; Thomas, Jack Ward (December 1988). "Ecological Uses of Vertebrate Indicator Species: A Critique". Conservation Biology. 2 (4): 316–328. doi:10.1111/j.1523-1739.1988.tb00195.x. ISSN   0888-8892.
  24. Kerby, Jacob L.; Richards-Hrdlicka, Kathryn L.; Storfer, Andrew; Skelly, David K. (January 2010). "An examination of amphibian sensitivity to environmental contaminants: are amphibians poor canaries?". Ecology Letters. 13 (1): 60–67. doi:10.1111/j.1461-0248.2009.01399.x. PMID   19845728.