Assimilative capacity

Last updated

Assimilative capacity is the ability for pollutants to be absorbed by an environment without detrimental effects to the environment or those who use of it. [1] Natural absorption into an environment is achieved through dilution, dispersion and removal through chemical or biological processes. [1] The term assimilative capacity has been used interchangeably with environmental capacity, receiving capacity and absorptive capacity. [2] It is used as a measurement perimeter in hydrology, meteorology and pedology for a variety of environments examples consist of: lakes, rivers, oceans, cities and soils. Assimilative capacity is a subjective measurement that is quantified by governments and institutions such as Environmental Protection Agency (EPA) of environments into guidelines. [3] [4] Using assimilative capacity as a guideline can help the allocation of resources while reducing the impact on organisms in an environment. [5] This concept is paired with carrying capacity in order to facilitate sustainable development of city regions. [1] Assimilative capacity has been critiqued as to its effectiveness due to ambiguity in its definition that can confuses readers and false assumptions that a small amount of pollutants has no harmful effect on an environment. [6]

Contents

Assimilative Capacity Diagram Assimilative Capacity Diagram.png
Assimilative Capacity Diagram

Hydrosphere

Ocean Waves Waves in pacifica 1.jpg
Ocean Waves
Creek (Buffalo, Wyoming, US) Clear Creek (Buffalo, Wyoming, USA) (1 June 2017) 5 (34657590880).jpg
Creek (Buffalo, Wyoming, US)

Assimilative capacity in hydrology is defined as the maximum amount of contaminating pollutants that a body of water can naturally absorb without exceeding the water quality guidelines and criteria. This determines the concentration of pollutants that can cause detrimental effects on aquatic life and humans that use it. [4] [7] Self-purification and dilution are the main factors effecting the total amount of assimilative capacity a body of water has. [1] Estimations of breaches of assimilative capacity focus on the health of aquatic organisms in order to predict an excess of pollutants in a body of water. Dilution is the main way that bodies of water reduce the concentration of contaminants to levels under their assimilative capacity. [1] This means that body of water that move rapidly or have a large volume of water will have larger assimilative capacities then a slow-moving stream.

Coastal and Marine

Coastal and Marine environments will have much greater assimilative capacity due to the large volumes of water creating a much greater dilution factor. Contaminants added into areas would be needed in much greater volumes in order to exceed the assimilative capacity and create harmful negative effects on aquatic life. However, oceans often are the end point for many pollutants resulting in large accumulation of pollutants. It is estimated that “270 tonnes of nitrogen enter the sea annually” in Western Australia. [2]

Rivers

Rivers have a large focus on being monitored as they are the primary place for runoff from agricultural industries. This results in there being large changes in their original conditions. Agricultural runoff is high in contaminants including Phosphorus and Nitrogen. When phosphorus is added to a river eutrophication occurs a rapid production of algae that’s production was previously limited by the amount of phosphorus in the water. [8] These algae have a high biochemical oxygen demand and reduce the available oxygen for other aquatic organisms. Close monitoring of the assimilative capacity or rivers is needed in order to stop eutrophication which can result in the loss of many aquatic organism.

Atmosphere

Earth's atmosphere Top of Atmosphere.jpg
Earth's atmosphere

Assimilative capacity of the atmosphere is defined as the maximum load of pollutants that can be added without compromise of its resources. Meteorologists calculate assimilative capacity through the atmosphere using ventilation coefficient or through the pollution potential. [9] The ventilation coefficient is calculated by multiply the mixing height (the height at which vigorous mixing of gasses occur) with the average wind speed. [1] [9] Atmospheric concentrations change rapidly as gasses move due to winds, convection current and dispersion of gasses. The pollution potential is determined by calculating the concentration of pollutants and comparing that to the acceptable limits. [9] This way of calculating takes into consideration the current level of pollutants and assesses how much more can be added in order to reach the assimilative capacity. Sulphur dioxide (SO2), Nitrogen monoxide (NO) and Nitrogen dioxide (NO2) and suspended particulate matter (SPM) are important pollutants to measure. High concentrations sulphur dioxide can cause acid rain which damages structures and increases acidity of soils and bodies of water. High concentrations nitrogen monoxide and nitrogen dioxide can cause photochemical smog which has adverse effects on those with compromised lungs. High concentrations of suspended particulate matter can be absorbed by the lungs into the bloodstream can cause pneumonia. [10]

Uses to determine management of environments

Assimilative capacity is used as a monitoring guideline for sustainable growth of city regions. Assimilative capacity allows governments to understand how much pressure a region is under. Working within the assimilative capacity means that regions will be constructed with future stability in mind. “An assimilative capacity study develops specific scientific modelling to support and assist municipalities and other legislative authorities in predicting the impacts of land use”. [11]

United States

In the United States legislation on assimilative capacity as a guideline for the maximum amount of pollutants to be added to bodies of water comes from each individual state and from the environmental protection agency. [12] Assimilative capacity is a quantitatively useful concept codified in the Clean Water Act and other laws and regulations that is unrelated to the perception of an environmental crisis. Assimilative capacity specifically refers to the capacity for a body of water to absorb constituents without exceeding a specific concentration, such as a water quality objective. Water quality objectives are set and periodically revised by regulatory agencies, such as the Environmental Protection Agency (EPA), to define the limits of water quality for different uses, which include human health, but also other ecologically important functions, wildlife habitat, irrigated agriculture, etc. For example, if the irrigation water quality objective for salt is 450 mg/L of total dissolved solids, the assimilative capacity of a body of water would be the amount of salt that could be added to the water such that its concentration would not exceed 450 mg/L.

India

India uses assimilative capacity in management of land, water and air. [1] [9] Though each have largely varying assimilative capacities due to variations in type of pollutants and the difference in dilution dispersion and chemical and biological breakdown in differing environments.

Comparison to accommodative capacity

Assimilative capacity has been critiqued as to the value it adds as a tool for creating guidelines in hydrology. There is a large amount of ambiguity in the definition as it is subjective. It has been questioned as to what exactly statements such as whether harmful to aquatic organism means “death of individual organisms, elimination of food chains, or a change in energy flow patterns”. [6] Inconsistency in assimilative capacity has led to the term to be restricted by the National Oceanic and Atmospheric Administration (NOAA) and Environmental Protection Agency (EPA). Accommodative capacity is used to mean “the rate at which waste material can be added to a body of water in such a way that the ambient concentration of contaminants is maintained below levels that produce unacceptable biological impact”. [13] Accommodative capacity has been suggested to remove ambiguity as uses of it have been more greatly defined in quantitative numbers.

See also

Related Research Articles

<span class="mw-page-title-main">Pollutant</span> Substance or energy damaging to the environment

A pollutant or novel entity is a substance or energy introduced into the environment that has undesired effects, or adversely affects the usefulness of a resource. These can be both naturally forming or anthropogenic in origin. Pollutants result in environmental pollution or become public health concerns when they reach a concentration high enough to have significant negative impacts.

<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">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 toxicology</span>

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">Biomagnification</span> Process of progressive accumulation in food chain

Biomagnification, also known as bioamplification or biological magnification, is the increase in concentration of a substance, e.g a pesticide, in the tissues of organisms at successively higher levels in a food chain. This increase can occur as a result of:

<span class="mw-page-title-main">Bioindicator</span> Indicator species that can be used to reveal the qualitative 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.

<span class="mw-page-title-main">Wastewater quality indicators</span> Ways to test the suitability of wastewater

Wastewater quality indicators are laboratory test methodologies to assess suitability of wastewater for disposal, treatment or reuse. The main parameters in sewage that are measured to assess the sewage strength or quality as well as treatment options include: solids, indicators of organic matter, nitrogen, phosphorus, indicators of fecal contamination. Tests selected vary with the intended use or discharge location. Tests can measure physical, chemical, and biological characteristics of the wastewater. Physical characteristics include temperature and solids. Chemical characteristics include pH value, dissolved oxygen concentrations, biochemical oxygen demand (BOD) and chemical oxygen demand (COD), nitrogen, phosphorus, chlorine. Biological characteristics are determined with bioassays and aquatic toxicology tests.

<span class="mw-page-title-main">Nonpoint source pollution</span> Pollution resulting from multiple sources

Nonpoint source (NPS) pollution refers to diffuse contamination of water or air that does not originate from a single discrete source. This type of pollution is often the cumulative effect of small amounts of contaminants gathered from a large area. It is in contrast to point source pollution which results from a single source. Nonpoint source pollution generally results from land runoff, precipitation, atmospheric deposition, drainage, seepage, or hydrological modification where tracing pollution back to a single source is difficult. Nonpoint source water pollution affects a water body from sources such as polluted runoff from agricultural areas draining into a river, or wind-borne debris blowing out to sea. Nonpoint source air pollution affects air quality, from sources such as smokestacks or car tailpipes. Although these pollutants have originated from a point source, the long-range transport ability and multiple sources of the pollutant make it a nonpoint source of pollution; if the discharges were to occur to a body of water or into the atmosphere at a single location, the pollution would be single-point.

<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.

<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">Urban runoff</span> Surface runoff of rainwater created by urbanization

Urban runoff is surface runoff of rainwater, landscape irrigation, and car washing created by urbanization. Impervious surfaces are constructed during land development. During rain, storms, and other precipitation events, these surfaces, along with rooftops, carry polluted stormwater to storm drains, instead of allowing the water to percolate through soil. This causes lowering of the water table and flooding since the amount of water that remains on the surface is greater. Most municipal storm sewer systems discharge untreated stormwater to streams, rivers, and bays. This excess water can also make its way into people's properties through basement backups and seepage through building wall and floors.

<span class="mw-page-title-main">Sewage</span> Wastewater that is produced by a community of people

Sewage is a type of wastewater that is produced by a community of people. It is typically transported through a sewer system. Sewage consists of wastewater discharged from residences and from commercial, institutional and public facilities that exist in the locality. Sub-types of sewage are greywater and blackwater. Sewage also contains soaps and detergents. Food waste may be present from dishwashing, and food quantities may be increased where garbage disposal units are used. In regions where toilet paper is used rather than bidets, that paper is also added to the sewage. Sewage contains macro-pollutants and micro-pollutants, and may also incorporate some municipal solid waste and pollutants from industrial wastewater.

<span class="mw-page-title-main">Agricultural pollution</span> Type of pollution caused by agriculture

Agricultural pollution refers to biotic and abiotic byproducts of farming practices that result in contamination or degradation of the environment and surrounding ecosystems, and/or cause injury to humans and their economic interests. The pollution may come from a variety of sources, ranging from point source water pollution to more diffuse, landscape-level causes, also known as non-point source pollution and air pollution. Once in the environment these pollutants can have both direct effects in surrounding ecosystems, i.e. killing local wildlife or contaminating drinking water, and downstream effects such as dead zones caused by agricultural runoff is concentrated in large water bodies.

<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.

Environmental impacts of cleaning products entail the consequences that come as a result of chemical compounds in cleaning products. These cleaning products can contain chemicals that have detrimental impacts on the environment or on people.

<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.

In aquatic toxicology, bioconcentration is the accumulation of a water-borne chemical substance in an organism exposed to the water.

<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">Passive sampling</span>

Passive sampling is an environmental monitoring technique involving the use of a collecting medium, such as a man-made device or biological organism, to accumulate chemical pollutants in the environment over time. This is in contrast to grab sampling, which involves taking a sample directly from the media of interest at one point in time. In passive sampling, average chemical concentrations are calculated over a device's deployment time, which avoids the need to visit a sampling site multiple times to collect multiple representative samples. Currently, passive samplers have been developed and deployed to detect toxic metals, pesticides, pharmaceuticals, radionuclides, polycyclic aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), and other organic compounds in water, while some passive samplers can detect hazardous substances in the air.

References

  1. 1 2 3 4 5 6 7 Khanna, P; Ram Babu, P; Suju, M. (1999). "Carrying-capacity as a basis for sustainable development a case study of National Capital Region in India". Progress in Planning. 52 (2): 101–166. doi:10.1016/s0305-9006(99)00004-5. ISSN   0305-9006.
  2. 1 2 Masini, R. J; Cary, J. L; Simpson, C. J; McComb, A. J. (1995). "Effects of light and temperature on the photosynthesis of temperate meadow-forming seagrasses in Western Australia". Aquatic Botany. 49 (4): 239–254. doi:10.1016/0304-3770(94)00432-l. ISSN   0304-3770.
  3. Goyal, P; Anand, S; Gera, B. S. (2006). "Assimilative capacity and pollutant dispersion studies for Gangtok city". Atmospheric Environment. 40 (9): 1671–1682. Bibcode:2006AtmEn..40.1671G. doi:10.1016/j.atmosenv.2005.10.057. ISSN   1352-2310.
  4. 1 2 US Environmental Protection Agency (EPA) (2015). "Overview of Total Maximum Daily Loads (TMDLs)". US EPA. Retrieved 2020-06-29.
  5. Cairns Jr, J. (1998). "Assimilative capacity – the key to sustainable use of the planet". Journal of Aquatic Ecosystem Stress and Recovery. 6 (4): 259–263. doi:10.1023/a:1009902127556. ISSN   1386-1980. S2CID   195219452.
  6. 1 2 Stebbing, A.R.D. (1981). "Assimilative capacity". Marine Pollution Bulletin. 12 (11): 362–363. Bibcode:1981MarPB..12..362S. doi:10.1016/0025-326x(81)90403-3. ISSN   0025-326X.
  7. Park, C; Allaby, M. (2017). "A Dictionary of Environment and Conservation". Oxford Reference. doi:10.1093/acref/9780191826320.001.0001.
  8. Neal, C; Jarvie, H. P. (2005). "Agriculture, community, river eutrophication and the Water Framework Directive". Hydrological Processes. 19 (9): 1895–1901. Bibcode:2005HyPr...19.1895N. doi:10.1002/hyp.5903. ISSN   0885-6087. S2CID   129462273.
  9. 1 2 3 4 Manju, N; Balakrishnan, R; Mani, N. (2002). "Assimilative capacity and pollutant dispersion studies for the industrial zone of Manali". Atmospheric Environment. 36 (21): 3461–3471. Bibcode:2002AtmEn..36.3461M. doi:10.1016/s1352-2310(02)00306-0. ISSN   1352-2310.
  10. Maynard, R. L; Waller, R. E. (1996). "Suspended particulate matter and health: new light on an old problem". Thorax. 51 (12): 1174–1176. doi: 10.1136/thx.51.12.1174 . ISSN   0040-6376. PMC   472758 . PMID   8994511.
  11. The Lake Simcoe Region Conservation Authority (LSRCA). "Assimilative Capacity Study - Lake Simcoe Region Conservation Authority". www.lsrca.on.ca. Retrieved 2020-06-29.
  12. Bahadori, A; Vuthaluru, H. B. (2010). "Simple Arrhenius-type function accurately predicts dissolved oxygen saturation concentrations in aquatic systems". Process Safety and Environmental Protection. 88 (5): 335–340. doi:10.1016/j.psep.2010.05.002. ISSN   0957-5820.
  13. Peter, G; O'Connor, T. (2019), "Ocean Disposal and Monitoring", Waste Disposal in the Oceans, Routledge, pp. 12–25, doi:10.4324/9780429267246-2, ISBN   978-0-429-26724-6, S2CID   213381057