Americamysis bahia

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Americamysis bahia
Scientific classification Red Pencil Icon.png
Kingdom: Animalia
Phylum: Arthropoda
Subphylum: Crustacea
Class: Malacostraca
Superorder: Peracarida
Order: Mysida
Family: Mysidae
Genus: Americamysis
Species:
A. bahia
Binomial name
Americamysis bahia
(Molenock, 1969) [1]
Synonyms [1]
  • Mysidopsis bahia Molenock, 1969

Americamysis bahia is a shrimp-like crustacean in the order Mysida, the opossum shrimps. It is native to estuarine waters in Texas and Florida in the United States. It is often referred to in the literature as Mysidopsis bahia and is widely cultured and used in the laboratory for toxicology testing.

Contents

Description

Americamysis bahia grows to a length of about 9.4 mm (0.37 in), the females being larger than the males. These shrimps are transparent, often with a yellowish, brownish or blackish tinge. [2]

Distribution and habitat

Americamysis bahia is native to the east coast of the United States, its range extending from Rhode Island to Florida and the Gulf of Mexico. It is an estuarine species and can tolerate a wide range of salinity levels ranging from 54 to 2 psu (practical salinity units), being most common around 30 psu. It is seldom found at depths greater than 2 m (6 ft 7 in) and its typical habitat is over sandy or muddy seabeds, often in seagrass meadows. [3]

Behaviour

Americamysis bahia is found on or just above the seabed, tending to be concentrated in slight depressions and facing towards the current. At night it makes vertical migrations to feed at the surface. Opossum shrimps are omnivores and although the diet of Americamysis bahia in the wild has not been studied, examination of the stomach contents of the closely related Americamysis almyra showed 31% vascular plant debris and 11% copepods and diatoms. In the laboratory it is usually fed on the larvae of the brine shrimp Artemia salina . Opossum shrimps play an important part in the food chain and are consumed in large quantities by such fish as the inland silverside, whiffs and flounders. [4]

Life cycle

Female Americamysis bahia shrimps become mature between the twelfth and twentieth day, depending on diet and temperature. The eggs are fertilised and the embryos develop in the female’s brood pouch, underneath her thorax. Batches of five to seven young per brood are usual and are released into the water column in four to six days. The juveniles are planktonic for twenty-four hours before settling on the bottom. Females can produce multiple broods over the course of a few months. [5]

Use in research

Americamysis bahia is relatively sensitive to toxic pollutants. Because of this and the fact that it is small, has a short life cycle, and is easy to culture, it is extensively used in toxicity testing. [6] [7]

Related Research Articles

Toxicity Degree of harmfulness of substances

Toxicity is the degree to which a chemical substance or a particular mixture of substances can damage an organism. Toxicity can refer to the effect on a whole organism, such as an animal, bacterium, or plant, as well as the effect on a substructure of the organism, such as a cell (cytotoxicity) or an organ such as the liver (hepatotoxicity). By extension, the word may be metaphorically used to describe toxic effects on larger and more complex groups, such as the family unit or society at large. Sometimes the word is more or less synonymous with poisoning in everyday usage.

Chronic toxicity, the development of adverse effects as a result of long term exposure to a contaminant or other stressor, is an important aspect of aquatic toxicology. Adverse effects associated with chronic toxicity can be directly lethal but are more commonly sublethal, including changes in growth, reproduction, or behavior. Chronic toxicity is in contrast to acute toxicity, which occurs over a shorter period of time to higher concentrations. Various toxicity tests can be performed to assess the chronic toxicity of different contaminants, and usually last at least 10% of an organism's lifespan. Results of aquatic chronic toxicity tests can be used to determine water quality guidelines and regulations for protection of aquatic organisms.

Mysida Small, shrimp-like crustacean

Mysida is an order of small, shrimp-like crustaceans in the malacostracan superorder Peracarida. Their common name opossum shrimps stems from the presence of a brood pouch or "marsupium" in females. The fact that the larvae are reared in this pouch and are not free-swimming characterises the order. The mysid's head bears a pair of stalked eyes and two pairs of antennae. The thorax consists of eight segments each bearing branching limbs, the whole concealed beneath a protective carapace and the abdomen has six segments and usually further small limbs.

Aquatic toxicology

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.

Wastewater quality indicators

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.

Inland silverside Species of fish

The inland silverside is a neotropical silverside native to eastern North America, and introduced into California. It is a fish of estuaries and freshwater environments.

<i>Neomysis integer</i> Species of crustacean

Neomysis integer is a species of opossum shrimp found in shallow marine bays and estuaries of Europe, with a transparent greenish or brownish body and a large cephalothorax. It is found in very shallow water in both high and low-salinity habitats. It is a filter feeder and the female broods her eggs in a brood pouch beneath her cephalothorax.

Environmental toxicology

Environmental toxicology is a multidisciplinary field of science concerned with the study of the harmful effects of various chemical, biological and physical agents on living organisms. Ecotoxicology is a subdiscipline of environmental toxicology concerned with studying the harmful effects of toxicants at the population and ecosystem levels.

Mysis salemaai is a shrimp-like crustacean in the Mysida order, inhabiting lakes of Ireland and South Scandinavia and brackish waters of the northern Baltic Sea.

The Biotic Ligand Model (BLM) is a tool used in aquatic toxicology that examines the bioavailability of metals in the aquatic environment and the affinity of these metals to accumulate on gill surfaces of organisms. BLM depends on the site-specific water quality including such parameters as pH, hardness, and dissolved organic carbon. In this model, lethal accumulation values are used to be predictive of lethal concentration values that are more universal for aquatic toxicology and the development of standards. Collection of water chemistry parameters for a given site, incorporation of the data into the BLM computer model and analysis of the output data is used to accomplish BLM analysis. Comparison of these values derived from the model, have repeatedly been found to be comparable to the results of lethal tissue concentrations from acute toxicity tests. The BLM was developed from the gill surface interaction model (GSIM) and the free ion activity model (FIAM). Both of these models also address how metals interact with organisms and aquatic environments. Currently, the United States Environmental Protection Agency (EPA) uses the BLM as a tool to outline Ambient Water Quality Criteria (AWQC) for surface water. Because BLM is so useful for investigation of metals in surface water, there are developmental plans to expand BLM for use in marine and estuarine environments.

The maximum acceptable toxicant concentration (MATC) is a value that is calculated through aquatic toxicity tests to help set water quality regulations for the protection of aquatic life. Using the results of a partial life-cycle chronic toxicity test, the MATC is reported as the geometric mean between the No Observed Effect Concentration (NOEC) and the lowest observed effect concentration (LOEC).

Petalophthalmidae is a family of marine crustaceans in the order Mysida, the opossum shrimps.

Mysidopsis is a genus of mysid shrimps in the family Mysidae. The sensitivity of these shrimps to water quality makes them suitable for bioassays. Mysidopsis bahia and Mysidopsis almyra, which are used frequently to test for pesticides and other toxic substances, are now classified as Americamysis bahia and Americamysis almyra.

<i>Americamysis</i> Genus of crustaceans

Americamysis is a genus of mysid shrimps in the family Mysidae. The sensitivity of these shrimps to water quality makes them suitable for bioassays. Americamysis bahia and Americamysis almyra, which are used frequently to test for pesticides and other toxic substances, are often referred to as Mysidopsis bahia and Mysidopsis almyra in the literature.

Americamysis almyra is a shrimp-like crustacean in the order Mysida, the opossum shrimps. It is native to estuarine waters in the western Atlantic Ocean and Gulf of Mexico. It is often referred to in the literature as Mysidopsis almyra.

<i>Gastrosaccus spinifer</i> Species of crustacean

Gastrosaccus spinifer is a shrimp-like crustacean in the order Mysida, the opossum shrimps, native to the eastern Atlantic Ocean and the coasts of Northern and Western Europe.

An early life stage (ELS) test is a chronic toxicity test using sensitive early life stages like embryos or larvae to predict the effects of toxicants on organisms. ELS tests were developed to be quicker and more cost-efficient than full life-cycle tests, taking on average 1–5 months to complete compared to 6–12 months for a life-cycle test. They are commonly used in aquatic toxicology, particularly with fish. Growth and survival are the typically measured endpoints, for which a Maximum Acceptable Toxicant Concentration (MATC) can be estimated. ELS tests allow for the testing of fish species that otherwise could not be studied due to length of life, spawning requirements, or size. ELS tests are used as part of environmental risk assessments by regulatory agencies including the U.S. Environmental Protection Agency (EPA) and Environment Canada, as well as the Organisation for Economic Co-operation and Development (OECD).

Toxicological databases are large compilations of data derived from aquatic and environmental toxicity studies. Data is aggregated from a large number of individual studies in which toxic effects upon aquatic and terrestrial organisms have been determined for different chemicals. These databases are then used by toxicologists, chemists, regulatory agencies and scientists to investigate and predict the likelihood that an organic or inorganic chemical will cause an adverse effect on exposed organisms.

The acute to chronic ratio (ACR) uses acute toxicity data to gauge the chronic toxicity (MATC) of a chemical of interest to an organism. The science behind determining a safe concentration to the environment is imperfect, statistically limited, and resource intensive. There is an unfilled demand for the rapid assessment of different chemical toxicity to many different organisms. The ACR is a proposed solution to this demand.

Toxic units (TU) are used in the field of toxicology to quantify the interactions of toxicants in binary mixtures of chemicals. A toxic unit for a given compound is based on the concentration at which there is a 50% effect for a certain biological endpoint. One toxic unit is equal to the EC50 for a given endpoint for a specific biological effect over a given amount of time. Toxic units allow for the comparison of the individual toxicities of a binary mixture to the combined toxicity. This allows researchers to categorize mixtures as additive, synergistic or antagonistic. Synergism and antagonism are defined by mixtures that are more or less toxic than predicted by the sum of their toxic units.

References

  1. 1 2 Mees, Jan (2013). "Americamysis bahia (Molenock, 1969)". WoRMS. World Register of Marine Species . Retrieved 2014-02-07.
  2. "Species: Americamysis bahia". Culture Journal. Marine Breeding Initiative. Retrieved 2014-02-07.
  3. Johnson, William S.; Allen, Dennis M. (2012). Zooplankton of the Atlantic and Gulf Coasts: A Guide to Their Identification and Ecology. JHU Press. p. 192. ISBN   9781421406183.
  4. Mayer, F. L.; Hamelink, J. L. (eds.) (2007). Aquatic Toxicology and Hazard Evaluation. ASTM International. pp. 110–111. ISBN   9780803102781.CS1 maint: extra text: authors list (link)
  5. Culturing Mysidopsis bahia. Supplemental Report. Environmental Protection Agency. 1990. EPA 505/8-90-006b.
  6. Wortham-Neal, Jennifer L.; Price, W. Wayne (2002). "Marsupial Developmental Stages in Americamysis bahia (Mysida: Mysidae)". Journal of Crustacean Biology. 22 (1): 98–112. doi: 10.1163/20021975-99990213 . JSTOR   1549611.
  7. U.S. Environmental Protection Agency (October 2002). Short-Term Methods for Estimating the Chronic Toxicity of Effluents and Receiving Waters to Marine and Estuarine Organisms (EPA 821-R-02-014) (PDF) (Report). U.S. Environmental Protection Agency. pp. 214–292. Retrieved November 15, 2017. 14.1.1 This method, adapted in part from USEPA (1987d), estimates the chronic toxicity of effluents and receiving waters to the mysid, Mysidopsis bahia, during a seven-day, static renewal exposure. The effects include the synergistic, antagonistic, and additive effects of all the chemical, physical, and additive components which adversely affect the physiological and biochemical functions of the test organisms.