Microcystin
Microcystins—or cyanoginosins—are a class of toxins produced by certain freshwater cyanobacteria, commonly known as blue-green algae.[3] Over 250[4] different microcystins have been discovered so far, of which microcystin-LR is the most common. Chemically they are cyclic heptapeptides produced through nonribosomal peptide synthases.[5]
Cyanobacteria can produce microcystins in large quantities during algal blooms which then pose a major threat to drinking and irrigation water supplies, and the environment at large.[6][7]
Characteristics
Microcystins—or cyanoginosins—are a class of toxins[8] produced by certain freshwater cyanobacteria; primarily Microcystis aeruginosa but also other Microcystis, as well as members of the Planktothrix, Anabaena, Oscillatoria and Nostoc genera.
Chemistry
Microcystins have a common structural framework of D-Ala1-X2-D-Masp3-Z4-Adda5-D-γ-Glu6-Mdha7, where X and Z are variable amino acids; the systematic name "microcystin-XZ" (MC-XZ in short) is then assigned based on the one letter codes (if available; longer codes otherwise) of the amino acids.
- D-Masp is D-erythro-β-methyl-isoaspartic acid, a derivative of β-amino acid form;[4]
- Adda is (all-S,all-E)-3-amino-9-methoxy-2,6,8-trimethyl-10-phenyldeca-4,6-dienoic acid, a β-amino acid exclusively found in microcystin and the related nodularin;
- Mdha is N-methyldehydroalanine, a derivative of dehydroalanine.[4] In nodularin it is replaced by Mdhb (N-methyldehydrobutyrine), another dehydroamino acid derivative.[18]
Mechanism of action
Microcystins
Factors affecting production
The microcystin-producing
Microcystins may have evolved as a way to deal with low iron supply in cyanobacteria: the molecule binds iron, and non-producing strains are significantly worse at coping with low iron levels.[22] Low iron supply up-regulates McyD, one of the microcystin synthetic operons.[23] Sufficient iron supply, however, can still boost microcystin production by making the bacterium better at photosynthesis, therefore producing sufficient ATP for MC biosynthesis.[24]
Microcystin production is also positively correlated with temperature.[25] Bright light and red light increases transcription of McyD, but blue light reduces it.[26] A wide range of other factors such as pH may also affect MC production, but comparison is complicated due to a lack of standard testing conditions.[27]
Exposure pathways
There are several ways of exposure to these hepatotoxins that humans can encounter one of which is through recreational activities like swimming, surfing, fishing, and other activities involving direct contact with contaminated water.[28] Another rare, yet extremely toxic, route of exposure that has been identified by scientists is through hemodialysis surgeries. One of the fatal cases for microcystic intoxication through hemodialysis was studied in Brazil where 48% of patients that received the surgery in a specific period of time died because the water used in the procedure was found to be contaminated.[29]
Microcystins are chemically stable over a wide range of temperature and pH, possibly as a result of their cyclic structure.[30] Microcystin-LR water contamination is resistant to boiling and microwave treatments.[31] Microcystin-producing bacteria algal blooms can overwhelm the filter capacities of water treatment plants. Some evidence shows the toxin can be transported by irrigation into the food chain.[32][33]
Lake Erie blooms
In 2011, a record outbreak of blooming microcystis occurred in Lake Erie, in part related to the wettest spring on record, and expanded lake bottom dead zones, reduced fish populations, fouled beaches, and damaged the local tourism industry, which generates more than $10 billion in revenue annually.[1]
In August 2014, the City of Toledo, Ohio detected unsafe levels of microcystin in its water supply due to harmful algal blooms in Lake Erie, the shallowest of the Great Lakes. The city issued an advisory to approximately 500,000 people that the water was not safe for drinking or cooking.[34][35] An Ohio state task force found that Lake Erie received more phosphorus than any other Great Lake, both from crop land, due to the farming practices, and from urban water-treatment centres.[21]
San Francisco Bay Area
In 2016, microcystin had been found in San Francisco Bay Area shellfish in seawater, apparently from freshwater runoff, exacerbated by drought.[36]
Iowa
In 2018, the Iowa Department of Natural Resources found microcystins at levels of 0.3 µg/L, or micrograms per liter (ppb), in the raw water supplies of 15 out of 26 public water systems tested.[37]
Oregon
In 2023, the Oregon Department of Environmental Quality (DEQ) and Oregon Health Authority issued a cyanobacteria advisory for much of the Willamette River as it runs through Portland.[38] The advisory affected the Willamette from the Ross Island Lagoon through Cathedral Park.[39] Testing by the DEQ showed microcystin levels at 549 ppb.[38]
Human health effects upon exposure
Microcystins cannot be broken down by standard
Studies suggest that the absorption of microcystins occurs in the gastrointestinal tract.[28] Furthermore, it was found that these hepatotoxins inhibit the activity of protein enzymes phosphatase PP1 and PP2A causing hemorrhagic shock and were found to kill within 45 minutes in mice studies.[43]
There appears to be inadequate information to assess the carcinogenic potential of microcystins by applying EPA Guidelines for Carcinogen Risk Assessment. A few studies suggest a relationship may exist between liver and colorectral cancers and the occurrence of cyanobacteria in drinking water in China.[44][45][46][47][48][49] Evidence is, however, limited due to limited ability to accurately assess and measure exposure.
Regulation
In the US, the EPA issued a health advisory in 2015.[50] A ten day Health Advisory was calculated for different ages which is considered protective of non-carcinogenic adverse health effects over a ten-day exposure to microcystins in drinking water: 0.3 μg/L for bottle-fed infants and young children of pre-school age and 1.6 μg/L for children of school age through adults.[50]: 28–29
See also
References
- ^ a b Michael Wines (March 14, 2013). "Spring Rain, Then Foul Algae in Ailing Lake Erie". The New York Times.
- ^ Joanna M. Foster (November 20, 2013). "Lake Erie is Dying Again, and Warmer Waters and Wetter Weather are to Blame". ClimateProgress. Archived from the original on August 3, 2014. Retrieved August 3, 2014.
- ^ "Cyanobacterial Harmful Algal Blooms (CyanoHABs) & Water". Mass.gov. Retrieved 9 June 2022.
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- ^ a b c "Increasing toxicity of algal blooms tied to nutrient enrichment and climate change". Oregon State University. October 24, 2013.
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- ^ Fatoki, O.S., Muyima, N.Y.O. & Lujiza, N. 2001. Situation analysis of water quality in the Umtata River Catchment. Water SA, (27) pp. 467–474.
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- ^ Oberholster PJ, Botha AM (2007). "Use of PCR based technologies for risk assessment of a winter cyanobacterial bloom in Lake Midmar, South Africa". African Journal of Biotechnology. 6 (15): 14–21.
- ^ Oberholster, P. 2008. Parliamentary Briefing Paper on Cyanobacteria in Water Resources of South Africa. Annexure "A" of CSIR Report No. CSIR/NRE/WR/IR/2008/0079/C. Pretoria. Council for Scientific and Industrial Research (CSIR).
- ^ Oberholster, P.J.; Cloete, T.E.; van Ginkel, C.; et al. (2008). "The use of remote sensing and molecular markers as early warning indicators of the development of cyanobacterial hyperscum crust and microcystin-producing genotypes in the hypertrophic Lake Hartebeespoort, South Africa" (PDF). Pretoria: Council for Scientific and Industrial Research. Archived from the original (PDF) on 2014-08-11.
- ^ Oberholster, P.J.; Ashton, P.J. (2008). "State of the Nation Report: An Overview of the Current Status of Water Quality and Eutrophication in South African Rivers and Reservoirs" (PDF). Pretoria: Council for Scientific and Industrial Research. Archived from the original (PDF) on 2014-08-08.
- ^ Turton, A.R. 2015. Water Pollution and South Africa's Poor. Johannesburg: South African Institute of Race Relations. http://irr.org.za/reports-and-publications/occasional-reports/files/water-pollution-and-south-africas-poor Archived 2017-03-12 at the Wayback Machine
- ^ a b Barnett A. Rattner, Glenn H. Olsen, Peter C. McGowan, Betty K. Ackerson, and Moira A. McKernan. "Harmful Algal Blooms and Bird Die-offs in Chesapeake Bay: A Potential Link?". Patuxent Wildlife Research Center.
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- ^ "Impacts of Climate Change on the Occurrence of Harmful Algal Blooms" (PDF). EPA. 2013. Archived from the original (PDF) on 2020-08-07. Retrieved 2014-08-03.
- ^ a b Suzanne Goldenberg (August 3, 2014). "Farming practices and climate change at root of Toledo water pollution". The Guardian.
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- ^ a b Funari E, Testai E. 2008. Human health risk assessment related to cyanotoxins exposure. Critical Reviews in Toxicology. 38(2). 97–125
- ^ a b Azevedo, Sandra M.F.O, Wayne W Carmichael, Elise M Jochimsen, Kenneth L Rinehart, Sharon Lau, Glen R Shaw, and Geoff K Eaglesham. 2002. “Human Intoxication by Microcystins During Renal Dialysis Treatment in Caruaru—Brazil.” Toxicology (Amsterdam) 181. 441–446.
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- ^ "Algal bloom leaves 500,000 without drinking water in northeast Ohio". Reuters. August 2, 2014.
- ^ Rick Jervis, USA TODAY (August 2, 2014). "Toxins contaminate drinking water in northwest Ohio". USA Today.
- ^ John Raphael BEWARE: High Levels of Freshwater Toxin Found in Shellfish from San Francisco Bay Oct 28, 2016. Nature World News
- ^ Kate Payne Toxic Bacteria Blooms Impacting Water Systems Across Iowa, DNR Survey Shows. November 1, 2018. National Public Radio
- ^ a b "Oregon Health Authority : Current Cyanobacteria Advisories : Cyanobacteria Blooms : State of Oregon". www.oregon.gov. Retrieved 2023-08-26.
- ^ "Swimmers, boaters should avoid toxic algae in Willamette River and Sauvie Island". Multnomah County. 2023-08-13. Retrieved 2023-08-26.
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- ^ Falconer, I.R. 2005. Cyanobacterial Toxins of Drinking Water Supplies: Cylindrospermopsins and Microcystins. Florida: CRC Press. 279 pages.
- ^ What health risks do humans face as a result of exposure to cyanotoxins? EPA, retrieved 12 Nov 2018
- ^ Carmichael, W.W. 1992. Cyanobacteria secondary metabolites: The cyanotoxins. J. Appl. Bacteriol. 72, 445–459
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- ^ a b Drinking Water Health Advisory for the Cyanobacterial Microcystin Toxins U.S. Environmental Protection Agency Office of Water, EPA Document Number: 820R15100, 75pp, 15 June 2015
Further reading
- National Center for Environmental Assessment. Toxicological Reviews of Cyanobacterial Toxins: Microcystins LR, RR, YR, and LA (NCEA-C-1765)
External links
- Harmful Algal Blooms (EPA), n.d. retrieved 12 Nov 2018
- Blue-Green Algae (Cyanobacteria) and their Toxins (Health Canada)
- Toxic cyanobacteria in water: A guide to their public health consequences, monitoring, and management (WHO)
- Cyanobacteria and Cyanotoxins: Information for Drinking Water Systems (EPA)
- Cyanobacteria Are Far From Just Toledo's Problem By Carl Zimmer, Aug. 7, 2014(The New York Times)