Найдено научных статей и публикаций: 9, для научной тематики: surfactants
Связанные научные тематики:
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On the Multifunctional Role of the Biota in the Self-Purification of Aquatic Ecosystems
(публикация автора на scipeople)
Ostroumov S. A.
, 2010
Ostroumov S. A. On the Multifunctional Role of the Biota in the Self-Purification of Aquatic Ecosystems. - Russian Journal of Ecology, Vol. 36, No. 6, 2005, pp. 414–420. Translated from Ekologiya, No. 6, 2005, pp. 452–459.
Moscow State...
Ostroumov S. A. On the Multifunctional Role of the Biota in the Self-Purification of Aquatic Ecosystems. - Russian Journal of Ecology, Vol. 36, No. 6, 2005, pp. 414–420. Translated from Ekologiya, No. 6, 2005, pp. 452–459.
Moscow State University, Vorob’evy gory, Moscow, 119991, Russia
Abstract
—Principles of the theory of the ecological mechanism of water self-purification based on multiple functions of the biota in freshwater and marine ecosystems are formulated. In developing this theory, the results of the author’s experiments with filtering hydrobionts have been used. These results indicate that the water self-purification mechanism is vulnerable to the impact of some pollutants and, in particular, surfactants. Conclusions drawn on the basis of the theory have practical significance for biodiversity conservation and for the sustainable
use of the biological resources of aquatic ecosystems.
http://www.springerlink.com/content/y6370w774lk7g786/;
DOI 10.1007/s11184-005-0095-x;
Key words: functioning of ecosystems ecosystem services aquatic ecosystems, water quality, water self-purification, pollution, theory, ecological safety, biota, organisms, marine, freshwater, water filtering, surfactants, biological resources, discovery, innovations, new data, new findings, aquatic ecology new ecotechnology ecotoxicology man-made changes anthropogenic effects new conceptualization habitat sustainability ecological stability.
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Concise results: well-cited publications on ecology and environment, online
(публикация автора на scipeople)
С. А. Остроумов, (S.A. Ostroumov)
, 2010
The concise results and shortlist of some well-cited publications on ecology and environment - in English, the full texts or abstracts available online free (updated 2010, Mar 20).
The publications by S.A.O. in the main part of the list below...
The concise results and shortlist of some well-cited publications on ecology and environment - in English, the full texts or abstracts available online free (updated 2010, Mar 20).
The publications by S.A.O. in the main part of the list below include those that described some innovations in conceptualization of the fundamentals of ecology, – e.g., such as the notion of ecosystem [15]. Previously, in the book ‘Introduction to Biochemical Ecology’, the same author explored another fundamental issue of ecology and made a new classification of interorganismal interactions mediated by chemicals. Also, some of the publications given below formulated a new theory of the biomachinery that provides the useful ecosystem’s service of improving water quality [2, 4, 14, 20, 24, 25, 31]. In another essential series of publications, a set of new biological effects of man-made chemicals were discovered [1, 6, 12, 16, 19, 27; and others]. As a result, some new hazards of chemical pollution to the biosphere were found [1, 2, 12, 17, 19, 21]. Practical recommendations to better protect aquatic biodiversity were published [18], which was a continuation of the book ‘Conservation of Living Nature and Resources: Problems, Trends, Prospects’ (by A. Yablokov, S. Ostroumov, Springer Press). Steps towards new technologies to combat pollution were made [30]. A list of priorities in the further research on the most urgent issues of ecology and environment was developed [23].
The publications [1-32] and other publications authored and coauthored by S.A.O. were commented and supported in the papers and books by many other authors [33-119]. Among them are the scientists who work in N. America (e.g., [50, 61, 100, 103]), Europe (e.g., [58, 68-70, 79, 84 ]; including France, Spain, Greece), Asia (e.g., [72, 81, 88, 101, 117]; including China and India), and other parts of the world.
KEY WORDS: ecosystem, pollutants, biomachinery that provide the ecosystem’s service of improving water quality, new biological effects of man-made chemicals, new hazards of chemical pollution to the biosphere, recommendations to better protect aquatic biodiversity, conservation of nature and resources, new phytotechnologies to combat pollution, priorities, environment protection; water self-purification; surfactants, detergents, filter-feeders, environmental safety
REFERENCES:
1. The book: Ostroumov S. A. Biological Effects of Surfactants. CRC Press. Taylor & Francis. Boca Raton, London, New York. 2006. 279 p. ISBN 0-8493-2526-9 [new facts and concepts on assessment of hazards from chemicals, new look on the factors important to water quality, to sustainability; new priorities in environmental safety]; the table of contents see at: http://www.chipsbooks.com/biosurfc.htm;
2. Ostroumov S. A. The concept of aquatic biota as a labile and vulnerable component of the water self-purification system - Doklady Biological Sciences, Vol. 372, 2000, pp. 286–289. http://sites.google.com/site/2000dbs372p286biotalabil/;
3. Ostroumov S. A., Kolesnikov M. P. Biocatalysis of Matter Transfer in a Microcosm Is Inhibited by a Contaminant: Effects of a Surfactant on Limnea stagnalis. - Doklady Biological Sciences, 2000, 373: 397–399. Translated from Doklady Akademii Nauk, 2000, Vol. 373, No. 2, pp. 278–280. http://sites.google.com/site/2000dbs373p397biocatallstag/;
4. Ostroumov S. A. An aquatic ecosystem: a large-scale diversified bioreactor with a water self-purification function. - Doklady Biological Sciences, 2000. Vol. 374, P. 514-516. http://sites.google.com/site/2000dbs374p514bioreactor/ ;
5. Ostroumov S.A. Criteria of ecological hazards due to anthropogenic effects on the biota: searching for a system. - Dokl Biol Sci (Doklady Biological Sciences). 2000; 371: 204-206. http://sites.google.com/site/2000dbs371p204criteria/ ;
6. Ostroumov S. A. An amphiphilic substance inhibits the mollusk capacity to filter out phytoplankton cells from water. - Biology Bulletin, 2001, Volume 28, Number 1, p. 95-102. ISSN 1062-3590 (Print) 1608-3059 (Online); DOI 10.1023/A:1026671024000; http://www.springerlink.com/content/l665628020163255/;
7. Ostroumov S. A. Inhibitory Analysis of Regulatory Interactions in Trophic Webs. - Doklady Biological Sciences, 2001, Vol. 377, pp. 139–141. Translated from Doklady Akademii Nauk, 2000, Vol. 375, No. 6, pp. 847–849. [In the paper, the author developed a new approach to analyze the fundamental ecological issue, the interactions between organisms in ecosystems. He suggested using the methodology of inhibitory analysis to study interactions in trophic chains. Important situation is the top–down control of plankton by benthic filter-feeders. This control, as the author’s experiments have shown, might be removed by chemical inhibitors (the latter may enter the ecosystem as pollutants)]. http://sites.google.com/site/2001dbs377p139inhibitory/; http://blog.researchgate.net/masterblog/299_Inhibitory_Analysis_A_new_method_for_analyzing_interactions_between_organisms_in_ecosystems;
8. Ostroumov SA. The synecological approach to the problem of eutrophication. - Dokl Biol Sci. (Doklady Biological Sciences). 2001; 381: 559-562. PMID: 12918433 [PubMed - indexed for MEDLINE]; http://scipeople.com/uploads/materials/4389/Danbio6_2001v381n5.E.eutrophication.pdf ;
9. Ostroumov SA. The hazard of a two-level synergism of synecological summation of anthropogenic effects. - Dokl Biol Sci. (Doklady Biological Sciences). 2001; 380: 499-501. http://sites.google.com/site/2001dbs380p499synerg/ ; PMID: 12918416 [PubMed - indexed for MEDLINE];
10. Ostroumov SA. Responses of Unio tumidus to mixed chemical preparations and the hazard of synecological summation of anthropogenic effects. - Dokl Biol Sci (Doklady Biological Sciences). 2001; 380: 492-495. http://sites.google.com/site/2001dbs380p492unio/; PMID: 12918414 [PubMed - indexed for MEDLINE];
11. Ostroumov SA, Kolesnikov MP. Pellets of some mollusks in the biogeochemical flows of C, N, P, Si, and Al. - Dokl Biol Sci (Doklady Biological Sciences). 2001; 379: 378-381. http://sites.google.com/site/2001dbs379p378pellets/; PMID: 12918380 [PubMed - indexed for MEDLINE];
12. Ostroumov SA. Imbalance of factors providing control of unicellular plankton populations exposed to anthropogenic impact. - Dokl Biol Sci (Doklady Biological Sciences). 2001; 379: 341-343. PMID: 12918370 [PubMed - indexed for MEDLINE]; http://sites.google.com/site/1dbs379p341imbalance/; https://www.researchgate.net/profile/Sergei_Ostroumov/blog/321_Discovery_of_the_system_where_chemical_pollution_could_impair_the_regulation_and_balance_in_the_abundance_of_phytoplankton_threat_to_ecological_stability_ ;
13. Ostroumov SA. Effect of amphiphilic chemicals on filter-feeding marine organisms. - Dokl Biol Sci (Doklady Biological Sciences). 2001; 378: 248-250. For the first time, oysters were used as the test-organisms in bioassay of synthetic surfactants and detergents. The new data revealed a novel type of hazard to mariculture. New negative effects of surfactants and chemical mixtures on water filtering activity of Crassostrea gigas were discovered. http://sites.google.com/site/2001dbs378p248effammaroyst/; PMID: 12918342 [PubMed - indexed for MEDLINE];
14. Ostroumov SA. Biodiversity protection and quality of water: the role of feedbacks in ecosystems. - Dokl Biol Sci (Doklady Biological Sciences). 2002; 382: 18-21; http://sites.google.com/site/2dbs382p18biodivers/; http://www.citeulike.org/pdf/user/ATP/article/6113559/ostroumov_02_biodiversity.pdf;
15. Ostroumov S.A. New definitions of the concepts and terms ecosystem and biogeocenosis. - Doklady Biological Sciences 2002 (March), Volume 383, Numbers 1- 6, p. 141-143. [ISSN 0012-4966 (Print) 1608-3105 (Online)]. https://www.researchgate.net/file.FileLoader.html?key=997c8c86899d5a6e24531054ad1bcd1e; PMID: 12053565 [PubMed - indexed for MEDLINE];
16. Ostroumov SA. A new type of effect of potentially hazardous substances: uncouplers of pelagial-benthal coupling. - Dokl Biol Sci (Doklady Biological Sciences). 2002; 383: 127-130. https://www.researchgate.net/file.FileLoader.html?key=d988acb599e121964c48114374a87e8d; www.springerlink.com/index/28V23JBFADL1Y100.pdf; In the paper new facts are reported that shows man-made hazards to 3 aspects of functioning of the biosphere and ecosystems: (1) formation of water quality; (2) biogeochemical flows of C, N, P and other constituents of biomass; (3) formation of deposits of organic matter as bottom sediments. https://www.researchgate.net/profile/Sergei_Ostroumov/blog/358_Three_new_key_hazards_to_the_functioning_of_the_biosphere; PMID: 12053562 [PubMed - indexed for MEDLINE];
17. Ostroumov S. A. Identification of a New Type of Ecological Hazard of Chemicals: Inhibition of Processes of Ecological Remediation. - Doklady Biological Sciences, Vol. 385, 2002 (November), pp. 377–379. [Translated from Doklady Akademii Nauk, Vol. 385, No. 4, 2002, pp. 571–573]. PMID: 12469618 [PubMed - indexed for MEDLINE]; https://www.researchgate.net/file.FileLoader.html?key=8408a7cfaa984764b812ce79c77007f2;
18. Ostroumov SA. System of principles for conservation of the biogeocenotic function and the biodiversity of filter-feeders. - Dokl Biol Sci (Doklady Biological Sciences). 2002; 383: 147-150. https://www.researchgate.net/file.FileLoader.html?key=888352078b275ef40a430eb5b4d7714c; https://www.researchgate.net/profile/Sergei_Ostroumov/blog/359_How_to_establish_a_new_type_of_reserves_to_protect_aquatic_biodiversity_and_ecosystem_services; PMID: 12053567 [PubMed - indexed for MEDLINE];
19. Ostroumov S. A. Inhibitory analysis of top-down control: new keys to studying eutrophication, algal blooms, and water self-purification // Hydrobiologia. 2002. vol. 469. P.117-129. A new approach to prevent pollution, eutrophication, and algal blooms was identified and analyzed in this paper. The approach is based on efficient use of the natural mechanisms of self-regulation of ecosystem DOI 10.1023/A:1015559123646; http://www.moipros.ru/files/author_4_article_9.doc; www.springerlink.com/index/R9PTJEQ5FK8VLA6M.pdf; http://scipeople.com/uploads/materials/4389/2Hydrobiologia469p117w%20Addendum.DOC;
20. Ostroumov S.A. Polyfunctional role of biodiversity in processes leading to water purification: current conceptualizations and concluding remarks. - Hydrobiologia, 2002 (February), 469: 203-204. DOI 10.1007/s10750-004-1875-1; http://scipeople.com/uploads/materials/4389/2H469p203.Polyfunctional.role.w.Addendum.rtf; http://www.springerlink.com/content/hcrfvmdncdm8e3pf/;
21. Ostroumov S. A., Walz N., Rusche R. Effect of a cationic amphiphilic compound on rotifers. - Doklady Biological Sciences. 2003 (May). Vol. 390. p. 252-255 [ISSN 0012-4966 (Print) 1608-3105 (Online)]. PMID: 12940156 [PubMed - indexed for MEDLINE]; https://www.researchgate.net/file.FileLoader.html?key=def6575c794b111fcc31275e853c2b15;
22. Ostroumov S.A. Anthropogenic effects on the biota: towards a new system of principles and criteria for analysis of ecological hazards. - Rivista di Biologia/Biology Forum. 2003. 96: 159-170. Review. PMID: 12852181 [PubMed - indexed for MEDLINE] http://sites.google.com/site/ostroumovsergei/publications-1/rivista2003criteria; http://scipeople.com/uploads/materials/4389/3RB96p159Anth..Criteria.doc; www.ncbi.nlm.nih.gov/pubmed/12852181;
23. Ostroumov S.A., Dodson S., Hamilton D., Peterson S., Wetzel R.G. Medium-term and long-term priorities in ecological studies // Rivista di Biologia / Biology Forum. 2003 (May). 96: 327-332. Abstracts in Eng. and Italian (p. 332). http://scipeople.com/uploads/materials/4389/3RivistaBio96Priorities2.rtf; www.ncbi.nlm.nih.gov/pubmed/14595906 ; PMID: 14595906 [PubMed - indexed for MEDLINE] Research priorities in ecology and environmental sciences for the future are formulated. The priorities for both fundamental and applied ecology are proposed. The list of priorities includes 50 items. The priorities are relevant to terrestrial, aquatic, and general ecology. The list of priorities is helpful when grant proposals are being prepared, evaluated, and selected for funding.
24. Ostroumov S. A. On the biotic self-purification of aquatic ecosystems: elements of the theory. - Doklady Biological Sciences, 2004, Vol. 396, Numbers 1- 6, p. 206-211. https://www.researchgate.net/file.FileLoader.html?key=60f338228d6f3c5114d223ab81e15d3b; https://www.researchgate.net/profile/Sergei_Ostroumov/blog/348_Useful_theory_of_natural_mechanisms_of_improving_water_quality; PMID: 15354827 [PubMed - indexed for MEDLINE];
25. Aquatic ecosystem as a bioreactor: water purification and some other functions. - Rivista di Biologia / Biology Forum, 2004, 97 (1): 67-78. Abstracts in Eng. and Italian. [A new fundamental concept is proposed of aquatic ecosystem as a bioreactor that carries out the function of water purification in natural water bodies and streams. The ecosystem as a bioreactor has the following characteristic attributes: (1) it is a large-scale (large-volume) bioreactor; (2) it is a diversified (in terms of the number of taxa and the scope of functional activities) bioreactor; (3) it possesses a broad range of biocatalytic (chemical-transforming and degrading) capabilities. New experimental data on xenobiotics - induced inhibition of the water filtration performed by the bivalve molluscs Unio tumidus, U. pictorum, M. galloprovincialis and inhibition of feeding by Limnaea stagnalis emphasized the potential ecological hazard from sublethal concentrations of pollutants (including those exemplified by synthetic surfactants and detergents). http://www.ncbi.nlm.nih.gov/pubmed/15648211; PMID: 15648211 [PubMed - indexed for MEDLINE]; http://scipeople.com/uploads/materials/4389/4Rivista.Biologia97p39Aquatic..Bioreactor.RTF; https://www.researchgate.net/profile/Sergei_Ostroumov/blog/407_New_concept_of_ecosystem; https://www.researchgate.net/profile/Sergei_Ostroumov/blog/410_New_Concept_of_Ecosystem;
26. Ostroumov S. A. Some aspects of water filtering activity of filter-feeders // Hydrobiologia, 2005. Vol. 542, No. 1. P. 275 – 286. http://scipeople.com/uploads/materials/4389/5Hydr542p275water.filt.doc; http://www.springerlink.com/content/u21p83p0423j8714/;
27. Ostroumov S. A., Widdows J. Inhibition of mussel suspension feeding by surfactants of three classes. // Hydrobiologia. 2006. Vol. 556, No. 1. Pages: 381 – 386. [For the first time the negative effects of the three surfactants on the filtration rates by marine mussels were presented in one paper. The xenobiotics tested represented anionic, cationic and non-ionic surfactants (tetradecyltrimethylammonium bromide, TDTMA, a representative of a class of cationic surfactants; sodium dodecyl sulphate, SDS, a representative of anionic alkyl sulfates; and Triton X-100, a representative of non-ionic hydroxyethylated alkyl phenols). Negative effects of SDS, TDTMA, and Triton X-100 on the filtration activity of marine mussels M. edulis and M. edulis / M. galloprovincialis were discovered. All three surfactants inhibited the clearance rates. This is the first publication of the negative effects of a cationic surfactant on Atlantic mussels Mytilus. The significance of the results for the ecology of marine ecosystems is discussed]. DOI 10.1007/s10750-005-1200-7; http://sites.google.com/site/ostroumovsergei/publications-1/hydrobiologia2006ostwidd; http://sites.google.com/site/3surfactantsfiltrationmytilus/; http://scipeople.ru/uploads/materials/4389/_Hydrobiologia2006%20vol%20556%20No.1%20pages381-386.pdf; http://www.springerlink.com/content/7166067538534421/;
28. Ostroumov S. A. Basics of the molecular-ecological mechanism of water quality formation and water self-purification. - Contemporary Problems of Ecology, 2008 (Feb), Vol. 1, No. 1, p. 147-152. [ISSN 1995-4255(Print) 1995-4263 (Online); DOI 10.1134/S1995425508010177; https://www.researchgate.net/file.FileLoader.html?key=e533be77c87735c6dcc5cfdb9db96cec; http://scipeople.com/uploads/materials/4389/CPEC2008BasicsMolEcol.Mech.WaterQuali(0147.pdf; http://www.springerlink.com/content/e380263154u73045/;
29. Ostroumov S. A. Biotic self-purification of aquatic ecosystems: from the theory to ecotechnologies. - Ecologica, 2007, vol. 15 (50), p.15-23. (ISSN 0354-3285). Some basic elements of a new theory for the biological mechanism for water self-purification are presented. Aquatic organisms (hydrobionts) are actively involved in various processes leading to water purification. Not only microorganisms (bacteria, cyanobacteria and fungi), but also algae, plants, invertebrates, and other groups of organisms are involved, which is discussed and analyzed in the paper. Results of the author's experiments that study the effects of various pollutants on aquatic organisms (freshwater and marine bivalves) are given. The theory is an innovative basis for developing ecological technologies to clean water and to upgrade its quality by using organisms and ecosystems [http://scindeks.nb.rs/article.aspx?artid=0354-32850750015O];
30. Ostroumov S.A., Shestakova T.V. Decreasing the measurable concentrations of Cu, Zn, Cd, and Pb in the water of the experimental systems containing Ceratophyllum demersum: The phytoremediation potential // Doklady Biological Sciences. 2009, Vol. 428, No. 1, p. 444-447. www.springerlink.com/index/ML1062K7271L318N.pdf; http://sites.google.com/site/9dbs444/; https://www.researchgate.net/file.FileLoader.html?key=8fd8998627b86102db72c9b237c25054;
31. Ostroumov S.A. Towards the general theory of ecosystem-depended control of water quality. - Ecologica, 2009, vol. 16, No. 54, p. 25-32. (Faculty of Biology, Moscow State University, Leninskie Gory, Moscow, 119991 Russia). Abstract: A new set of ecological generalizations formulated in this paper represent, in a systematized form, the basic elements of the qualitative theory of biotic control of water quality and water self-purification in freshwater and marine ecosystems. The theory contributes to a better understanding of the issues of stability and regulation in the biosphere. The theory is supported by the results of the author’s experimental studies of the effects exerted by surfactants, detergents and other pollutants on aquatic organisms. http://sites.google.com/site/9enecologica16p25theory/;
32. Ostroumov S.A. Suspension-feeders as factors influencing water quality in aquatic ecosystems. - In: The Comparative Roles of Suspension-Feeders in Ecosystems, R.F. Dame, S. Olenin (Eds.), Springer, Dordrecht, 2004. p. 147-164. [Proceedings of the Advanced Research Workshop on the Comparative Roles of Suspension-Feeders in Ecosystems, Nida, Lithuania 4–9 October 2003. Suspension-feeders are found in both pelagic and benthic systems. They function as an important part of an ecosystem's biomachinery that maintains water quality and purification potential in aquatic systems. They remove suspended matter and excrete faeces, pseudofaeces and dissolved inorganic materials that contribute to nutrient cycling between the water column and the benthic habitats. Suspension-feeders are a key part of many natural aquatic remediation systems and they can decrease some negative anthropogenic impacts. Recent author’s experiments are reported that demonstrate new effects of pollutants on the filtration rates of suspension-feeders. Table 1: factors decreasing water quality in aquatic ecosystems; Table 2: how filter-feeders may produce effects on 9 processes of water purification (chemical oxidation by oxygen, photodegradation etc.); Table 3: quantitative data on filter-feeders of 12 large taxa (Rotifers, Polychaeta etc.); Table 4: amount of the days for the water column to be filtered in 20 ecosystems; Table 5: production of biosediments per year or per day by filter-feeders; Table 6: chemicals that inhibit filtration rates (mainly the data generated by the author); Table 7: Key facts and principles that characterize suspension - feeders as part of water-filtering biomachinery maintaining water quality; Table 8: the level-block approach to the analysis of ecological hazards of anthropogenic effects on the biota. New concepts: polyfunctional role of suspension-feeders regulating ecosystem processes (p.155); "suspension-feeders have a potential to contribute to creating habitat heterogeneity (in terms of patchiness of concentrations of suspended matter in water) (p.157); "ecological taxation: suspension-feeders pay ecological tax to the community (ecosystem)" (p.157)]. ISBN 978-1-4020-3028-4 (Print) 978-1-4020-3030-7 (Online). DOI 10.1007/1-4020-3030-4_9.
Some of the publications above and the results in them won awards and Diplomas, including:
Diploma at the 1st International Forum on Conservancy of Nature (Moscow, 7- 9th September 2005), signed by the Co-Chairs of the Forum, Deputy Minister of Natural Resources of Russian Federation and Vice-President of the Trade Chamber of Russian Federation).
Diploma of the journal 'Ecology and Life' (awarded 15 October 2005).
Diploma of the competition 'Sustainable use of natural resources and environmental protection – strategy of sustainable development of Russia in the 21st century' at the international conference 'Sustainable Development: Nature-Society-Man' (organized in 2006, Moscow, by the Ministry of Natural Resources) for the paper by Ostroumov S.A. and Solomonova E.A. "On studies of water self-purification and interactions between pollutants (surfactants) and biota: searching approaches to issues relevant to sustainable use of water resources " (Directive of the Ministry of Natural Resources No.126 of 02 June 2006; the Diploma was signed by the Minister).
Diploma to the book 'Biotic Mechanism of Self-purification of Freshwater and Marine Water' by Dr. S. A. Ostroumov, awarded at the 7th International Conference ‘Aquatic Ecosystems, Organisms, Innovations’ (2005). Diploma of the Academy of Aquatic Sciences for the series of innovative publications on aquatic ecology, interactions between chemicals and organisms, and water self-purification, including the books 'Biological Effects of Surfactants in Connection with the Anthropogenic Impact on the Biosphere'; 'Biological Effects of Surfactants on Organisms'; 'Biotic Mechanism of Self-Purification of Freshwater and Marine Water'; 'Pollution, Self-Purification and Restoration of Aquatic Ecosystems'; 'Biological Effects of Surfactants', (awarded in 2006).
Diploma of the Academy of Aquatic Sciences 'for his innovative contribution to improvement of environmental and ecological education', including the book 'Ecology and Hydrobiology. Curricula of Lecture Courses' (awarded in 2006).
Diploma of the Moscow Society of the Researchers of Nature (awarded in 2007).
The publications above [1-32] and other publications authored and coauthored by S.A.Ostroumov were commented and cited as valuable contributions in the following publications:
33. Chatzinikolaou Y., Ioannou A., Lazaridou M. Intra-basin spatial approach on pollution load estimation in a large Mediterranean river. – Desalination. 2010 (January) Volume 250, Issue 1, Pages 118-129. DOI:10.1016/j.desal.2008.12.062.
34. Chatzinikolaou Y., Lazaridou M. Identification of the self-purification stretches of the Pinios River, Central Greece. - Mediterranean Marine Science, 2007, Volume 8/2, p.19-32.
35. Dingjiang Chen, Jun Lu, Yena Shen. (D. Chen, J. Lu, Y. Shen) Artificial neural network modelling of concentrations of nitrogen, phosphorus and dissolved oxygen in a non-point source polluted river in Zhejiang Province, southeast China. // Hydrological Processes. Early View (Articles online in advance of print); Published Online: 21 Oct 2009; Copyright © 2010 John Wiley & Sons, Ltd.
36. Mohneke, M., Rödel, M.-O. Declining amphibian populations and possible ecological consequences - A review. // Salamandra, 2009, 45 (4), pp. 203-210.
37. Dafforn, K.A., Glasby, T.M., Johnston, E.L. Links between estuarine condition and spatial distributions of marine invaders // Diversity and Distributions 2009, v. 15 (5), pp. 807-821.
38. Stabili, L., Licciano, M., Longo, C., Corriero, G., Mercurio, M. Evaluation of microbiological accumulation capability of the commercial sponge Spongia officinalis var. adriatica (Schmidt) (Porifera, Demospongiae) Water Research, 2008, vol. 42 (10-11), pp. 2499-2506.
39. Bussell, J.A., Gidman, E.A., Causton, D.R., Gwynn-Jones, D., Malham, S.K., Jones, M.L.M., Reynolds, B., Seed, R. Changes in the immune response and metabolic fingerprint of the mussel, Mytilus edulis (Linnaeus) in response to lowered salinity and physical stress. - Journal of Experimental Marine Biology and Ecology, 2008, v. 358 (1), pp. 78-85.
40. Hartig E.K., Grozev O., Rozenzweig C. Climate change, agriculture and wetlands in Eastern Europe: vulnerability, adaptation and policy // Climatic Change 1997. 36: 107–121.
41. Timofeev N. P. Ecological relations of agricultural populations of ecdysteroid-containing plants Rhaponticum carthamoides (Willd.) Iljin and Serratula coronata L. with herbivorous insects. Report 2. Composition variability of phytoecdysteroids in agrocenoses and their role in the vulnerability of plants to phytophagans. - Contemporary Problems of Ecology [MAIK Nauka/Interperiodica distributed by Springer Science+Business Media LLC.; ISSN 1995-4255 (Print) 1995-4263 (Online)]; 2009 (December) Volume 2, Number 6, p. 531-541. [DOI 10.1134/S1995425509060071]. Translated from: Sibirskii Ekologicheskii Zhurnal, 2009, Vol. 16, No. 6, pp. 829–842.
42. Abakumov V.A. Development of some concepts and issues of ecology and hydrobiology. — Ecol. Studies, Haz., Sol., 2006, v. 11, p. 34-38.
43. Abakumov V.A. Innovative approaches to remediation and restoration of polluted aquatic systems. – Water: Technology and Ecology. 2007. No. 4. p. 69-73.
44. Abakumov V.A. New achievements in the studies of aquatic ecosystems and organisms: the concept of ecological repair. - Water: Technology and Ecology. 2007. No. 2. p. 70-71.
45. Abakumov V.A. New advances in remediation and restoration of polluted aquatic systems. – Problems of Biogeochemistry and Geochemical Ecology. 2007, No. 2 (4), 98-100.
46. Abakumov V.A. New concept in the development of the theory of water self-purification: ecological repair. – Problems of Biogeochemistry and Geochemical Ecology. 2007, No. 2 (4), 45-46.
47. Aizdaicher N. A., Zh. V. Markina. Toxic effects of detergents on the alga Plagioselmis prolonga (Cryptophyta) // Russian Journal of Marine Biology [MAIK Nauka/Interperiodica, distributed by Springer ISSN1063-0740 (Print) 1608-3377 (Online)] Vol. 32, No. 1. 2006. P. 45-49. www.springerlink.com/index/D5P746W5P9G4G452.pdf. DOI 10.1134/S1063074006010068.
48. Ali, A.M.M. 2007. Water quality enhancement in Sloterbinnenpolder (Amsterdam, the Netherlands) by adopting ecological engineering approaches. M.Sc.Thesis EC 07.17. UNESCO-IHE (Institute for Water Education). 92 p.
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50. Brooks, B.W., Riley, T.M., Taylor, R.D. Water quality of effluent-dominated ecosystems: Ecotoxicological, hydrological, and management considerations. - Hydrobiologia, 2006, 556 (1), pp. 365-379.
51. Carr G. M. Water Quality for Ecosystem and Human Health. United Nations Environment Programme Global Environment Monitoring System/Water Programme. 2006. 122 p. (ISBN 92-95039-10-6). [http://www.gemswater.orghttp://www.gemstat.orgtel; http://www.gemswater.org/digital_atlas/digital_atlas.pdf.]
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53. Dobrovolsky G.V. About development of some concepts of the teaching on the biosphere (the 80th anniversary of the publication of the book 'Biosphere' by V.I.Vernadsky). — Water: Technology and Ecology. 2007. No. 1, p. 63-68.
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FULL TEXTS OF SOME OF THE PUBLICATIONS, comments, and CONTENTS in a nutshell see at:
http://blog.researchgate.net/masterblog/619_Vital_role_of_aquatic_organisms_in_improving_water_quality;
http://blog.researchgate.net/masterblog/610_New_unified_theory_of_the_ecological_mechanisms_to_improve_water_quality_and_to_make_water_clear_a_basis_for_water_purification_and_waste_water_treatment;
http://blog.researchgate.net/masterblog/608_Does_implementation_of_environmental_law_depend_on_new_improvement_of_ecological_terms_Fundamental_solutions_suggested;
http://blog.researchgate.net/masterblog/594_New_plant_species_as_a_potent_tool_to_clean_water_and_to_remove_heavy_metals;
http://blog.researchgate.net/masterblog/466_The_Threat_of_Shampoo_to_the_Biosphere;
http://blog.researchgate.net/masterblog/410_A_New_Concept_For_Ecosystems;
http://blog.researchgate.net/masterblog/389_Stopping_Pollution_Eutrophication_and_Algal_Blooms;
http://blog.researchgate.net/masterblog/379_Underwater_Secrets_of_Global_Change;
http://blog.researchgate.net/masterblog/369_Vulnerability_of_Major_Plankton_Groups_Rotifers;
http://blog.researchgate.net/masterblog/358_Three_New_Key_Hazards_to_the_Functioning_of_the_Biosphere;
http://blog.researchgate.net/masterblog/299_Inhibitory_Analysis_A_new_method_for_analyzing_interactions_between_organisms_in_ecosystems;
https://www.researchgate.net/profile/Sergei_Ostroumov/blog/347_Biodiversity_and_stability_of_ecosystems;
http://blog.researchgate.net/masterblog/276_New_threat_to_water_quality_discovery_of_the_new_important_type_of_hazards_from_pollution_Synecological_summation_of_effects_on_different_trophic_levels;
http://blog.researchgate.net/masterblog/255_Criteria_of_ecological_hazards_due_to_anthropogenic_effects_on_the_biota_Searching_for_a_system;
http://blog.researchgate.net/masterblog/262__The_Concept_of_Aquatic_Biota_as_a_Labile_and_Vulnerable_Component_of_the_Water_SelfPurification_System;
http://blog.researchgate.net/masterblog/241_innovative_concept_of_ecosystem_as_a_multifunctional_bioreactor_one_of_its_functions_is_upgrading_water_quality_ecosystem_service;
http://blog.researchgate.net/masterblog/180_A_new_type_of_effect_of_potentially_hazardous_substances
http://blog.researchgate.net/masterblog/369_Vulnerability_of_Major_Plankton_Groups_Rotifers;
https://www.researchgate.net/profile.ProfileBlogEntry.html?dbw=true&blogId=373;
https://www.researchgate.net/profile/Sergei_Ostroumov/blog/388_new_keys_to_prevent_pollution_eutrophication_algal_blooms;
http://blog.researchgate.net/masterblog/379_Underwater_Secrets_of_Global_Change;
https://www.researchgate.net/profile/Sergei_Ostroumov/blog/407_New_concept_of_ecosystem
https://www.researchgate.net/profile/Sergei_Ostroumov/blog/410_New_Concept_of_Ecosystem;
http://blog.researchgate.net/masterblog/410_A_New_Concept_For_Ecosystems;
http://sites.google.com/site/2000dbs371p204criteria/
http://sites.google.com/site/2000dbs373p397biocatallstag/
http://sites.google.com/site/2000dbs374p514bioreactor/
http://sites.google.com/site/2001dbs379p378pellets/
http://sites.google.com/site/2001dbs377p139inhibitory/
http://sites.google.com/site/2001dbs378p248effammaroyst/
http://sites.google.com/site/2001dbs380p499synerg/
http://sites.google.com/site/2001dbs380p492unio/
http://sites.google.com/site/2dbs382p18biodivers/;
http://sites.google.com/site/bioeffectsofsurfactants/
http://sites.google.com/site/surfactantinhibitfilterfeed02/
http://sites.google.com/site/3surfactantsfiltrationmytilus/
http://sites.google.com/site/9dbs444/;
https://www.researchgate.net/file.FileLoader.html?key=8fd8998627b86102db72c9b237c25054;
http://scipeople.com/uploads/materials/4389/Danbio6_2001v381n5.E.eutrophication.pdf;
https://www.researchgate.net/file.FileLoader.html?key=d988acb599e121964c48114374a87e8d;
https://www.researchgate.net/file.FileLoader.html?key=888352078b275ef40a430eb5b4d7714c; https://www.researchgate.net/profile/Sergei_Ostroumov/blog/359_How_to_establish_a_new_type_of_reserves_to_protect_aquatic_biodiversity_and_ecosystem_services;
https://www.researchgate.net/file.FileLoader.html?key=997c8c86899d5a6e24531054ad1bcd1e;
https://www.researchgate.net/file.FileLoader.html?key=e533be77c87735c6dcc5cfdb9db96cec;
http://scipeople.com/uploads/materials/4389/CPEC2008BasicsMolEcol.Mech.WaterQuali(0147.pdf;
http://scipeople.com/uploads/materials/4389/5Hydr542p275water.filt.doc;
http://www.moipros.ru/files/author_4_article_9.doc; http://scipeople.com/uploads/materials/4389/2Hydrobiologia469p117w%20Addendum.DOC;
http://scipeople.com/uploads/materials/4389/4Rivista.Biologia97p39Aquatic..Bioreactor.RTF;
http://scipeople.com/uploads/materials/4389/3RivistaBio96Priorities2.rtf;
http://scipeople.com/users/2943391/
http://scipeople.com/group/334/
http://scipeople.com/group/334/topic/1485/
https://www.researchgate.net/profile/Sergei_Ostroumov/blog/409_most_cited_publications_by_Dr_SA_Ostroumov_in_English_available_online;
http://blog.researchgate.net/masterblog/466_The_Threat_of_Shampoo_to_the_Biosphere;
http://scipeople.com/uploads/materials/4389/2010Nakoplenie.Preprint(Part.1.(BioshereEcotoxGeochem.doc;
ADDITIONAL REFERENCES OF RELEVANT PUBLICATIONS see:
http://sites.google.com/site/ostroumovsapublicationsineng/
http://sites.google.com/site/ostroumovsergei/
http://sites.google.com/site/bioticupgradewaterquality2008/
http://sites.google.com/site/ostroumovsa/
http://sites.google.com/site/biochemicalecology/
http://sites.google.com/site/ostroumovsapublicationsruen/
http://sites.google.com/site/ostroumovsergei/publications-that-cited-saostroumov
http://sites.google.com/site/biosphereostroumov/home
http://sites.google.com/site/ecologytobemostcitedtomorrow/home
http://sites.google.com/site/ecologytobemostcitedtomorrow/list-of-publications-by-sa-ostroumov
http://scipeople.ru/users/2943391/
https://www.researchgate.net/profile/Sergei_Ostroumov/blog/321_Discovery_of_the_system_where_chemical_pollution_could_impair_the_regulation_and_balance_in_the_abundance_of_phytoplankton_threat_to_ecological_stability_ ;
POSITIVE EVALUATIONS of some of the results published by S.A. Ostroumov see in:
Petrosyan V.S. Review of the book: Biological Effects of Surfactants. CRC Press. Taylor & Francis. - Ecological Studies, Hazards, Solutions, 2007. vol. 12, p. 117-119 (in English);
Review of the book: Ostroumov S.A. Biological Effects of Surfactants. CRC Press. Taylor & Francis. Boca Raton, London, New York. 2006. 279 p. – Bulletin Samarskaya Luka. - 2007. - V. 16, № 4(22). - P. 864-867. Bibliogr. 10 refs. http://www.ssc.smr.ru/media/journals/samluka/2007/16_4_22.pdf;
Review of the book: Biological Effects of Surfactants. CRC Press. Taylor & Francis. Boca Raton, London, New York. 2006. 279 p. // Problems of Biogeochemistry and Geochemical Ecology. 2007. № 2 (4). p.108;
Review of the book: S.A. Ostroumov. Biological Effects of Surfactants (2006). - Ecologica, 2008. v.15, No. 51, p. 71-72. (ISSN 0354-3285; in English);
Review of the book: Ostroumov S.A. Biological Effects of Surfactants. CRC Press. Taylor & Francis. Boca Raton, London, New York. 2006. 279 p. – Toxicological Review [Toksikologicheskij Vestnik], 2009, No. 2, p. 40;
POSITIVE COMMENTS OF INTERNATIONAL EXPERTS see:
http://blog.researchgate.net/masterblog/347_Biodiversity_and_stability_of_ecosystems;
https://www.researchgate.net/group/Water_quality_Water_self-purification_role_of_biota/board/thread/4400_A_new_way_of_eutrophication_control?viewLast=true;
https://www.researchgate.net/group/Water_quality_Water_self-purification_role_of_biota/board/thread/4412_want_to_be_part_of_you?viewLast=true;
https://www.researchgate.net/group/Science_Communication/board/thread/4494_New_data_help_save_energy_and_effort_in_water_trea?c=16875#c16875;
https://www.researchgate.net/group/Environmental_researches_malacology/board/thread/2179_Sewage_outfalls_into_water_courses?viewLast=true;
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The concise results and shortlist of some well-cited publications on ecology and environment - in English, the full texts or abstracts available online free
(публикация автора на scipeople)
Ostroumov S. A.
, 2010
The concise results and shortlist of some well-cited publications on ecology and environment - in English, the full texts or abstracts available online free (updated 2010, Feb 11)
The publications by S.A. Ostroumov in the main part of the list...
The concise results and shortlist of some well-cited publications on ecology and environment - in English, the full texts or abstracts available online free (updated 2010, Feb 11)
The publications by S.A. Ostroumov in the main part of the list below include those that described some innovations in conceptualization of the fundamentals of ecology, – such as the notion of ecosystem [15]. Previously, in the book ‘Introduction to Biochemical Ecology’, the same author explored another fundamental issue of ecology and made a new classification of interorganismal interactions mediated by chemicals. Also, some of the publications given below formulated a new theory of the biomachinery that provides the useful ecosystem’s service of improving water quality [2, 4, 14, 20, 24, 25, 31]. In another essential series of publications, a set of new biological effects of man-made chemicals were discovered [1, 6, 12, 16, 19, 27; and others]. As a result, some new hazards of chemical pollution to the biosphere were found [1, 2, 12, 17, 19, 21]. Practical recommendations to better protect aquatic biodiversity were published [18], which was a continuation of the book ‘Conservation of Living Nature and Resources: Problems, Trends, Prospects’ (by A. Yablokov, S. Ostroumov, Springer Press). Steps towards new technologies to combat pollution were made [30]. A list of priorities in further research on most urgent issues of ecology and environment was developed [23].
The publications [1-32] and other publications authored and coauthored by S.A.O. were commented and supported in the papers and books by many other authors [33-117]. Among them are the scientists who work in N. America (e.g., [50, 61, 100, 103]), Europe (e.g., [58, 68-70, 79, 84 ]; including France, Spain, Greece), Asia (e.g., [72, 81, 88, 101, 117]; including China and India), and other parts of the world.
KEY WORDS: ecosystem, pollutants, biomachinery that provide the ecosystem’s service of improving water quality, new biological effects of man-made chemicals, new hazards of chemical pollution to the biosphere, recommendations to better protect aquatic biodiversity, conservation of nature and Resources, new phytotechnologies to combat pollution, priorities, environment protection; water self-purification; surfactants, detergents, filter-feeders, environmental safety
REFERENCES:
1. book: Ostroumov S. A. Biological Effects of Surfactants. CRC Press. Taylor & Francis. Boca Raton, London, New York. 2006. 279 p. ISBN 0-8493-2526-9 [new facts and concepts on assessment of hazards from chemicals, new look on the factors important to water quality, to sustainability; new priorities in environmental safety]; the table of contents see at: http://www.chipsbooks.com/biosurfc.htm;
2. Ostroumov S. A. The concept of aquatic biota as a labile and vulnerable component of the water self-purification system - Doklady Biological Sciences, Vol. 372, 2000, pp. 286–289. http://sites.google.com/site/2000dbs372p286biotalabil/;
3. Ostroumov S. A., Kolesnikov M. P. Biocatalysis of Matter Transfer in a Microcosm Is Inhibited by a Contaminant: Effects of a Surfactant on Limnea stagnalis. - Doklady Biological Sciences, 2000, 373: 397–399. Translated from Doklady Akademii Nauk, 2000, Vol. 373, No. 2, pp. 278–280. http://sites.google.com/site/2000dbs373p397biocatallstag/;
4. Ostroumov S. A. An aquatic ecosystem: a large-scale diversified bioreactor with a water self-purification function. - Doklady Biological Sciences, 2000. Vol. 374, P. 514-516. http://sites.google.com/site/2000dbs374p514bioreactor/ ;
5. Ostroumov S.A. Criteria of ecological hazards due to anthropogenic effects on the biota: searching for a system. - Dokl Biol Sci (Doklady Biological Sciences). 2000; 371: 204-206. http://sites.google.com/site/2000dbs371p204criteria/ ;
6. Ostroumov S. A. An amphiphilic substance inhibits the mollusk capacity to filter out phytoplankton cells from water. - Biology Bulletin, 2001, Volume 28, Number 1, p. 95-102. ISSN 1062-3590 (Print) 1608-3059 (Online); DOI 10.1023/A:1026671024000; http://www.springerlink.com/content/l665628020163255/;
7. Ostroumov S. A. Inhibitory Analysis of Regulatory Interactions in Trophic Webs. - Doklady Biological Sciences, 2001, Vol. 377, pp. 139–141. Translated from Doklady Akademii Nauk, 2000, Vol. 375, No. 6, pp. 847–849. [In the paper, the author developed a new approach to analyze the fundamental ecological issue, the interactions between organisms in ecosystems. He suggested using the methodology of inhibitory analysis to study interactions in trophic chains. Important situation is the top–down control of plankton by benthic filter-feeders. This control, as the author’s experiments have shown, might be removed by chemical inhibitors (the latter may enter the ecosystem as pollutants)]. http://sites.google.com/site/2001dbs377p139inhibitory/; http://blog.researchgate.net/masterblog/299_Inhibitory_Analysis_A_new_method_for_analyzing_interactions_between_organisms_in_ecosystems;
8. Ostroumov SA. The synecological approach to the problem of eutrophication. - Dokl Biol Sci. (Doklady Biological Sciences). 2001; 381: 559-562. PMID: 12918433 [PubMed - indexed for MEDLINE]; http://scipeople.com/uploads/materials/4389/Danbio6_2001v381n5.E.eutrophication.pdf ;
9. Ostroumov SA. The hazard of a two-level synergism of synecological summation of anthropogenic effects. - Dokl Biol Sci. (Doklady Biological Sciences). 2001; 380: 499-501. http://sites.google.com/site/2001dbs380p499synerg/ ; PMID: 12918416 [PubMed - indexed for MEDLINE];
10. Ostroumov SA. Responses of Unio tumidus to mixed chemical preparations and the hazard of synecological summation of anthropogenic effects. - Dokl Biol Sci (Doklady Biological Sciences). 2001; 380: 492-495. http://sites.google.com/site/2001dbs380p492unio/; PMID: 12918414 [PubMed - indexed for MEDLINE];
11. Ostroumov SA, Kolesnikov MP. Pellets of some mollusks in the biogeochemical flows of C, N, P, Si, and Al. - Dokl Biol Sci (Doklady Biological Sciences). 2001; 379: 378-381. http://sites.google.com/site/2001dbs379p378pellets/; PMID: 12918380 [PubMed - indexed for MEDLINE];
12. Ostroumov SA. Imbalance of factors providing control of unicellular plankton populations exposed to anthropogenic impact. - Dokl Biol Sci (Doklady Biological Sciences). 2001; 379: 341-343. PMID: 12918370 [PubMed - indexed for MEDLINE]; http://sites.google.com/site/1dbs379p341imbalance/; https://www.researchgate.net/profile/Sergei_Ostroumov/blog/321_Discovery_of_the_system_where_chemical_pollution_could_impair_the_regulation_and_balance_in_the_abundance_of_phytoplankton_threat_to_ecological_stability_ ;
13. Ostroumov SA. Effect of amphiphilic chemicals on filter-feeding marine organisms. - Dokl Biol Sci (Doklady Biological Sciences). 2001; 378: 248-250. For the first time, oysters were used as the test-organisms in bioassay of synthetic surfactants and detergents. The new data revealed a novel type of hazard to mariculture. New negative effects of surfactants and chemical mixtures on water filtering activity of Crassostrea gigas were discovered. http://sites.google.com/site/2001dbs378p248effammaroyst/; PMID: 12918342 [PubMed - indexed for MEDLINE];
14. Ostroumov SA. Biodiversity protection and quality of water: the role of feedbacks in ecosystems. - Dokl Biol Sci (Doklady Biological Sciences). 2002; 382: 18-21; http://sites.google.com/site/2dbs382p18biodivers/; http://www.citeulike.org/pdf/user/ATP/article/6113559/ostroumov_02_biodiversity.pdf;
15. Ostroumov S.A. New definitions of the concepts and terms ecosystem and biogeocenosis. - Doklady Biological Sciences 2002 (March), Volume 383, Numbers 1- 6, p. 141-143. [ISSN 0012-4966 (Print) 1608-3105 (Online)]. https://www.researchgate.net/file.FileLoader.html?key=997c8c86899d5a6e24531054ad1bcd1e; PMID: 12053565 [PubMed - indexed for MEDLINE];
16. Ostroumov SA. A new type of effect of potentially hazardous substances: uncouplers of pelagial-benthal coupling. - Dokl Biol Sci (Doklady Biological Sciences). 2002; 383: 127-130. https://www.researchgate.net/file.FileLoader.html?key=d988acb599e121964c48114374a87e8d; www.springerlink.com/index/28V23JBFADL1Y100.pdf; In the paper new facts are reported that shows man-made hazards to 3 aspects of functioning of the biosphere and ecosystems: (1) formation of water quality; (2) biogeochemical flows of C, N, P and other constituents of biomass; (3) formation of deposits of organic matter as bottom sediments. https://www.researchgate.net/profile/Sergei_Ostroumov/blog/358_Three_new_key_hazards_to_the_functioning_of_the_biosphere; PMID: 12053562 [PubMed - indexed for MEDLINE];
17. Ostroumov S. A. Identification of a New Type of Ecological Hazard of Chemicals: Inhibition of Processes of Ecological Remediation. - Doklady Biological Sciences, Vol. 385, 2002 (November), pp. 377–379. [Translated from Doklady Akademii Nauk, Vol. 385, No. 4, 2002, pp. 571–573]. PMID: 12469618 [PubMed - indexed for MEDLINE]; https://www.researchgate.net/file.FileLoader.html?key=8408a7cfaa984764b812ce79c77007f2;
18. Ostroumov SA. System of principles for conservation of the biogeocenotic function and the biodiversity of filter-feeders. - Dokl Biol Sci (Doklady Biological Sciences). 2002; 383: 147-150. https://www.researchgate.net/file.FileLoader.html?key=888352078b275ef40a430eb5b4d7714c; https://www.researchgate.net/profile/Sergei_Ostroumov/blog/359_How_to_establish_a_new_type_of_reserves_to_protect_aquatic_biodiversity_and_ecosystem_services; PMID: 12053567 [PubMed - indexed for MEDLINE];
19. Ostroumov S. A. Inhibitory analysis of top-down control: new keys to studying eutrophication, algal blooms, and water self-purification // Hydrobiologia. 2002. vol. 469. P.117-129. A new approach to prevent pollution, eutrophication, and algal blooms was identified and analyzed in this paper. The approach is based on efficient use of the natural mechanisms of self-regulation of ecosystem DOI 10.1023/A:1015559123646; http://www.moipros.ru/files/author_4_article_9.doc; www.springerlink.com/index/R9PTJEQ5FK8VLA6M.pdf; http://scipeople.com/uploads/materials/4389/2Hydrobiologia469p117w%20Addendum.DOC;
20. Ostroumov S.A. Polyfunctional role of biodiversity in processes leading to water purification: current conceptualizations and concluding remarks. - Hydrobiologia, 2002 (February), 469: 203-204. DOI 10.1007/s10750-004-1875-1; http://scipeople.com/uploads/materials/4389/2H469p203.Polyfunctional.role.w.Addendum.rtf; http://www.springerlink.com/content/hcrfvmdncdm8e3pf/;
21. Ostroumov S. A., Walz N., Rusche R. Effect of a cationic amphiphilic compound on rotifers. - Doklady Biological Sciences. 2003 (May). Vol. 390. p. 252-255 [ISSN 0012-4966 (Print) 1608-3105 (Online)]. PMID: 12940156 [PubMed - indexed for MEDLINE]; https://www.researchgate.net/file.FileLoader.html?key=def6575c794b111fcc31275e853c2b15;
22. Ostroumov S.A. Anthropogenic effects on the biota: towards a new system of principles and criteria for analysis of ecological hazards. - Rivista di Biologia/Biology Forum. 2003. 96: 159-170. Review. PMID: 12852181 [PubMed - indexed for MEDLINE] http://sites.google.com/site/ostroumovsergei/publications-1/rivista2003criteria; http://scipeople.com/uploads/materials/4389/3RB96p159Anth..Criteria.doc; www.ncbi.nlm.nih.gov/pubmed/12852181;
23. Ostroumov S.A., Dodson S., Hamilton D., Peterson S., Wetzel R.G. Medium-term and long-term priorities in ecological studies // Rivista di Biologia / Biology Forum. 2003 (May). 96: 327-332. Abstracts in Eng. and Italian (p. 332). http://scipeople.com/uploads/materials/4389/3RivistaBio96Priorities2.rtf; www.ncbi.nlm.nih.gov/pubmed/14595906 ; PMID: 14595906 [PubMed - indexed for MEDLINE] Research priorities in ecology and environmental sciences for the future are formulated. The priorities for both fundamental and applied ecology are proposed. The list of priorities includes 50 items. The priorities are relevant to terrestrial, aquatic, and general ecology. The list of priorities is helpful when grant proposals are being prepared, evaluated, and selected for funding.
24. Ostroumov S. A. On the biotic self-purification of aquatic ecosystems: elements of the theory. - Doklady Biological Sciences, 2004, Vol. 396, Numbers 1- 6, p. 206-211. https://www.researchgate.net/file.FileLoader.html?key=60f338228d6f3c5114d223ab81e15d3b; https://www.researchgate.net/profile/Sergei_Ostroumov/blog/348_Useful_theory_of_natural_mechanisms_of_improving_water_quality; PMID: 15354827 [PubMed - indexed for MEDLINE];
25. Aquatic ecosystem as a bioreactor: water purification and some other functions. - Rivista di Biologia / Biology Forum, 2004, 97 (1): 67-78. Abstracts in Eng. and Italian. [A new fundamental concept is proposed of aquatic ecosystem as a bioreactor that carries out the function of water purification in natural water bodies and streams. The ecosystem as a bioreactor has the following characteristic attributes: (1) it is a large-scale (large-volume) bioreactor; (2) it is a diversified (in terms of the number of taxa and the scope of functional activities) bioreactor; (3) it possesses a broad range of biocatalytic (chemical-transforming and degrading) capabilities. New experimental data on xenobiotics - induced inhibition of the water filtration performed by the bivalve molluscs Unio tumidus, U. pictorum, M. galloprovincialis and inhibition of feeding by Limnaea stagnalis emphasized the potential ecological hazard from sublethal concentrations of pollutants (including those exemplified by synthetic surfactants and detergents). http://www.ncbi.nlm.nih.gov/pubmed/15648211; PMID: 15648211 [PubMed - indexed for MEDLINE]; http://scipeople.com/uploads/materials/4389/4Rivista.Biologia97p39Aquatic..Bioreactor.RTF; https://www.researchgate.net/profile/Sergei_Ostroumov/blog/407_New_concept_of_ecosystem; https://www.researchgate.net/profile/Sergei_Ostroumov/blog/410_New_Concept_of_Ecosystem;
26. Ostroumov S. A. Some aspects of water filtering activity of filter-feeders // Hydrobiologia, 2005. Vol. 542, No. 1. P. 275 – 286. http://scipeople.com/uploads/materials/4389/5Hydr542p275water.filt.doc; http://www.springerlink.com/content/u21p83p0423j8714/;
27. Ostroumov S. A., Widdows J. Inhibition of mussel suspension feeding by surfactants of three classes. // Hydrobiologia. 2006. Vol. 556, No. 1. Pages: 381 – 386. [For the first time the negative effects of the three surfactants on the filtration rates by marine mussels were presented in one paper. The xenobiotics tested represented anionic, cationic and non-ionic surfactants (tetradecyltrimethylammonium bromide, TDTMA, a representative of a class of cationic surfactants; sodium dodecyl sulphate, SDS, a representative of anionic alkyl sulfates; and Triton X-100, a representative of non-ionic hydroxyethylated alkyl phenols). Negative effects of SDS, TDTMA, and Triton X-100 on the filtration activity of marine mussels M. edulis and M. edulis / M. galloprovincialis were discovered. All three surfactants inhibited the clearance rates. This is the first publication of the negative effects of a cationic surfactant on Atlantic mussels Mytilus. The significance of the results for the ecology of marine ecosystems is discussed]. DOI 10.1007/s10750-005-1200-7; http://sites.google.com/site/ostroumovsergei/publications-1/hydrobiologia2006ostwidd; http://sites.google.com/site/3surfactantsfiltrationmytilus/; http://scipeople.ru/uploads/materials/4389/_Hydrobiologia2006%20vol%20556%20No.1%20pages381-386.pdf; http://www.springerlink.com/content/7166067538534421/;
28. Ostroumov S. A. Basics of the molecular-ecological mechanism of water quality formation and water self-purification. - Contemporary Problems of Ecology, 2008 (Feb), Vol. 1, No. 1, p. 147-152. [ISSN 1995-4255(Print) 1995-4263 (Online); DOI 10.1134/S1995425508010177; https://www.researchgate.net/file.FileLoader.html?key=e533be77c87735c6dcc5cfdb9db96cec; http://scipeople.com/uploads/materials/4389/CPEC2008BasicsMolEcol.Mech.WaterQuali(0147.pdf; http://www.springerlink.com/content/e380263154u73045/;
29. Ostroumov S. A. Biotic self-purification of aquatic ecosystems: from the theory to ecotechnologies. - Ecologica, 2007, vol. 15 (50), p.15-23. (ISSN 0354-3285). Some basic elements of a new theory for the biological mechanism for water self-purification are presented. Aquatic organisms (hydrobionts) are actively involved in various processes leading to water purification. Not only microorganisms (bacteria, cyanobacteria and fungi), but also algae, plants, invertebrates, and other groups of organisms are involved, which is discussed and analyzed in the paper. Results of the author's experiments that study the effects of various pollutants on aquatic organisms (freshwater and marine bivalves) are given. The theory is an innovative basis for developing ecological technologies to clean water and to upgrade its quality by using organisms and ecosystems [http://scindeks.nb.rs/article.aspx?artid=0354-32850750015O];
30. Ostroumov S.A., Shestakova T.V. Decreasing the measurable concentrations of Cu, Zn, Cd, and Pb in the water of the experimental systems containing Ceratophyllum demersum: The phytoremediation potential // Doklady Biological Sciences. 2009, Vol. 428, No. 1, p. 444-447. www.springerlink.com/index/ML1062K7271L318N.pdf; http://sites.google.com/site/9dbs444/; https://www.researchgate.net/file.FileLoader.html?key=8fd8998627b86102db72c9b237c25054;
31. Ostroumov S.A. Towards the general theory of ecosystem-depended control of water quality. - Ecologica, 2009, vol. 16, No. 54, p. 25-32. (Faculty of Biology, Moscow State University, Leninskie Gory, Moscow, 119991 Russia). Abstract: A new set of ecological generalizations formulated in this paper represent, in a systematized form, the basic elements of the qualitative theory of biotic control of water quality and water self-purification in freshwater and marine ecosystems. The theory contributes to a better understanding of the issues of stability and regulation in the biosphere. The theory is supported by the results of the author’s experimental studies of the effects exerted by surfactants, detergents and other pollutants on aquatic organisms. http://sites.google.com/site/9enecologica16p25theory/;
32. Ostroumov S.A. Suspension-feeders as factors influencing water quality in aquatic ecosystems. - In: The Comparative Roles of Suspension-Feeders in Ecosystems, R.F. Dame, S. Olenin (Eds.), Springer, Dordrecht, 2004. p. 147-164. [Proceedings of the Advanced Research Workshop on the Comparative Roles of Suspension-Feeders in Ecosystems, Nida, Lithuania 4–9 October 2003. Suspension-feeders are found in both pelagic and benthic systems. They function as an important part of an ecosystem's biomachinery that maintains water quality and purification potential in aquatic systems. They remove suspended matter and excrete faeces, pseudofaeces and dissolved inorganic materials that contribute to nutrient cycling between the water column and the benthic habitats. Suspension-feeders are a key part of many natural aquatic remediation systems and they can decrease some negative anthropogenic impacts. Recent author’s experiments are reported that demonstrate new effects of pollutants on the filtration rates of suspension-feeders. Table 1: factors decreasing water quality in aquatic ecosystems; Table 2: how filter-feeders may produce effects on 9 processes of water purification (chemical oxidation by oxygen, photodegradation etc.); Table 3: quantitative data on filter-feeders of 12 large taxa (Rotifers, Polychaeta etc.); Table 4: amount of the days for the water column to be filtered in 20 ecosystems; Table 5: production of biosediments per year or per day by filter-feeders; Table 6: chemicals that inhibit filtration rates (mainly the data generated by the author); Table 7: Key facts and principles that characterize suspension - feeders as part of water-filtering biomachinery maintaining water quality; Table 8: the level-block approach to the analysis of ecological hazards of anthropogenic effects on the biota. New concepts: polyfunctional role of suspension-feeders regulating ecosystem processes (p.155); "suspension-feeders have a potential to contribute to creating habitat heterogeneity (in terms of patchiness of concentrations of suspended matter in water) (p.157); "ecological taxation: suspension-feeders pay ecological tax to the community (ecosystem)" (p.157)]. ISBN 978-1-4020-3028-4 (Print) 978-1-4020-3030-7 (Online). DOI 10.1007/1-4020-3030-4_9.
Some of the publications above and the results in them won awards and Diplomas, including:
Diploma at the 1st International Forum on Conservancy of Nature (Moscow, 7- 9th September 2005), signed by the Co-Chairs of the Forum, Deputy Minister of Natural Resources of Russian Federation and Vice-President of the Trade Chamber of Russian Federation).
Diploma of the journal 'Ecology and Life' (awarded 15 October 2005).
Diploma of the competition 'Sustainable use of natural resources and environmental protection – strategy of sustainable development of Russia in the 21st century' at the international conference 'Sustainable Development: Nature-Society-Man' (organized in 2006, Moscow, by the Ministry of Natural Resources) for the paper by Ostroumov S.A. and Solomonova E.A. "On studies of water self-purification and interactions between pollutants (surfactants) and biota: searching approaches to issues relevant to sustainable use of water resources " (Directive of the Ministry of Natural Resources No.126 of 02 June 2006; the Diploma was signed by the Minister).
Diploma to the book 'Biotic Mechanism of Self-purification of Freshwater and Marine Water' by Dr. S. A. Ostroumov, awarded at the 7th International Conference ‘Aquatic Ecosystems, Organisms, Innovations’ (2005). Diploma of the Academy of Aquatic Sciences for the series of innovative publications on aquatic ecology, interactions between chemicals and organisms, and water self-purification, including the books 'Biological Effects of Surfactants in Connection with the Anthropogenic Impact on the Biosphere'; 'Biological Effects of Surfactants on Organisms'; 'Biotic Mechanism of Self-Purification of Freshwater and Marine Water'; 'Pollution, Self-Purification and Restoration of Aquatic Ecosystems'; 'Biological Effects of Surfactants', (awarded in 2006).
Diploma of the Academy of Aquatic Sciences 'for his innovative contribution to improvement of environmental and ecological education', including the book 'Ecology and Hydrobiology. Curricula of Lecture Courses' (awarded in 2006).
Diploma of the Moscow Society of the Researchers of Nature (awarded in 2007).
The publications above [1-32] and other publications authored and coauthored by S.A.Ostroumov were commented and cited as valuable contributions in the following publications:
33. Chatzinikolaou Y., Ioannou A., Lazaridou M. Intra-basin spatial approach on pollution load estimation in a large Mediterranean river. – Desalination. 2010 (January) Volume 250, Issue 1, Pages 118-129. DOI:10.1016/j.desal.2008.12.062.
34. Chatzinikolaou Y., Lazaridou M. Identification of the self-purification stretches of the Pinios River, Central Greece. - Mediterranean Marine Science, 2007, Volume 8/2, p.19-32.
35. Dingjiang Chen, Jun Lu, Yena Shen. (D. Chen, J. Lu, Y. Shen) Artificial neural network modelling of concentrations of nitrogen, phosphorus and dissolved oxygen in a non-point source polluted river in Zhejiang Province, southeast China. // Hydrological Processes. Early View (Articles online in advance of print); Published Online: 21 Oct 2009; Copyright © 2010 John Wiley & Sons, Ltd.
36. Mohneke, M., Rödel, M.-O. Declining amphibian populations and possible ecological consequences - A review. // Salamandra, 2009, 45 (4), pp. 203-210.
37. Dafforn, K.A., Glasby, T.M., Johnston, E.L. Links between estuarine condition and spatial distributions of marine invaders // Diversity and Distributions 2009, v. 15 (5), pp. 807-821.
38. Stabili, L., Licciano, M., Longo, C., Corriero, G., Mercurio, M. Evaluation of microbiological accumulation capability of the commercial sponge Spongia officinalis var. adriatica (Schmidt) (Porifera, Demospongiae) Water Research, 2008, vol. 42 (10-11), pp. 2499-2506.
39. Bussell, J.A., Gidman, E.A., Causton, D.R., Gwynn-Jones, D., Malham, S.K., Jones, M.L.M., Reynolds, B., Seed, R. Changes in the immune response and metabolic fingerprint of the mussel, Mytilus edulis (Linnaeus) in response to lowered salinity and physical stress. - Journal of Experimental Marine Biology and Ecology, 2008, v. 358 (1), pp. 78-85.
40. Hartig E.K., Grozev O., Rozenzweig C. Climate change, agriculture and wetlands in Eastern Europe: vulnerability, adaptation and policy // Climatic Change 1997. 36: 107–121.
41. Timofeev N. P. Ecological relations of agricultural populations of ecdysteroid-containing plants Rhaponticum carthamoides (Willd.) Iljin and Serratula coronata L. with herbivorous insects. Report 2. Composition variability of phytoecdysteroids in agrocenoses and their role in the vulnerability of plants to phytophagans. - Contemporary Problems of Ecology [MAIK Nauka/Interperiodica distributed by Springer Science+Business Media LLC.; ISSN 1995-4255 (Print) 1995-4263 (Online)]; 2009 (December) Volume 2, Number 6, p. 531-541. [DOI 10.1134/S1995425509060071]. Translated from: Sibirskii Ekologicheskii Zhurnal, 2009, Vol. 16, No. 6, pp. 829–842.
42. Abakumov V.A. Development of some concepts and issues of ecology and hydrobiology. — Ecol. Studies, Haz., Sol., 2006, v. 11, p. 34-38.
43. Abakumov V.A. Innovative approaches to remediation and restoration of polluted aquatic systems. – Water: Technology and Ecology. 2007. No. 4. p. 69-73.
44. Abakumov V.A. New achievements in the studies of aquatic ecosystems and organisms: the concept of ecological repair. - Water: Technology and Ecology. 2007. No. 2. p. 70-71.
45. Abakumov V.A. New advances in remediation and restoration of polluted aquatic systems. – Problems of Biogeochemistry and Geochemical Ecology. 2007, No. 2 (4), 98-100.
46. Abakumov V.A. New concept in the development of the theory of water self-purification: ecological repair. – Problems of Biogeochemistry and Geochemical Ecology. 2007, No. 2 (4), 45-46.
47. Aizdaicher N. A., Zh. V. Markina. Toxic effects of detergents on the alga Plagioselmis prolonga (Cryptophyta) // Russian Journal of Marine Biology [MAIK Nauka/Interperiodica, distributed by Springer ISSN1063-0740 (Print) 1608-3377 (Online)] Vol. 32, No. 1. 2006. P. 45-49. www.springerlink.com/index/D5P746W5P9G4G452.pdf. DOI 10.1134/S1063074006010068.
48. Ali, A.M.M. 2007. Water quality enhancement in Sloterbinnenpolder (Amsterdam, the Netherlands) by adopting ecological engineering approaches. M.Sc.Thesis EC 07.17. UNESCO-IHE (Institute for Water Education). 92 p.
49. Beacham W., C. J. Moseley. Beacham's Guide to Environmental Issues & Sources. Washington: Beacham Publishing, 1993. – 3335 p. [ISBN: 0933833318].
50. Brooks, B.W., Riley, T.M., Taylor, R.D. Water quality of effluent-dominated ecosystems: Ecotoxicological, hydrological, and management considerations. - Hydrobiologia, 2006, 556 (1), pp. 365-379.
51. Carr G. M. Water Quality for Ecosystem and Human Health. United Nations Environment Programme Global Environment Monitoring System/Water Programme. 2006. 122 p. (ISBN 92-95039-10-6). [http://www.gemswater.orghttp://www.gemstat.orgtel; http://www.gemswater.org/digital_atlas/digital_atlas.pdf.]
52. Danilov-Danil’yan V. I., M. V. Bolgov, V. G. Dubinina, V. S. Kovalevskii, A. G. Kocharyan, N. M. Novikova. Assessment of admissible runoff withdrawals in small river basins: Methodological principles // Water Resources [MAIK Nauka/ Interperiodica, distributed by Springer; ISSN 0097-8078 (Print) 1608-344X (Online)]. 2006, Vol. 33, No. 2. P.205-218. DOI10.1134/S0097807806020096. (Original Russian Text: V.I. Danilov-Danil’yan, M.V. Bolgov, V.G. Dubinina, V.S. Kovalevskii, A.G. Kocharyan, N.M. Novikova, 2006, published in ‘Vodnye Resursy’ 2006, Vol. 33, No. 2, p. 224–238).
53. Dobrovolsky G.V. About development of some concepts of the teaching on the biosphere (the 80th anniversary of the publication of the book 'Biosphere' by V.I.Vernadsky). — Water: Technology and Ecology. 2007. No. 1, p. 63-68.
54. Dobrovolsky G.V. On the 80th anniversary of the book 'The Biosphere' by V.I.Vernadsky. Developing some important parts of the teaching on the biosphere. – Ecological Chemistry (Ekologicheskaya Khimiya). 2007, v.16(3), p.135–143.
55. Dobrovolsky G.V., G.S.Rozenberg, I.K. Toderas (Editors). Discovery of a New Type of Hazardous Anthropogenic Impact in Ecology of Animals and the Biosphere: Inhibition of the Filtration Activity of Bivalves by Surfactants. 2nd edition. Moscow. MAX Press. 2008. 108 p.
56. Dolgonosov B.M., Gubernatorova, T.N. A nonlinear model of contaminant transformations in an aquatic environment, 2005, Water Resources, 32 (3), pp. 291-304 [MAIK Nauka/ Interperiodica distributed by Springer. ISSN 0097-8078 (Print) 1608-344X (Online)]; Translated from ‘Vodnye Resursy’, Vol. 32, No. 3, 2005, pp. 322–336.
57. Dolgonosov B.M., Gubernatorova, T.N. Kinetics of the enzymatic decomposition of macromolecules with a fractal structure. - Theoretical Foundations of Chemical Engineering, 2007, 41 (6), pp. 868-877.
58. Fauvet, G., Claret, C., Marmonier, P. Influence of benthic and interstitial processes on nutrient changes along a regulated reach of a large river (Rhône River, France). - Hydrobiologia 2001, 445, pp. 121-131.
59. Ferk F., Misik M., Hoelzl C., Uhl M., Fuerhacker M., Grillitsch B., Parzefall W., Nersesyan A., Micieta K., Grummt T., Ehrlich V., Knasmüller S. Benzalkonium chloride (BAC) and dimethyldioctadecyl-ammonium bromide (DDAB), two common quaternary ammonium compounds, cause genotoxic effects in mammalian and plant cells at environmentally relevant concentrations // Mutagenesis. 2007 22(6): 363-370.
60. Filippenko, V. N. Gravi- and chemotropisms of the primary maize roots when affected by lead and cadmium. - Russian Journal of Plant Physiology, 2001, Vol. 48; Number 1, p. 12-18. [Nauka/ Interperiodica Publishing, USA, ISSN 1021-4437(Print) 1608-3407 (Online)] DOI10.1023/A:1009082011029 (translated from: Fiziologiia Rastenii).
61. Fisenko A. I. A new long-term on site clean-up approach applied to non-point sources of pollution // Water, Air, & Soil Pollution. 2004, Vol. 156, No. 1-4, p. 1-27.
62. Fuchedzhi O. A., S. A. Konnova, A. S. Boiko and V. V. Ignatov Role of the clasping-leaved pondweed ( Potamogeton perfoliatus) polysaccharides in formation of its bacterial environment. – Microbiology [MAIK Nauka/Interperiodica distributed by Springer Science+Business Media LLC.; ISSN 0026-2617 (Print) 1608-3237 (Online)] 2008 Volume 77, Number 1, p. 84-89. DOI10.1007/s11021-008-1012-7. Translated from:
63. Fuchedzhi O. A., S. A. Konnova, A. S. Boiko, V. V. Ignatov. Rol' polisakharidov rdesta pronzennolistnogo v formirovanii ego bakterial'nogo okruzheniya. - Mikrobiologiya - 2008, Vol. 77, No. 1, P. 96-102. [MAIK "Nauka/Interperiodica" Russian Academy of Science].
64. Gaidin A. M. Formirovanie khimicheskogo sostava vody pri zatoplenii sernykh kar'erov. -Geoekologiya. Inzhenernaya geologiya. Gidrogeologiya.Geokriologiya - 2008, No. 2, P. 118-123.
65. Gifford, S., Dunstan, R.H., O'Connor, W., Koller, C.E., MacFarlane, G.R. Aquatic zooremediation: deploying animals to remediate contaminated aquatic environments. - 2007. Trends in Biotechnology 25 (2), pp. 60-65.
66. Glazovsky N. F. Change in the anthropogenic geochemical impact on the biosphere// GeoJournal [Springer, Netherlands ISSN0343-2521 (Print) 1572-9893 (Online)] 1990, Volume 20, Number 2, P.115-119.
67. Goldsmith F. B. Review: Conservation of Living Nature and Resources. - The Journal of Ecology, 1992. Vol. 80, No. 1, p. 186-187.
68. Grande, R., Di Pietro, S., Di Campli, E., Di Bartolomeo, S., Filareto, B., Cellini, L. Bio-toxicological assays to test water and sediment quality. - Journal of Environmental Science and Health - Part A Toxic/Hazardous Substances and Environmental Engineering, 2007, 42 (1), pp. 33-38.
69. Hernandez, I., Fernandez-Engo, M.A., Perez-Llorens, J.L., Vergara, J.J. Integrated outdoor culture of two estuarine macroalgae as biofilters for dissolved nutrients from Sparus aurata waste waters. – 2005, Journal of Applied Phycology, 17 (6), pp. 557-567.
70. Hernandez, I., Perez-Pastor, A., Vergara, J.J., Martinez-Aragon, J.F., Fernandez-Engo, M.A., Perez-Llorens, J.L. Studies on the biofiltration capacity of Gracilariopsis longissima: From microscale to macroscale. 2006. Aquaculture, 252 (1), p. 43-53.
71. Investing in Natural Capital: The Ecological Economics Approach to Sustainability (Editors: AnnMari Jansson, Monica Hammer, Robert Costanza, Carl Folke, Sandra Koskoff); Publisher: Island Press. 1994. 520 p. [Series: Intl Society for Ecological Economics] [ISBN-13: 9781559633161].
72. Jiang, J.-G., Shen, Y.-F. Estimation of the natural purification rate of a eutrophic lake after pollutant removal, 2006, Ecological Engineering, 28 (2), pp. 166-173.
73. Jhones C. C., L. Gama, L. Giddings, V. Rico-Gray, A. Velazquez. Caracterizacion de los paisajes terrestres actuales de la peninsula de Yucatan. - Investigaciones Geograficas, 2000, Issue: 42, p. 28-39. [ISSN: 01884611].
74. Kapitsa A.P. Formulation of fundamental principles for foundation of the theory of the apparatus of the biosphere. – Environment Ecology and Safety of Life Activity. 2007. No. 1 (37). P. 68-71.
75. Kapitsa A.P. Establishing the fundamental principles for the theory of the apparatus of the biosphere. – Problems of Biogeochemistry and Geochemical Ecology. 2007, No. 2 (4), 1-4.
76. Kondratyev K. Ya., A. A. Buznikov, O. M. Pokrovskii. Global Change and Remote Sensing. 1996 Wiley, 370 p. [ ISBN:0471960780].
77. Kriksunov E.A. The new developments in studying contemporary issues of ecology, hydrobiology, and environmental sciences. [A review of volume 11 of the series "Ecological Studies, Hazards, Solutions" (Moscow, MAX Press, 2006, 208 p., ed. by S.A.O.)]. – Ecology of Environment and Life Safety. 2006, No. 6. p. 93.
78. Kuznetsov O.L. (Editor) Ability of synthetic surfactants to decrease the filtering activity of bivalves (Diploma of Scientific Discovery No. 274). - Scientific Discoveries (Collection of short description of scientific discoveries – 2005) Мoscow. The International Academy of Authors of Scientific Discoveries and Inventions. 2006. P. 5-8. [ISBN 5-87499-062-8].
79. Licciano, M., Terlizzi, A., Giangrande, A., Cavallo, R.A., Stabili, L. Filter-feeder macroinvertebrates as key players in culturable bacteria biodiversity control: A case of study with Sabella spallanzanii (Polychaeta: Sabellidae). 2007. Marine Environmental Research, 64 (4), p. 504-513.
80. Lobova T.I., Y.V. Barkhatov, L.Y. Popova. Antibiotic resistance of heterotrophic bacteria in Shira Lake: natural and anthropogenic impacts. - Aquatic Microbial Ecology. 2002. Vol. 30, no. 1, pp. 11-18.
81. Makushkin, E.O., Korsunov, V.M. Self-purification of water current and the role of microbiological transformation of organic matter in the system of the Selenga river and its delta. - Doklady Biological Sciences, 2005, 404 (1-6), pp. 372-374 [MAIK Nauka/Interperiodica, distributed by Springer Science+Business Media LLC. ISSN 0012-4966 (Print) 1608-3105 (Online)] Translated from ‘Doklady Akademii Nauk’, Vol. 404, No. 4, 2005, p. 567–569.
82. Markina Zh. V., N. A. Aizdaicher. Influence of laundry detergents on the abundance dynamics and physiological state of the benthic microalga Attheya ussurensis (Bacillariophyta) in laboratory culture // Russian Journal of Marine Biology [MAIK Nauka/Interperiodica distributed by Springer Science+Business Media LLC; ISSN 1063-0740 (Print) 1608-3377 (Online)]. 2007. Volume 33, Number 6, P. 391-398. DOI 10.1134/S1063074007060053. http://www.springerlink.com/content/9704t6101872x474/;
83. Mearns, A.J., Reish, D.J., Oshida, P.S., Buchman, M., Ginn, T., Donnelly, R. Effects of pollution on marine organisms. - Water Environment Research, 2007. v. 79 (10), p. 2102-2160.
84. Neofitou, C., Dimitriadis, A., Pantazis, P., Psilovikos, A., Neofitou, N., Paleokostas, A. Self-purification of a long-stretched gully affects the restoration of an alpine-type lake in northern Greece. - Fresenius Environmental Bulletin, 2005.14 (12 A), p. 1141-1149.
85. Nikiforov S. M. The Use of Data on Allozyme Variability in Marine Invertebrate Populations for Biological Monitoring // Russian Journal of Marine Biology, 2001, Volume 27, Supplement 1, P. S27-S37.
86. Ostergren, D. An Organic Act after a Century of Protection: The Context, Content, and Implications of the 1995 Russian Federation Law on Specially Protected Natural Areas. - Natural Resources Journal, 2001, Vol. 41; Part 1, p.125-152 [Publisher: University of New Mexico, USA, ISBN ISSN0028-0739].
87. Prevodnik, A., Lilja, K., Bollner, T. Benzo[a]pyrene up-regulates the expression of the proliferating cell nuclear antigen (PCNA) and multixenobiotic resistance polyglycoprotein (P-gp) in Baltic Sea blue mussels (Mytilus edulis L.). - 2007. Comparative Biochemistry and Physiology - C Toxicology and Pharmacology, 145 (2), p. 265-274. [doi:10.1016/j.cbpc.2006.12.014]
88. Ren, R.-L., Liu, M.-S., Zhang, J.-M., Zhang, M., Xu, M. Self-purification ability of a water-carrying lake. 2007. Chinese Journal of Ecology 26 (8), pp. 1222-1227.
89. Rozenberg G.S. Ostroumov Sergei Andreevich [the bibliography of the main 5 monographs published during the period 1983 – 2004]. – In the book: Ecology in Pictures. Togliatti. Publishing house of the Institute of Ecology of Volga Basin, Russian Academy of Sciences, 2007, p.146. ISBN 978-5-93424-298-6.
90. Ryabushkina N. A. Synergism of Metabolite Action in Plant Responses to Stresses. - Russian Journal of Plant Physiology. 2005. Vol. 52, No. 4. P. 547-552 [ISSN 1021-4437 (Print) 1608-3407 (Online)] [MAIK Nauka/Interperiodica distributed by Springer Science+Business Media LLC.] Translated from ‘Fiziologiya Rastenii’, Vol. 52, No. 4, 2005, pp. 614–621.
91. Safi, K.A., Hewitt, J.E., Talman, S.G. The effect of high inorganic seston loads on prey selection by the suspension-feeding bivalve, Atrina zelandica .- 2007. Journal of Experimental Marine Biology and Ecology 344 (2), p. 136-148 .
92. Samuilov, V.D., Fedorenko, T.A. Lag Phase of CO2-Dependent O2 Evolution by Illuminated Anabaena variabilis Cells. 1999. Biochemistry (Moscow) 64 (6), pp. 610-619.
93. Saratovskikh E. A., E. V. Shtamm. Effects of chlorinated phenols on DNA stability [= Vliyanie khlorsoderzhashchikh fenolov na stabil'nost' DNK]. - Khimicheskaya Fizika. 2007. - Vol. 26, No. 7, p. 67-73. [MAIK "Nauka/ Interperiodica"].
94. Selivanovskaya S.Y., V.Z. Latypova, N.Y. Stepanova, Y.T. Hung. Bioassay of Industrial and Hazardous Waste Pollutants. - In: Handbook of Industrial and Hazardous Wastes Treatment: Second Edition, Revised and Expanded (Editors: Lawrence K. Wang, Yung-Tse Hung, Howard H. Lo, Constantine Yapijakis) CRC Press, 2004, (in toto 1345 p.) [ISBN 0824741145, 9780824741143] P. 15-62.
95. Selivanovskaya S.Y., V.Z. Latypova, N.Y. Stepanova, Y.T. Hung . Bioassay of Industrial Waste Pollutant. - In: Hazardous Industrial Waste Treatment (Editors: L. K. Wang, Y.-T. Hung, H. H. Lo, C. Yapijakis). CRC Press, 2007, P. 15-62 (in toto 516 p.) [ISBN 0849375746, 9780849375743] [books.google.com].
96. Soldatov A. A., Gostyukhina O. L., Golovina I. V. Antioxidant enzyme complex of tissues of the bivalve Mytilus galloprovincialis Lam. under normal and oxidative-stress conditions: A review. - Applied Biochemistry and Microbiology, 2007. Vol. 43; No. 5, p. 556-562. [Publisher Springer Science + Business Media, ISSN 0003-6838, Translated from the journal: ‘Prikladnaia Biokhimiia i Mikrobiologiia’].
97. Stabili, L., Licciano, M., Giangrande, A., Longo, C., Mercurio, M., Marzano, C.N., Corriero, G. Filtering activity of Spongia officinalis var. adriatica (Schmidt) (Porifera, Demospongiae) on bacterioplankton: Implications for bioremediation of polluted seawater. - 2006, Water Research, v. 40 (16), pp. 3083-3090.
98. Valkiunas G. Practical importance of parasitic diseases: An outlook from the point of view of ecological parasitology. - Ekologija (Vilnius). 2001. Nr. 3, p. 28-33. [ISSN 0235–7224].
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101. Wang X., Y. An, J. Zhang, X. Shi, C. Zhu, R. Li , M. Zhu, S. Chen. Contribution of biological processes to self-purification of water with respect to petroleum hydrocarbon associated with No. 0 diesel in Changjiang Estuary and Jiaozhou Bay, China // Hydrobiologia, 2002. Volume 469, Numbers 1-3, P. 179-191.
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104. Goldsmith F. B. Review: Conservation of Living Nature and Resources, by A. V. Yablokov; S. A. Ostroumov. - The Journal of Ecology, 1992. Vol. 80, No. 1, p. 186-187.
105. Zaitsev Iu.P., V.O. Mamaev, V. Mamaev. Marine Biological Diversity in the Black Sea: A Study of Change and Decline. - 1997 - United Nations Publications.
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110. Melekhova O.P., E.I.Egorova, T.I.Evseeva, V.M.Glazer, S.A.Geras'kin, YU.K.Doronin, A.A.Kitashova, A.V.Kitashov, YU.P.Kozlov, I.A.Kondrat'eva, G.V.Kossova, S.V.Kotelevtsev, D.N.Matorin, S.A.Ostroumov, S.I.Pogosyan, A.V.Smurov, G.N.Solovykh, A.L.Stepanov, N.A.Tushmalova, L.V.Cacenko. Biological Control of the Environment: Bioindication and Biotesting. Мoscow: Publishing Center Academia 2007, 288 p. ISBN 978-5-7695-3560-4.
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112. Ermakov V. V., Tjutikov S.F. Geohimicheskaja ekologija zhivotnyh. – Moscow: Nauka, 2008;
113. Bussell, J. A., E. A. Gidman, D. R. Causton, D.Gwynn-Jones, S. K. Malham, M. L.M. Jones, B. Reynolds and R.Seed. Changes in the immune response and metabolic fingerprint of the mussel, Mytilus edulis (Linnaeus) in response to lowered salinity and physical stress. - Journal of Experimental Marine Biology and Ecology. 2008, Volume 358, Issue 1, Pages 78-85. [doi:10.1016/j.jembe.2008.01.018]
114. Jiang, J.-G., and Y.-F. Shen. Estimation of the natural purification rate of a eutrophic lake after pollutant removal. - Ecological Engineering. 2006, Volume 28, Issue 2, Pages 166-173. [doi:10.1016/j.ecoleng.2006.06.002]
115. Safi K. A., J. E. Hewitt and S. G. Talman. The effect of high inorganic seston loads on prey selection by the suspension-feeding bivalve, Atrina zelandica. - Journal of Experimental Marine Biology and Ecology, 2007, Volume 344, Issue 2, Pages 136-148.
116. Pandey J., Chauhan A., Jain R.K. Integrative approaches for assessing the ecological sustainability of in situ bioremediation. - FEMS Microbiology Reviews 2008, Volume 33, Issue 2, Pages 324 – 375.
117. Samal N. R.; A. Mazumdar; K. D. Jöhnk; F. Peeters. Assessment of ecosystem health of tropical shallow waterbodies in eastern India using turbulence model. - Aquatic Ecosystem Health & Management, 1539-4077, Volume 12, Issue 2, 2009, Pages 215 – 225.
FULL TEXTS OF SOME OF THE PUBLICATIONS, and SHORT CONTENTS see at:
http://blog.researchgate.net/masterblog/299_Inhibitory_Analysis_A_new_method_for_analyzing_interactions_between_organisms_in_ecosystems;
https://www.researchgate.net/profile/Sergei_Ostroumov/blog/347_Biodiversity_and_stability_of_ecosystems;
http://blog.researchgate.net/masterblog/276_New_threat_to_water_quality_discovery_of_the_new_important_type_of_hazards_from_pollution_Synecological_summation_of_effects_on_different_trophic_levels;
http://blog.researchgate.net/masterblog/255_Criteria_of_ecological_hazards_due_to_anthropogenic_effects_on_the_biota_Searching_for_a_system;
http://blog.researchgate.net/masterblog/262__The_Concept_of_Aquatic_Biota_as_a_Labile_and_Vulnerable_Component_of_the_Water_SelfPurification_System;
http://blog.researchgate.net/masterblog/241_innovative_concept_of_ecosystem_as_a_multifunctional_bioreactor_one_of_its_functions_is_upgrading_water_quality_ecosystem_service;
http://blog.researchgate.net/masterblog/180_A_new_type_of_effect_of_potentially_hazardous_substances
http://blog.researchgate.net/masterblog/369_Vulnerability_of_Major_Plankton_Groups_Rotifers;
https://www.researchgate.net/profile.ProfileBlogEntry.html?dbw=true&blogId=373;
https://www.researchgate.net/profile/Sergei_Ostroumov/blog/388_new_keys_to_prevent_pollution_eutrophication_algal_blooms;
http://blog.researchgate.net/masterblog/379_Underwater_Secrets_of_Global_Change;
https://www.researchgate.net/profile/Sergei_Ostroumov/blog/407_New_concept_of_ecosystem
https://www.researchgate.net/profile/Sergei_Ostroumov/blog/410_New_Concept_of_Ecosystem;
http://blog.researchgate.net/masterblog/410_A_New_Concept_For_Ecosystems;
http://sites.google.com/site/2000dbs371p204criteria/
http://sites.google.com/site/2000dbs373p397biocatallstag/
http://sites.google.com/site/2000dbs374p514bioreactor/
http://sites.google.com/site/2001dbs379p378pellets/
http://sites.google.com/site/2001dbs377p139inhibitory/
http://sites.google.com/site/2001dbs378p248effammaroyst/
http://sites.google.com/site/2001dbs380p499synerg/
http://sites.google.com/site/2001dbs380p492unio/
http://sites.google.com/site/2dbs382p18biodivers/;
http://sites.google.com/site/bioeffectsofsurfactants/
http://sites.google.com/site/surfactantinhibitfilterfeed02/
http://sites.google.com/site/3surfactantsfiltrationmytilus/
http://sites.google.com/site/9dbs444/;
https://www.researchgate.net/file.FileLoader.html?key=8fd8998627b86102db72c9b237c25054;
http://scipeople.com/uploads/materials/4389/Danbio6_2001v381n5.E.eutrophication.pdf;
https://www.researchgate.net/file.FileLoader.html?key=d988acb599e121964c48114374a87e8d;
https://www.researchgate.net/file.FileLoader.html?key=888352078b275ef40a430eb5b4d7714c; https://www.researchgate.net/profile/Sergei_Ostroumov/blog/359_How_to_establish_a_new_type_of_reserves_to_protect_aquatic_biodiversity_and_ecosystem_services;
https://www.researchgate.net/file.FileLoader.html?key=997c8c86899d5a6e24531054ad1bcd1e;
https://www.researchgate.net/file.FileLoader.html?key=e533be77c87735c6dcc5cfdb9db96cec;
http://scipeople.com/uploads/materials/4389/CPEC2008BasicsMolEcol.Mech.WaterQuali(0147.pdf;
http://scipeople.com/uploads/materials/4389/5Hydr542p275water.filt.doc;
http://www.moipros.ru/files/author_4_article_9.doc; http://scipeople.com/uploads/materials/4389/2Hydrobiologia469p117w%20Addendum.DOC;
http://scipeople.com/uploads/materials/4389/4Rivista.Biologia97p39Aquatic..Bioreactor.RTF;
http://scipeople.com/uploads/materials/4389/3RivistaBio96Priorities2.rtf;
http://scipeople.com/users/2943391/
http://scipeople.com/group/334/
http://scipeople.com/group/334/topic/1485/
https://www.researchgate.net/profile/Sergei_Ostroumov/blog/409_most_cited_publications_by_Dr_SA_Ostroumov_in_English_available_online;
http://blog.researchgate.net/masterblog/466_The_Threat_of_Shampoo_to_the_Biosphere;
http://scipeople.com/uploads/materials/4389/2010Nakoplenie.Preprint(Part.1.(BioshereEcotoxGeochem.doc;
ADDITIONAL REFERENCES OF RELEVANT PUBLICATIONS see:
http://sites.google.com/site/ostroumovsapublicationsineng/
http://sites.google.com/site/ostroumovsergei/
http://sites.google.com/site/bioticupgradewaterquality2008/
http://sites.google.com/site/ostroumovsa/
http://sites.google.com/site/biochemicalecology/
http://sites.google.com/site/ostroumovsapublicationsruen/
http://sites.google.com/site/ostroumovsergei/publications-that-cited-saostroumov
http://sites.google.com/site/biosphereostroumov/home
http://sites.google.com/site/ecologytobemostcitedtomorrow/home
http://sites.google.com/site/ecologytobemostcitedtomorrow/list-of-publications-by-sa-ostroumov
http://scipeople.ru/users/2943391/
https://www.researchgate.net/profile/Sergei_Ostroumov/blog/321_Discovery_of_the_system_where_chemical_pollution_could_impair_the_regulation_and_balance_in_the_abundance_of_phytoplankton_threat_to_ecological_stability_ ;
POSITIVE EVALUATIONS of some of the results published by S.A. Ostroumov see in:
Petrosyan V.S. Review of the book: Biological Effects of Surfactants. CRC Press. Taylor & Francis. - Ecological Studies, Hazards, Solutions, 2007. vol. 12, p. 117-119 (in English);
Review of the book: Ostroumov S.A. Biological Effects of Surfactants. CRC Press. Taylor & Francis. Boca Raton, London, New York. 2006. 279 p. – Bulletin Samarskaya Luka. - 2007. - V. 16, № 4(22). - P. 864-867. Bibliogr. 10 refs. http://www.ssc.smr.ru/media/journals/samluka/2007/16_4_22.pdf;
Review of the book: Biological Effects of Surfactants. CRC Press. Taylor & Francis. Boca Raton, London, New York. 2006. 279 p. // Problems of Biogeochemistry and Geochemical Ecology. 2007. № 2 (4). p.108;
Review of the book: S.A. Ostroumov. Biological Effects of Surfactants (2006). - Ecologica, 2008. v.15, No. 51, p. 71-72. (ISSN 0354-3285; in English);
Review of the book: Ostroumov S.A. Biological Effects of Surfactants. CRC Press. Taylor & Francis. Boca Raton, London, New York. 2006. 279 p. – Toxicological Review [Toksikologicheskij Vestnik], 2009, No. 2, p. 40;
POSITIVE COMMENTS OF INTERNATIONAL EXPERTS see:
http://blog.researchgate.net/masterblog/347_Biodiversity_and_stability_of_ecosystems;
https://www.researchgate.net/group/Water_quality_Water_self-purification_role_of_biota/board/thread/4400_A_new_way_of_eutrophication_control?viewLast=true;
https://www.researchgate.net/group/Water_quality_Water_self-purification_role_of_biota/board/thread/4412_want_to_be_part_of_you?viewLast=true;
https://www.researchgate.net/group/Science_Communication/board/thread/4494_New_data_help_save_energy_and_effort_in_water_trea?c=16875#c16875;
https://www.researchgate.net/group/Environmental_researches_malacology/board/thread/2179_Sewage_outfalls_into_water_courses?viewLast=true;
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4. |
Effects of sodium dodecylbenzene sulfonate and sodium dodecyl sulfate on the Mytilus galloprovincialis biomarker system
(публикация автора на scipeople)
Liu B., Z. Yu, X. Song, F. Yang
- Ecotoxicology and Environmental Safety , 2010
Effects of sodium dodecylbenzene sulfonate and sodium dodecyl sulfate on the Mytilus galloprovincialis biomarker system.
Liu B., Z. Yu, X. Song, F. Yang - Ecotoxicology and Environmental Safety, 2009.
doi:10.1016/j.ecoenv.2009.12.011 | How to Cite...
Effects of sodium dodecylbenzene sulfonate and sodium dodecyl sulfate on the Mytilus galloprovincialis biomarker system.
Liu B., Z. Yu, X. Song, F. Yang - Ecotoxicology and Environmental Safety, 2009.
doi:10.1016/j.ecoenv.2009.12.011 | How to Cite or Link Using DOI
Crown copyright © 2009 Published by Elsevier Inc.
Bo Liu a, b, Corresponding Author Contact Information, E-mail The Corresponding Author, Zhiming Yu a, Xiuxian Song a and Fei Yang b
a Key Laboratory of Marine Ecology & Environmental Sciences, Institute of Oceanology, Chinese Academy of Sciences, Qingdao 266071, China
b Key Laboratory of Marine Bio-resources Sustainable Utilization in Liaoning Province’s University, Dalian Fisheries University, Dalian 116023, China
Received 3 August 2009; revised 3 December 2009; accepted 6 December 2009. Available online 31 December 2009.
Abstract: The effects of in vivo exposure of Mytilus galloprovincialis to two anionic surfactants (SDBS and SDS) on the molecular biomarker system were studied. After continuous exposure for 72 days, activities/levels of GST, GPx and GSH were significantly higher than in corresponding control groups following exposure to 3.000 mg/L SDS and SDBS. Activities of SOD and CAT were significantly inhibited by experimental SDBS (except CAT in 0.100 mg/L group), but not by SDS. Statistical analysis of enzyme activities/levels suggested that there were significant positive relationships between GST and GPx, and negative relationships were found between GSH and CAT, GSH and SOD. Amplified fragment length polymorphism (AFLP) results showed that a greater genotoxic effect was observed for SDBS than for SDS. Based on the above results, the biomarker system of mussels can be affected by the two anionic surfactants (≥3.000 mg/L); it was more easily affected by SDBS than by SDS.
Fragment of the text: With large discharges of anionic surfactants every year, the effects of anionic surfactants on
antioxidant enzymes of bivalve/fish have attracted more and more recent attention (Guilhermino
et al., 2000; Ostroumov, 2003; da Silva and Meirelles, 2004; Romanelli et al., 2004; Wu et
Keywords: Sodium dodecyl sulfate (SDS); Sodium dodecylbenzene sulfonate (SDBS); Mytilus galloprovincialis; Biomarker; Antioxidant enzymes; Genotoxicity; Metabolism
Article Outline:
1. Introduction
2. Materials and methods
2.1. Site description
2.2. Experimental organisms and chemicals
2.3. Experimental setup
2.3.1. Exposure experiment protocol
2.3.2. Biochemical indices analysis
2.3.2.1. Supernatant preparation
2.3.2.2. Measurement of the indices
2.3.2.3. Statistical analysis
2.3.3. DNA extraction and AFLP analysis
3. Results
3.1. Biochemical responses of mussels subjected to various treatments and pearson correlation coefficients between the indices detected in M. galloprovincialis
3.2. AFLP analysis
4. Discussion
4.1. Biochemical indices analysis
4.1.1. Phase II enzymes and cofactors
4.1.2. Oxidative stress parameters
4.1.3. Immunological parameters
4.2. Genotoxic parameter
5. Conclusion
Acknowledgements
References
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Fig. 1. Map of the Jiaozhou Bay with locations of sampling stations.
View Within Article
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Fig. 2. Examples of AFLP pattern obtained comparing DNA from control (2) and treated (1) SDS 3.0 or (3) SDBS 3.0, using E35-M62.
View Within Article
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Fig. 3. Dendrogram, computed with SM index, defining genetic differences due to DNA sequences, between SDS 3.0 (1), SDBS 3.0 (3) and control (2).
View Within Article
Table 1.
Sequences of primers used for AFLP analysis.
View table in article
View Within Article
Table 2.
Biochemical response (mean with standard deviation in parenthesis) of mussels subjected to various treatments and analysis. C, control; SDS, sodium dodecyl sulfate; SDBS, sodium dodecylbenzene sulfonate.
View table in article
GSH is reported as nmol/mg protein; GST is reported as nmol GSH consumed/mg protein/min; GPx is reported as μmol NADPH oxidized/mg protein/min; SOD is reported as U/mg protein/min; CAT is reported as ln(A1/A2)/(t2−t1)/mg protein; AKP is reported as mg phenol/mg protein/15 min; iNOS is reported as nmol NO/mg protein/min. *p<0.05, denotes statistically significantly different from the control group.
View Within Article
Table 3.
Pearson correlation coefficients between the indices detected in Mytilus galloprovincialis (effect of SDS-above diagonal; effect of SDBS-below diagonal).
View table in article
(**p<0.01, *p<0.05)
View Within Article
Corresponding author at: Key Laboratory of Marine Bio-resources Sustainable Utilization in Liaoning Province’s University, Dalian Fisheries University, Dalian 116023, China. ...
Effects of sodium dodecylbenzene sulfonate and sodium dodecyl sulfate on the Mytilus galloprovincialis biomarker system. Liu B., Z. Yu, X. Song, F. Yang - Ecotoxicology and Environmental Safety, 2009. doi:10.1016/j.ecoenv.2009.12.011 |
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5. |
Aquatic ecosystem as a bioreactor: water purification and some other functions
(публикация автора на scipeople)
Ostroumov S. A.
- Rivista di Biologia / Biology Forum , 2004
Ostroumov S. A. Aquatic ecosystem as a bioreactor: water purification and some other functions. - Rivista di Biologia / Biology Forum. 2004. vol. 97. p. 39-50.
Abstract (short). A fundamental concept is proposed of aquatic ecosystem as a...
Ostroumov S. A. Aquatic ecosystem as a bioreactor: water purification and some other functions. - Rivista di Biologia / Biology Forum. 2004. vol. 97. p. 39-50.
Abstract (short). A fundamental concept is proposed of aquatic ecosystem as a bioreactor that carries out the function of water purification in natural water bodies and streams. The ecosystem as a bioreactor has the following characteristic attributes: (1) it is a large-scale (large-volume) bioreactor; (2) it is a diversified (in terms of the number of taxa and the scope of functional activities) bioreactor; (3) it possesses a broad range of biocatalytic (chemical-transforming and degrading) capabilities. New experimental data on xenobiotics -induced inhibition of the water filtration performed by the molluscs Unio tumidus, U. pictorum, M. galloprovincialis and inhibition of feeding by Limnaea stagnalis emphasized the potential ecological hazard from sublethal concentrations of pollutants (including those exemplified by synthetic surfactants and detergents).
Keywords: environmental hazards, man-made impacts, anthropogenic effects, pollutants, xenobiotics, aquatic ecosystems, water purification, water filtration, bivalves, surfactants, detergents, biosphere, water quality;
SDS, sodium dodecylsulfate; TX100, Triton X-100;
TDTMA, tetradecyltrimethylammonium bromide;
ABSTRACT (EXTENDED, with fragments of the text of the paper):
Ostroumov S. A. Aquatic ecosystem as a bioreactor: water purification and some other functions. Rivista di Biologia / Biology Forum. 2004. vol. 97. p. 39-50.
1 Introduction
2 Methods
3 Role of the main groups of organisms in the biological processes of water purification
4 Aquatic ecosystem as a bioreactor with some features
5. Man-made effects and the effects of some xenobiotics
6. Aquatic ecosystems as part of the apparatus of the biosphere
7. Conclusions.
Abbreviations: SDS, sodium dodecylsulfate; TX100, Triton X-100;
TDTMA, tetradecyltrimethylammonium bromide;
1. INTRODUCTION
Priorities of ecological research include the further studies of ecosystem functioning (Ostroumov et al., [2003]) that include functioning towards water purification (the self-purification of water) in natural water bodies and streams.
The self-purification of water in natural ecosystems is a complex group of processes which includes physical, chemical, and biological components (Sushchenya, [1975]; Alimov [ 1981], [2000]; Skurlatov, [1988]; Uhlmann, [1988]; Izrael, and Tsyban, [1989]; Ostroumov [1998], [2001], [2002b]; Wetzel [2001]). Although biological aspects of water self-purification are generally attributed to heterotrophic microorganisms, the other groups of organisms are also known to play a significant role in this process (Sushchenya, [1975]; Konstantinov [1979], Alimov [ 1981], [2000], Wallace, and Starkweather, [1985]; Vymazal, [1988]; Walz, [1995]; Monakov[1998]; Wetzel [2001]; also, Vinberg, [1973]; Bul'on, Nikulina, [1976]; Ivanova,[1976]; Khlebovich, [1976]; - cit. in Ostroumov, [2001]).
The goal of this work was to analyze some data from the literature and our own experimental data on water self-purification under natural conditions and to formulate a fundamental concept of the aquatic ecosystem as an analog of a bioreactor (in a broad sense) that contributes to water self-purification mediated by main groups of aquatic organisms.
This paper is based on some previous publications of the author (Ostroumov [2000c], [2001], [2002a]).
2. METHODS.
The rate of water purification by macrozoobenthic filter feeders was measured experimentally as described earlier (Ostroumov [2001]). After the water sample had been kept with filter feeders for a certain time, the water filtration efficiency was monitored by the measuring the optical density of the suspension of unfiltered single - cell organisms that remained in the water column. The control samples of water were subjected to the same procedure of filtration, but without the contaminant (chemical) tested. Some other methods of the studies of the effects of contaminants on aquatic organisms are described in (Waterbury & Ostroumov [1994] , Ostroumov et al. [1997]).
3. ROLE OF THE MAIN GROUPS OF ORGANISMS IN THE BIOLOGICAL PROCESSES OF WATER PURIFICATION.
Self-purification of water includes the following biological processes: (1) biodegradation of contaminants; (2) accumulation and sequestration of toxicants in aquatic organisms and the resultant removal of the toxicants from the water column (e.g. Vymazal, [1988]); (3) generation and emission of oxygen required for oxidative degradation of contaminants; (4) uptake of biogenic substances (including N and P) and organic substances from the aquatic environment; (5) production of exometabolites; (6) water filtration (Sushchenya, [1975]; Alimov [1981]; Wallace, and Starkweather, [1985]; Monakov [1998]); and (7) formation of pellet and detritus particles (e.g., Wotton et al. [1998]); and their sedimentation to the bottom (for review, see e.g., Konstantinov,[ 1979]; Ostroumov [1986], [1998], [2001], [2002b]; Skurlatov, [ 1988]). This list is far from complete, and some other biological phenomena simultaneously contribute to several processes listed above. Analysis of the relative contributions of individual groups of aquatic organisms to water self-purification as an integral function of an ecosystem (Table 1) shows that the main groups of organisms simultaneously contribute to several processes of the system of water self-purification. None of the main groups of aquatic organisms can be regarded as being insignificant in terms of water purification. The role of each group of aquatic organisms in these processes can be summarized as an integral ecological rating, which is calculated as the sum of the number of pluses in the corresponding row of Table 1. It is seen from Table 1 that this rating is sufficiently high in all groups of organisms.
Thus, the whole range of biological diversity of aquatic organisms is an important factor in water self-purification (Sushchenya, [1975]; Alimov [1981, 2000], Wallace, and Starkweather, [1985]; Wotton et al. [1998]; Ostroumov [2001], Wetzel [2001]). The biota representatives of the water column, the entire ecosystem volume, the boundary regions of the ecosystem, and zones of contact between the ecosystem and its environment are involved in water purification. Activities of unicellular organisms (including those freely suspended in water, immobilized, and attached to various particles, surfaces, and substrates) (e.g., Inkina, [1988]) as well as of other aquatic organisms (e.g., Ostroumov [2001], Wetzel [2001]) suggest that an aquatic ecosystem may be regarded as a bioreactor (in a metaphorically broad sense; i.e., including biological, physical, and chemical aspects). However, unlike industrial bioreactors, such a broad-sense bioreactor has the following important features.
4. AQUATIC ECOSYSTEM AS A BIOREACTOR WITH SOME FEATURES.
The first feature is a fundamental difference in the bioreactor size. The volume of technological bioreactors does not exceed a few hundred cubic meters, whereas the volume of natural ecosystems is significantly larger. For example, the volumes of lake and estuary ecosystems reach thousands of cubic kilometers: Lake Baikal, 22995 km 3 ; Lake Superior, 12221 km 3 ; Lake Michigan, 4871 km 3 ; Lake Issyk-Kul, 1730 km 3 ; Lake Ladoga, 908 km 3 ; Lake Onega, 280 km 3 ; Lake Balkhash, 112 km 3 ; and Lake Sevan, 38 km 3 ; (1 km 3 = 10 9 m 3 ). This increases the biospheric role of ecological, biochemical, and biofiltration processes in these systems. Therefore, the physical size and volume of the system within which water self-purification take place should be taken into consideration. Thus, natural ecosystems can be regarded as large-size (large-scale) analogues of bioreactors.
The second feature is the differences (in terms of size and diversity) between the gene-pool of organisms inhabiting natural ecosystems and the genetic pool of organizms grown in technological bioreactors. This difference leads to a significantly larger diversity of functional activities of organisms in natural ecosystems. Technological bioreactors are usually inoculated with monocultures or, less frequently, mixed cultures with a small number of constituting species. In contrast to technological bioreactors, the biological diversity of natural ecosystems is substantially broader. According to some incomplete estimates, the number of species in natural ecosystems is as many as several hundred to several thousand (e.g., Konstantinov, [1979]). These estimates were obtained without regard to the number of strains of individual microbial species. If the prokaryote strains are taken into account, the quantitative estimates of the biological diversity of taxa in natural ecosystems may increase by several orders of magnitude.
Third, an aquatic ecosystem is characterized by a higher degree of autonomy (including energy autonomy) than technological bioreactors. This autonomy is based on the presence of autotrophic organisms. Thus we suggest that natural ecosystems should be regarded as multispecies and diversified (i.e., based on the diversity of organisms and their functions) analogs of bioreactors, implementing a broad spectrum of catalytic functions (including transformation and degradation of contaminants).
5. MAN-MADE EFFECTS AND THE EFFECTS OF SOME XENOBIOTICS.
Anthropogenic sublethal effects (including the inhibition of physiological activities) and behavioral changes in virtually any group or taxon of aquatic organisms may decrease the bioreactor efficiency. Some sublethal effects should be regarded as a potential hazard to the purification function (Ostroumov [1998], [2000a ], [2000b], [2002a]; Ostroumov et al. [1997], [1999 ] ). Because the main groups of macroorganisms and microorganisms play a substantial role in self-purification of ecosystems, it is very important to compare the sensitivities of the organisms to various contaminants. In some cases, macroorganisms are at least as sensitive (or even more sensitive) to contaminants as microorganisms (Table 2).
According to the presently adopted regulation of ecological monitoring and bioassaying, the ability of chemical compounds to damage the self-purification potential of ecosystems is being tested using heterotrophic bacteria alone. However, it follows from Table 2 that this approach may result in an underestimation of the effects of contaminants on more sensitive biological components of self-purified ecosystems (e.g., some macroorganisms).
We obtained new data on the ability of xenobiotics to inhibit water filtration by marine and freshwater organisms and on the hygienic function of pulmonary mollusks associated with elimination of organic matter (the removal of phytomass) from the water column in aquatic ecosystems (Table 3).
Some sublethal concentrations of contaminants may inhibit vital activities of other organisms involved in the functioning of the ecosystem as an analog of a bioreactor (e.g., Ostroumov [2001], [2002a], Ostroumov et al. [1999]).
6. AQUATIC ECOSYSTEMS AS PART OF THE APPARATUS OF THE BIOSPHERE.
V.I. Vernadsky considered the biota as the apparatus of the biosphere (Vernadsky, [2001]). To continue and develop his thought, we could consider aquatic ecosystems and aquatic biota as a key part of that apparatus. In that capacity, aquatic ecosystem carries a number of functions, not only the one function discussed above (water purification). Among those biospherically important functions are the following: (1) production of organic matter; (2) removing the excess organic matter; ( 3 ) mediating, catalyzing, and regulating biogeochemical flows and cycles; ( 4) harboring biodiversity and by doing so harboring the genetic pool of biodiversity; (5) providing links among various parts of the biosphere; ( 6) contributing to stability of the biosphere.
7. CONCLUSIONS. The fundamental concept put forward in this work emphasizes that both the biological diversity of aquatic organisms and their normal level of physiological activities are required to provide the effective functioning of an ecosystem as an analog of a bioreactor. That bioreactor carries a number of biospherically important functions and processes (we call them 'microbiospheric processes') including those of water purification (environmental remediation, ecological repair). This may lead to a deeper insight into the mechanisms of aquatic ecosystems and to better understanding of hazards of the anthropogenic impact on the biosphere (Yablokov, Ostroumov [1983], [1985], [1991]; Ostroumov [1986]; [Wetzel, 2001]).
REFERENCES
Alimov, A. F., [1981], Functional ecology of bivalves. - Nauka Press, Leningrad. 248 pp.
Alimov A.F. [2000], Elements of aquatic ecosystem function theory. Nauka Press, St.Peterburg.
Inkina, G.A. [1988]. Bacteria as a component of the suspended matter in water ecosystems. - Microbiology (Mikrobiologijja, in Russ.) 57: 140-145.
Izrael, Yu. A. and A. V. Tsyban, [1989]: Anthropogenic ecology of the ocean. - Gidrometizdat., Leningrad, 528 pp.
Konstantinov, A.S., [1979]. Obshchaya gidrobiologiya (General Hydrobiology), Vysshaya Shkola, Moscow.
Monakov, A.V.1998: Feeding of freshwater invertebrates.– Institute of Ecological and Evolutionary Problems of Russian Academy of Sciences, Moscow, 322 p.
Ostroumov, S.A., [1986], Vvedenie v biokhimicheskuyu ekologiyu (Introduction to Biochemical Ecology), Moscow University Press, Moscow. –176 p.
Ostroumov S.A. [1998], Biological filtering and ecological machinery for self-purification and bioremediation in aquatic ecosystems: towards a holistic view. Rivista di Biologia / Biology Forum. 91: 247-258.13.
Ostroumov, S.A., [2000a], Biological effects of surfactants in connection with the anthropogenic impact on the biosphere. MAX Press, Moscow. 116 p.
Ostroumov S. A. [2000b], Criteria of Ecological Hazards Due to Anthropogenic Effects on the Biota: Searching for a System. Doklady Biological Sciences, 371: 204–206. (Translated from the Russian edition: Ostroumov, S.A., [2000] Doklady Akademii Nauk, 371 ( 6): 844–846).
Ostroumov S.A. [2000 c] Aquatic ecosystem: a large-scale, diversified bioreactor with the function of water self-purification. Doklady Akademii Nauk, 374, (3) : 427–429.
Ostroumov, S.A., [ 2001], Biological effects of surfactants on organisms. MAX Press, Moscow. 334 p.
Ostroumov S.A. [2002a]. Inhibitory analysis of top-down control: new keys to studying eutrophication, algal blooms, and water self-purification. Hydrobiologia. 469: 117-129 p.
Ostroumov S.A. [2002b]. Polyfunctional role of biodiversity in processes leading to water purification: current conceptualizations and concluding remarks. Hydrobiologia. 469 (1-3): -203-204 p.
Ostroumov S. A. [2003]. Studying effects of some surfactants and detergents on filter-feeding bivalves. Hydrobiologia. 500: 341-344.
Ostroumov S.A., Dodson S., Hamilton D., Peterson S., and Wetzel R.G. [2003] Medium-term and long-term priorities in ecological studies. Rivista di Biologia / Biology Forum. 96: 327-332.
Ostroumov, S.A., Donkin, P., and Staff, F., [1997], Effects of surfactants on mussels Mytilus edulis. Vestnik Moskovskogo Universiteta. Serija Biologiya (Bulletin of Moscow University. Series Biology.) 3 : 30 - 36. (in Russian with English abstract).
Ostroumov, S.A., Kolotilova, N.N., Piskunkova, N.F., Kartasheva N.V., Lyamin M.Ya., and Kraevsky V.M. [1999] Effects of surfactants representing quaternary ammonium compounds on unicellular cyanobacteria, green algae, and rotifers. Vodnye ekosistemy i organizmy (Aquatic Ecosystems and Organisms), Dialog –Moscow University Press, Moscow, pp. 45–46.
Skurlatov, Yu. I., [1988]: Fundamentals of the management of quality of water. - Ekologicheskaja Khimija Vodnoi Sredy (Ecological Chemistry of Aquatic Environment). 1: 230-255.
Sushchenya, L. M., [1975]: Quantitative trends in the feeding of crustaceans. - Nauka I Tehnika Press, Minsk, 208 pp. (in Russ.)
Uhlmann, D. [1988]: Hydrobiologie. Ein Grundriß für Ingenieure und Naturwissenschaftler. - G. Fischer, Jena, 3. Ed., 298 pp.
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Yablokov, A.V. and Ostroumov, S.A., [1991]. Conservation of Living Nature and Resources: Problems, Trends and Prospects. Springer Press, Berlin.
LIST OF TABLES:
Table 1. Contribution of aquatic organisms to some processes important for water self-purification in ecosystem (some examples; a simplified model).
Table 2. Effect of Triton X-100 (TX) and tetradecyltrimethylammonium bromide (TDTMA) on biological organisms.
Table 3. Inhibition of some functions of molluscs important for water self-purification under exposure to sublethal concentrations of contaminants (new data). Note: SDS, sodium dodecylsulfate; TX100, Triton X-100; TDTMA, tetradecyltrimethylammonium bromide;
ADDENDUM (written in 2010):
After preparing this paper for publication, a number of other articles and some books were published, which supported the main conclusions of this paper. Among those more recent publications were the following:
Ostroumov S. A. Biological Effects of Surfactants. CRC Press. Taylor & Francis. Boca Raton, London, New York. 2006. 279 p. ISBN 0-8493-2526-9 [new facts and concepts on assessment of hazards from chemicals, new look on the factors important to water quality, to sustainability; new priorities in environmental safety]; and other publications.
Ostroumov S. A. Aquatic ecosystem as a bioreactor: water purification and some other functions. - Rivista di Biologia / Biology Forum. 2004. vol. 97. p. 39-50. |
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Inhibitory analysis of top-down control: new keys to studying eutrophication, algal blooms, and water self-purification
(публикация автора на scipeople)
 
Ostroumov S.A.
- Hydrobiologia , 2002
Ostroumov S.A. Inhibitory analysis of top-down control: new keys to studying eutrophication, algal blooms, and water self-purification. // Hydrobiologia. 2002 (Feb). v. 469, p. 117-129. DOI 10.1023/A:1015559123646....
Ostroumov S.A. Inhibitory analysis of top-down control: new keys to studying eutrophication, algal blooms, and water self-purification. // Hydrobiologia. 2002 (Feb). v. 469, p. 117-129. DOI 10.1023/A:1015559123646. http://www.moipros.ru/files/author_4_article_9.doc; www.springerlink.com/index/R9PTJEQ5FK8VLA6M.pdf;
Keywords: self-purification, filter-feeders, surfactants, detergents, benthic bivalves, aquatic ecosystems, eutrophication, algal blooms, hazards of chemical pollution, water quality, phytoplankton, marine and freshwater invertebrates, clearance rate, biological effects of xenobiotics, pollutants
ABSTRACT (A SHORT VERSION):
Top-down control is an important type of interspecies interactions in food webs. It is especially important for aquatic ecosystems. Phytoplankton grazers contribute to the top-down control of phytoplankton populations. The paper is focused on the role of benthic filter feeders in the control of plankton populations as a result of water filtering and the removal of cells of plankton from the water column. New data on the inhibitory effects of surfactants and detergents on benthic filter-feeders (Unio tumidus, U. pictorum, Mytilus galloprovincialis, M. edulis, and Crassostrea gigas) are presented and discussed. Importance and efficiency of that approach to the problems of eutrophication and water self-purification is pointed out. Chemical pollution may pose a threat to the natural top-down control of phytoplankton and water self-purification process. The latter is considered an important prerequisite for sustainable use of aquatic resources.
ABBREVIATIONS: CR - clearance rate; LAS - linear alkylbenzene sulphonate; NOEC - No observable effect consentration; QSAR – quantitative structure - activity relationship; SFG - Scope for Growth; SDS – sodium dodecyl sulphate; TDTMA - tetradecyltrimethylammonium bromide; TX100 - Triton X-100
ADDENDUM TO THE ABSTRACT (EXTENDED VERSION):
1. INTRODUCTION
By definition, the organisms of the two adjacent trophic levels interact with each other so that the organisms of the higher trophic level may produce some effect on the organisms of the lower trophic level. If the latter are not too abundant, the effects of the organisms of the higher level lead to limiting, decreasing or stabilizing the populations of the organisms of the lower trophic level. These effects might be considered a control or a partial control of the organisms of the lower trophic level. Many examples of interactions of that type were studied in various natural and experimental systems (Table 1). The significance of top-down control attributes additional importance to studies of the grazing activity of crustaceans (e.g., Sushchenya, 1975; Gutelmaher, 1986), rotifers (e.g., Monakov, 1998; Bul’on et al., 1999), protozoan plankton (e.g., Bul’on et al., 1999), and benthic invertebrates (e.g., Alimov, 1981; Donkin et al., 1989, 1991; Zaika, 1992; Ogilvie & Mitchell, 1995; Widdows et al., 1995a, Widdows et al., 1995b; Newell, 1999), and other invertebrates (Monakov, 1998).
In aquatic ecosystems, the problem of the control of the organisms of the lower trophic level (algae) is of outstanding importance because it is relevant to the problem of eutrophication. Also, control mechanisms are important in better understanding the problem of algal blooms, including the toxic algae blooms. To avoid over-simplification, we should realize that there are many factors that regulate the abundance of algal populations; top-down control is only one of them.
Many species of invertebrates of both plankton and benthos belong to the higher trophic level as compared with algae and cyanobacteria of phytoplankton. As for zooplankton species and their filter-feeding activity, an important body of information was presented and analyzed in (Sushchenya, 1975; Gutelmaher, 1986). Filtering activity of benthic species has also been studied (e.g., Alimov, 1981; Ostroumov et al., 1997, 1998).
In this paper we focus on some species of invertebrates of benthos, which are filter-feeders and in this capacity contribute to the top-down control of phytoplankton.
2. ROLE OF BENTHIC INVERTEBRATES IN FILTERING WATER AND RESULTING PHYTOPLANKTON GRAZING: FILTER-FEEDERS
The diversity of benthic organisms that filter water and remove algal cell and other particulate matter is broad. Filter-feeders inhabit the bottom of both freshwater and marine ecosystems. To facilitate broader general conclusions, in this paper we will consider both freshwater and marine organisms. The range of filter-feeders includes sponges, polychaetes, molluscs, echinoderms, larvae of many insects, ascidians, and some other invertebrates.
There are many examples of massive scale water filtering by benthos (e.g., Table 2; see also: Alimov, 1981; Ostroumov & Fedorov, 1999). It was shown that in some man-made reservoirs the total volume of water is filtered by benthic bivalves 2-24 times annually (e.g., Konstantinov, 1979). In a shallow lake in New Zealand the total volume is filtered during a time period of less than 2 days (Ogilvie & Mitchell, 1995). Equally massive filtering activity was discovered for the benthic sponges in the coastal waters of Lake Baikal which stores 22, 995 km3 of superb clean water (for comparison, the amount of the annual world consumption of freshwater was 3, 240 km3, and the annual freshwater withdrawal in Europe was 359 km3, in North and Central America 697 km3; the data for year 1987) (World Resources 1995-1995).
As a result of water filtering, algal cells are removed from the water column. It is important that some filter-feeders (e.g., bivalves) remove more algae than they need for feeding purposes. Excessive amounts of algae biomass and other particulate matter are excreted in the form of pellets (to distinguish them from regular faeces they are called pseudofaeces) which are larger in size than the algal cells and therefore they settle to the bottom rapidly. The amount of pseudofaeces may exceed the amount of the assimilated food manyfold. As a result, the total activity of bivalve molluscs in removing algal biomass from the water column and in making water clearer is far beyond just the trophic needs of bivalves.
The total weight of organic matter that is removed from a water column and deposited as bottom sediments is measured as high as kilograms per m2 per year. E.g., in the ecosystem of the man-made reservoir Volgogradskoe, the amount of the formerly suspended matter that was removed by molluscs from the water column and finally sedimented was 8.3 kg m-2 annually (Kondratiev, 1976; cited in Konstantinov, 1979). For the entire reservoir that is located in the center of the largest European river, the amount of sedimented matter was as high as 29 million tons.
3. INHIBITORY EFFECTS OF XENOBIOTICS AND POLLUTANTS: A DECREASE IN WATER FILTRATION AND ASSOCIATED PHYTOPLANKTON GRAZING
Man-made chemicals can produce strong inhibition of water filtering by benthic molluscs or impair the normal pattern of opening bivalves which is needed to maintain the efficient filtration of water. Some examples of those effects are given in Table 3. More examples could be found in literature (e.g., Stuijfzand, 1995; Ostroumov, 1998). The experiments were usually conducted using some phytoplankton species as the organism that is being removed from the water column during the filtration experiment. Thus, in experiments with bivalve Mytilus edulis, the algae Isochrysis galbana are often used (Donkin et al., 1997; Ostroumov et al., 1997; 1998). In our experiments with M. galloprovincialis (see below) we have observed a xenobiotic-induced decrease in grazing phytoplankton cells of Monochrysis lutheri and Dunaliella viridis. In our experiments with freshwater bivalves Unio tumidus and U. pictorum, we described some pollutant-induced inhibition of the removal of green algae Scenedesmus quadricauda and cyanobacteria Synechocystis.
The major part of our experiments were done in the laboratory. Under field conditions, it was described that in polluted habitats the biomass and vitality of bivalves declined (Zaika, 1992), which means that their contribution to water filtering is negatively affected. It was possible to develop an integrative parameter, Scope for Growth (SFG) which enables the scientist to estimate the total amount of energy available for the population of mussels for its growth and reproduction (after deduction of the amount of energy is lost during respiration etc.) (Widdows et al., 1995a, 1995b). It was shown that in terms of the entire populations, in polluted habitats the reduced filtration and reduced intake of energy from digested plankton (and seston as a whole) led to the fact that SFG was reduced.
4. MORE SPECIFIC EXAMPLES AND NEW DATA: INHIBITORY EFFECTS OF SURFACTANTS
We have initiated a systematic study of the effects of another class of aquatic pollutants, namely surfactants, on the water-filtering activity of bivalves and on the resulting removal of algal cells from the water column.
Among the various organic chemicals that are entering the natural environment in large amounts (Yablokov & Ostroumov, 1983, 1985, 1991), surfactants play a significant role (Ostroumov, 1986; 1990; 1991; 1994 a; 1994b; Marcomini et al., 1988; Quiroga et al., 1989; Granmo et al, 1991; Fernandez et al., 199; Lewis, 1991; Takada & Ishiwatari, 1991; Chalaux et al., 1992; Terzic & Ahel, 1993). It was shown that surfactants produce negative and sometimes also stimulatory effects on cyanobacteria (Waterbury & Ostroumov, 1994), green algae (e.g., Goryunova & Ostroumov, 1986), diatoms (Ostroumov & Maertz-Wente, 1991), plant seedlings (Ostroumov, 1986; 1990; 1991; Nagel et al., 1987; Maximov et al., 1988; Telitchenko & Ostroumov, 1990), shrimp (Drewa et al., 1988), Daphnia magna and D. pulex (e.g., Maki & Bishop, 1979; Martinez et al., 1989), freshwater amphipods (Pantani et al., 1995), rotifers (Kartasheva & Ostroumov, 1998), fish (e.g., Versteeg & Shorter, 1992; Malcolm et al., 1995). Some data on the effects of linear alkylbenzene sulphonate (LAS) on Mytilus galloprovincialis Lmk (Bressan et al., 1989; Marin et al., 1993), Mytilus edulis (Granmo, 1972) and some other marine benthic species (Marin et al., 1991) are available. However, almost nothing was known about the effects of alkylsulfates, nonionic surfactants (derivatives of nonylphenols), and some other surfactants as well as detergents on the filtering activity of Mytilus edulis, M. galloprovincialis, Crassostrea gigas, Unio tumidus, and U. pictorum.
The purpose of the experimental part of this work was to obtain data on the effects of some surfactants and surfactant-containing products including detergents, on the ability of bivalves (M. edulis, M. galloprovincialis, Unio tumidus, and U. pictorum) to filter water and remove algal or other cells from it.
Freshwater mussels Unio sp. were collected in the Moscow River. Mytilus galloprovincialis were collected at the Black Sea. Crassostrea gigas were grown at a mariculture farm (the Black Sea, Institute of Biology of Southern Seas NANU). M. edulis were collected at the Exmouth estuary and kept in tanks with aeration , water flow and periodic automatic imitation of low tide (water was removed out of tanks for 3 h every day) (Dr. Donkin’s participation and help in the work with M. edulis is acknowledged).
The temperature in experiments with M. galloprovincialis and C. gigas was mostly 22-27 C, in the experiments with Unio sp. 18-20 C. The cell removal and the cell density during the filtration by molluscs was measured using Hitachi 200-20 spectrophotometer (experiments with Unio sp.) and SF-26 (LOMO) spectrophotometer (experiments with M. galloprovincialis and C. gigas). In experiments with M. edulis (temperature 16 C), the number of cells per unit of volume was measured using the Coulter counter ( Coulter Electronics, model Industrial D). When a sample of filtered water without adding algae was used, the Coulter count was usually below 200.
The clearance rate (CR) was calculated according to Widdows & Salkeld (1993) using the following equation:
CR (l h-1) = (Volume of water e.g. 2 l) x (loge C1 -- logeC2)/time interval in h
where C1 and C2 are cell concentrations at the beginning and end of each time increment (e.g. 0.5 h).
Statistical analysis was performed using EXCEL software. For linear regression analysis, an option was used which gives an opportunity to fix the intercept at a predetermined value.
Several chemicals were used. Sodium dodecyl sulfate (SDS) (molecular mass 288.38) was purchased from Fluka. The purity was > 99% (assayed by GC, analysis number 332533/1 395). Triton X-100 (TX100) (x = 9-10 ethoxy units, H2O < 1 %, residue on ignition, 0.2%, analysis number 43306/1 795) was purchased also from Fluka. Tetradecyltrimethylammonium bromide (TDTMA, molecular mass 336.4) was purchased from Sigma (St.Louis, Missouri, 63178 USA; lot 55H1322). Detergents used were available commercially.
Results of the experimentation were as following.
Freshwater bivalves, Unio tumidus and U. pictorum removed planktonic cells from water. The ability to do so was inhibited by surfactants of several types (Table 4), including TDTMA, and TX100 .
A marine species, M. galloprovincialis, was also efficient in removing from water cells of phytoplankton and unicellular organisms in general. Several surfactants as well as detergents which contain surfactants inhibited this ability of M. galloprovincialis (Table 4). The chemicals tested included surfactants TDTMA, SDS, and several detergents, such as Tide-Lemon, Lotos-Extra, Losk-Universal.
In experiments with M. edulis, after one hour of filtering, in the control set (clean water) the number of algal cells per unit of volume decreased to almost 5.6% of the initial level, which is a good example of how efficiently bivalves can control planktonic populations (Table 5). This is in accord with the large amount of data on the significant filtration rates of bivalves (Alimov, 1981; Monakov, 1998) and their impact on ecosystems (Zaika, 1992). In the important series of measurements, in the control beakers (filtration of unpolluted water) the number of algal cells decreased by a factor of 15.98, while in the beakers with SDS (1 mg l–1) the number of cells decreased by a factor of 7.93. Thus, the algal cell density in control was half that in the system at the initial concentration of 1 mg l–1. The difference increased by the end of the experiment.
When the initial concentration of SDS was 2 mg l–1, a substantial difference from the control set was observed after the first half-hour period (Table 6). After 65 min of filtering, the algal cell density in the control set was almost 1/3 that contained in the system with SDS.
Further increase of the initial concentration of SDS up to 4 mg l–1 caused a dramatic 3-times increase of the cell density over that in the control set after only 35 min of filtering. In 65-min of filtering, the difference was 6-fold, and following 95-min filtering - over 14-fold.
At the initial concentration of SDS 5 mg l–1, the difference between systems with and without SDS was over 16-fold after 125 min of filtering.
It was possible to calculate the clearance rate (CR), using a standard formula widely accepted in the literature ( Donkin et al. 1989; 1991; Widdows & Salkeld, 1993).
The summary of the inhibitory effects shows, with a few exceptions, two general trends:
1) an increase in the initial concentration of SDS in the range of 0.5 to 5 mg l–1 gave rise to an the increase in the inhibitory effect on CR (Table 7);
2) at any given concentration of SDS, the highest effect took place during the first 30-min period, with some decrease in the inhibitory effect by the end of the experiment.
The latter trend, however, was not paralleled by a mitigation of the effect on the residual algal cell density in the water. When the cell density was considered, the difference from the control was maximal by the end of the experiment.
Using another chemical, a non-ionic surfactant Triton X-100, we obtained similar data with EC50 close to that of SDS (Table 8). At a concentration of 4 mg l–1, the inhibition of the clearance rate during the time period of 30 min after the beginning of the experiment was almost 10-fold, and during the later period of time, the inhibition was about 5-fold.
The data obtained in our study showed that the filtering activity of mussels demonstrated a more sensitive response than some other biotests we had used in our experiments in bioassaying SDS, including green algae (Goryunova & Ostroumov, 1986) and plant seedlings (Nagel et al., 1987). The filtering activity of mussels was also more sensitive to SDS than some of the traditional lethal biotests with aquatic invertebrates and fish which had been applied for studies of LAS and alkyl sulfates (Sivak et al., 1982; Ostroumov, 1991).
It is noteworthy that the inhibitory effect of SDS on CR was developed within a rather narrow range of SDS concentrations (1 to 5 mg l–1). That could be in accord with a hypothesis that the decrease in CR is at least in part the result of a behavioural response of mussels.
Our data on effects of SDS are in good agreement with the results obtained by other authors who studied effects of another anionic surfactant, linear alkylbenzene sulphonate (LAS) on filtering rate. It was shown that in experiments with exposure for 48 h and 96 h the filtration rate of mussels Mytilus galloprovincialis was reduced when concentration of dissolved LAS was higher than 1.5 mg l–1 (Bressan et al., 1989). In our experiments the biotest was slightly more sensitive as we exposed the animals to the surfactant for 1.5 h prior to beginning measurements and observed some inhibition at the initial concentration of 1 mg l–1.
Bressan et al. (1989) studied also effects of LAS on the growth of mussels and on mortality and spermatozoids of freshwater bivalve molluscs. They observed some decrease in the increment of length of the major axis of the shell of mussels at concentrations of LAS as low as 0.25 and 0.5 mg l–1, but the effect required up to 70 days to be observed. No significant effects were found within 30 days of their experiments. The length of time that was necessary to reveal the effect was a limitation of the technique, however it was impressive to observe almost a 2-fold decrease in growth when the chronic experiment with a relatively low level of LAS (0.25 mg l–1 ) lasted for 160 days and more.
In a parallel experiment the same authors observed a 30% increase in the respiration of LAS-treated (220 days, 0.25 mg l–1 ) young mussels (Bressan et al., 1989). Unfortunately, they did not specify what they called young mussels.
Some decrease in filtering rate was observed in another set of experiments when the concentration of LAS was 0.25 mg l–1 , but the duration of the surfactant treatment was much longer (220 days) than in our experiment, and the size of mussels was again not specified (Bressan et al., 1989). Also, they have shown that, at a concentration of 1 mg l–1, LAS inhibited the filtration rate after 7 days of exposure. It seems important that in our experiments we observed effects after only 1.5 hours of exposure to the anionic surfactant.
The LC50 (48 h) was about 40 mg l–1 and LC50 (96 h) was about 1.7 mg l–1 (Bressan et al., 1989), which was much lower than in the case of freshwater bivalves Anodonta cygnea and Unio elongatulus. For the latter two species, LC50 (96 h) was about 200 mg l–1 (Bressan et al, 1989). The mobility of spermatozoa of A. cygnea was almost completely inhibited at a concentration of LAS equal to 20 mg l–1.
Measurements of CR were used to quantify the toxic effects of chemicals and to study QSAR (Donkin & Widdows, 1990) for various chemicals, including alkanes and phenyl alkanes (Donkin et al., 1991) as well as such aromatics as toluene, naphthalene, n-propylbenzene, 1-chloronaphthalene, biphenyl etc. (Donkin et al., 1989). Two xenobiotics, including an organotin compound, inhibited the fitration rate by Dressena polymorpha and Crenomytilus grayanus (Mitin, 1984).
The filtering activity of not only bivalves, but also of other filter-feeders is vulnerable to the inhibition by surfactants. In experiments with rotifers Brachionus angularis Gosse, we have shown that TDTMA inhibited their filtration rate and the removal of cells of Chlorella sp. from the water (Kartasheva & Ostroumov, 1998). At a TDTMA concentration of 0.5 mg l–1, the average efficiency of filtration was 58.5% of that in control.
However important these kinds of studies of CR are, it is also important to consider the general consequences of a decrease in the CR for the ecosystem.
The role of the filtering activity of mussels is connected with their high population densities. It was estimated that at Narragansett Bay, Rhode Island, mussels represented about 77% (11 kg m -2) of the total community dry weight (Nixon et al., 1971), and numbers of the same order of magnitude were reported for other locations (Seed & Suchanek, 1992). Taking into account that, in our experiments, one mussel with a total wet weight about 8.5 g filtered over 1 L of water per hour, it is easy to estimate that, at high abundancy, a mussel community may filter over 100 L water per hour per 1 m2 of the sea bottom.
A comparison of the tables for residual cell densities and CR for specific concentrations of surfactants shows that even a small decrease in CR produces a large difference in the residual cell density. The latter parameter may be considered as a model for any kind of particles which are being removed from the seawater by mussel filtering. In this way we may predict a huge decline in the natural ability of benthic communities to purify natural water when the water is polluted by surfactants as well as by other chemicals reducing the CR.
Changes (inhibition) of the filtering activity of bivalves might have many consequences in changing many parameters and processes in ecosystems, which were considered in more detail in (Ostroumov et al., 1997; 1998; Ostroumov, 1998).
Those considerations show that the inhibition of CR has consequences not limited by the prosperity of the mussel population, but that it is important for the state of the marine and estuarine ecosystems in much broader terms. Prospects of chemical-induced inhibition of water filtration by bivalves poses some ecological hazards in view of the role of bivalves in eutrophication control. The latter was studied in the case of the ecosystem of Chesapeake Bay (the Atlantic coast of the U.S.A.) (Newell et al., 1999).
5. SENSITIVITY OF PLANKTON GRAZERS TO XENOBIOTICS - ANALOGOUS EVIDENCE FOR ZOOPLANKTON
Analysis of the specific LC50 for Cladocera and various species of algae shows that in case of many pollutants Cladocera are more sensitive than algae. According to the data disseminated at the recent workshop in Netherlands (9-12 December 1999, Den Helder, TNO; participants of the research project: M. Scholten, R. Jak, B. Clement, E. Foekema, P.Hernandez, K.Kaag, H. van Dokkum, M. Smit), in the case of the following pesticides, species of Cladocera (mainly Daphnia magna, D. pulex, Ceriodaphnia dubia) are more sensitive: anilazin, benomyl, bentazon, cyfluthrin, dimethoat, lindan, maneb, zineb, and ziram. In case of several pesticides, it was directly shown that the inhibitory effects on feeding were observed at lower concentrations, than the concentrations which induced mortality. EC50 (effects on feeding within 4-24 h) were lower than LC50 (24-48 h) for endosulfan, diazinon, methyl parathion, lindan, and dichlobenil (according to the data distributed at the same workshop). In case of atrazine, a concentration of 1.6 mg l–1 within 10 min produced 50% reduction in feeding, which shows again that feeding activity is inhibited at concentrations lower than those inducing mortality: LC50 (48 h) was 9.88 mg l–1.
Also, NOEC (No observable effect concentration) was the basis for comparing sensitivities of Cladocera and various species of algae to pesticides. In case of the following chemicals a higher sensitivity of Cladocera was found: azinfos-methyl, cyromazin, diazinon, dimethoat, endosulfan, fenpropathrin, malathion, mecoprop, propoxur, trifluralin, and some other pesticides.
All these data as well as the new evidence in the experiments conducted at TNO during the project led by Dr. M. Scholten (see Table 1) are in accord with the concept that pollutants may impair top-down control of algae. This conclusion is analogous to the conclusion made by us on the basis of our data for benthic filter-feeders.
6. SYNOPTIC OVERVIEW AND GENERAL CONCLUSIONS
Some benthic organisms, including spongi, polychets, bivalves, echinoderms, larvae of insects, ascidia and some others proved to be efficient organisms in filtering water and thereby in reducing the amount of particulate matter suspended in the water. Benthic filter-feeders remove from the surrounding water various suspended particles including algal cells. By doing so, they contribute to natural mechanisms that keep algal populations under some control. That type of top-down control under some circumstances might become especially important. The problem of algal blooms in the context of eutrophication is increasing attention to all mechanisms of control of algal populations including the control by virtue of water filtering by benthic filter-feeders, including bivalves. Some pollutants were shown to be efficient inhibitors that decrease water filtering and resulting grazing phytoplankton. Those chemicals produced a decrease in removal of algae from water column by bivalves.
The author initiated systematic studies of effects of surfactants and detergents on filtering activity and removal of algae by freshwater and marine bivalves. Marine and freeshwater bivalves Mytilus edulis, M. galloprovincialis, and Unio sp. are efficient in removing unicellular organisms from water in result of their filtration activity. They are capable of drastically reducing the amount of cells of phytoplankton in water. This is an important mechanism contributing to natural control of algal populations in ecosystems. This regulatory mechanism is vulnerable to aquatic pollutants as exemplified by surfactants and detergents. New data are obtained and presented in this paper on how surfactants (anionic, non-ionic, and cationic ones) and surfactant-containing detergents inhibit the ability of marine and freshwater bivalves to remove cells of algae and cyanobacteria from water. On the basis of our new data, the final conclusion is that the new evidence support the views proposed in (Ostroumov, 1998; 1999; 2000c; 2000e) about the vulnerability of the filtration activity of invertebrates (both planktonic and benthic animals) to some pollutants, including surfactants. Our data and general conclusion are in accord with the idea that pollutants can induce reduction in grazing efficiency of benthic and planktonic invertebrates.
We consider the studies of inhibitory effects of chemicals on fiter-feeders as an effective approach to elucidating the details of filter-feeding and associated removal of phytoplankton from the water column. The mechanisms and rates of plankton removal are of utmost importance for controlling levels of plankton which are the key parameters in processes of eutrophication and algal blooms.
Water filtering activity of invertebrates is part of water self-purification in ecosystems. The self-purification of water is one of preconditions for the sustainable use of water resources. Therefore, the vulnerability of filter-feeders to aquatic pollutants (including surfactants and detergents) leads to a potential threat to the sustainable use of aquatic resources in situations when the ability of ecosystems to purify water is inhibited by pollutants.
In sum, on the basis of the data presented here and in some of our publications (Ostroumov, 1998; 1999; 2000a; Ostroumov et al., 1997, 1998; Ostroumov & Fedorov, 1999), the following inferences are to be made:
1. Surfactants inhibit the filtering ability of marine and freshwater bivalves with a drastic effect on the amount of particulate material (modelled here by algal cells) left in the water.
2. When considering the environmental importance of surfactants and detergents (and of a broader range of xenobiotics and pollutants as well), the ramifications relevant to disturbance of the natural ability of the ecosystem to control phytoplankton populations should be taken into account.
3. Our new data are in accordance with the opinion (Ostroumov, 1990; 1991; 2000b; 2000c; 2000d; Telitchenko & Ostroumov, 1990; Yablokov & Ostroumov, 1991) that surfactants, if being discharged into the environment at substancial rates, might, under some circumstances and in some ecosystems, become more significant as environmental pollutants than it was thought before.
4. We make the prediction that many new examples are to be found of pollutants (both organic and inorganic) which inhibit filtration rate of filter-feeders (not only bivalves, but also other benthic and plankton organisms) and by doing so reduce the ability of invertebrates to control unicellular plankton populations. We predict that new examples are to be found of pollutants which inhibit the ability of invertebrates to control eutrophication.
5. Sustainable use of resources of aquatic ecosystems requires as an important pre-condition the efficient functioning of the ecosystems towards self-regulating and water self-purification. This pre-requisite includes normal functioning of top-down control excercised by the organisms at the higher levels of the trophic chains of ecosystems.
6. Studies of inhibitory effects of chemicals on the top-level organisms (e.g., grazers of plankton, including benthic filter-feeders) are a useful approach in obtaining information on the top-down control in trophic chains.
LIST OF TABLES:
Table 1. Top-down control in various natural and experimental systems (examples).
Table 2. Water-filtering activity of benthic organisms in some ecosystems (examples).
Table 3. Xenobiotics and contaminants that were shown to inhibit water-filtering activity of bivalves.
Table 4. New data on the inhibitory effect of surfactants and products that contain surfactants on the filtration efficiency of bivalve molluscs.
Table 5. Decrease in Isochrysis galbana cell density (per 0.5 ml) during filtering by Mytilus edulis in clean water (control beakers, A) and at 1 mg l–1 SDS (experimental beakers, B).
Table 6. Effect of SDS (2 mg l–1) on the efficiency of water filtering measured as the number of cells of Isochrysis galbana (per 0.5 mL) in the water after the 30-min period of filtering by Mytilus edulis.
Table 7. Inhibition (%) of the clearance rate (CR) of Isochrysis galbana during filtering by Mytilus edulis at various concentrations of SDS (after Ostroumov et al., 1998, with some changes).
Table 8. Effect of Triton X-100 on the clearance rate during filtering algae Isochrysis galbana by mussels Mytilus edulis (after Ostroumov et al., 1998, with some changes).
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The paper was cited and suported (examples):
The paper [Inhibitory analysis of top-down control: new keys to studying eutrophication, algal …S.A. Ostroumov - Hydrobiologia, 2002] was cited by:
Water Quality of Effluent-dominated Ecosystems: Ecotoxicological, Hydrological, and Management Considerations. - Hydrobiologia
[Springer Netherlands];
ISSN 0018-8158 (Print) 1573-5117 (Online);
Volume 556, Number 1, 2006 (February).
DOI 10.1007/s10750-004-0189-7;
p. 365-379;
Bryan W. Brooks 1 , Timothy M. Riley 2 and Ritchie D. Taylor 3
(1) Department of Environmental Studies, Center for Reservoir and Aquatic Systems Research, Baylor University, One Bear Place # 97266, Waco, Texas 76798, USA;
(2) Barton Springs / Edwards Aquifer Conservation District, 1124 Regal Row, Austin, Texas 78748, USA;
(3) Department of Public Health, Centre for Water Resource Studies, Western Kentucky University, 1 Big Red Way, EST 437, Bowling Green, Kentucky 42101, USA;
- - - --------------------
Medit. Mar. Sci., 8/2, 2007, 19-32;
Mediterranean Marine Science;
Volume 8/2, 2007, 19-32;
Identification of the self-purification stretches of the Pinios River, Central Greece
Y. CHATZINIKOLAOU 1, 2 and M. LAZARIDOU 1
1Department of Zoology, School of Biology, Faculty of Sciences,
Aristotle University of Thessaloniki, Greece;
2Institute of Inland Waters, Hellenic Centre for Marine Research,
46.7 km Athinon - Souniou Av., 190 13, P.O. Box 712, Anavissos, Hellas;
- - - - -
Impact of Dam Construction on Water Quality and Water Self-Purification Capacity of the Lancang River, China. - Water Resources Management
[Springer Netherlands],
ISSN 0920-4741 (Print) 1573-1650 (Online),
Volume 23, Number 9, 2009 (July).
DOI 10.1007/s11269-008-9351-8;
pp. 1763-1780;
GuoLiang Wei 1, 2, ZhiFeng Yang 1, BaoShan Cui 1 Contact Information, Bing Li 2, He Chen 1, JunHong Bai 1 and ShiKui Dong 1
(1) State Key Laboratory of Water Environment Simulation, School of Environment, Beijing Normal University, Beijing, 100875, P. R. China
(2) Nuclear and Radiation Safety Centre, State Environmental Protection Administration, Beijing, 100088, P. R. China
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Assessment of ecosystem health of tropical shallow waterbodies in eastern India using turbulence model
Authors: N. R. Samal a; A. Mazumdar b; K. D. Joumlhnk c;nF. Peeters d
Affiliations: a Dept. of Civil Engineering, National Institute of Technology Durgapur, Durgapur, West Bengal, India;
b School of Water Resources Engineering, Jadavpur University, Kolkata, West Bengal, India;
c Leibniz-Institute of Freshwater Ecology and Inland Fisheries, Neuglobsow, Germany
d Limnologisches Institut, University of Konstanz, Konstanz, Germany;
DOI: 10.1080/14634980902908589;
Published in: journal Aquatic Ecosystem Health & Management, Volume 12, Issue 2, April 2009, pages 215 – 225
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Lake and Reservoir Management
Bhatti, Zafar
Water Environment Research [Water Environ. Res.]. Vol. 76, no. 6, pp. 2106-2154. Oct 2004.
- - -------------------------------------
the examples were added on April 11, 2010.
Hydrobiologia. 2002. v. 469, p. 117-129. DOI 10.1023/A:1015559123646. |
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7. |
Anthropogenic effects on the biota: towards a new system of principles and criteria for analysis of ecological hazards
(публикация автора на scipeople)
Ostroumov S. A.
- Rivista di Biologia / Biology Forum , 2010
Ostroumov S. A. Anthropogenic effects on the biota: towards a new system of principles and criteria for analysis of ecological hazards. Rivista di Biologia / Biology Forum. 2003. 96: 159-170. [ISSN 0035-6050]...
Ostroumov S. A. Anthropogenic effects on the biota: towards a new system of principles and criteria for analysis of ecological hazards. Rivista di Biologia / Biology Forum. 2003. 96: 159-170. [ISSN 0035-6050]
http://scipeople.ru/publication/67657/;
http://sites.google.com/site/ostroumovsergei/publications-1/rivista2003criteria; http://scipeople.com/uploads/materials/4389/3RB96p159Anth..Criteria.doc; www.ncbi.nlm.nih.gov/pubmed/12852181;
http://www.tilgher.it/(ekdo002s40etdh55stgyltvf)/index.aspx?lang=eng&tpr=4&act=abs&id=650;
The currently accepted system of criteria for evaluating environmental and ecological hazards of man-made chemicals (pollutants) is vulnerable to criticism. In this paper, a new concept of the system of approaches towards criteria for evaluating the ecological hazard from man-made impact is proposed. It is suggested to assess the man-made impacts (including effects of pollutants and xenobiotics) on the biota according to the following four levels of disturbance in biological and ecological systems: (1) the level of individual responses; (2) the level of aggregated responses of groups of organisms; (3) the level of stability and integrity of the ecosystem; (4) the level of contributions of the ecosystem to biospheric processes. On the basis of the author's experimental studies, an example is given of how to apply the proposed approach and the system of criteria to the analysis of concrete experimental data. To exemplify the efficiency of the proposed approach, it is shown how to use it to analyze new data on effects of a synthetic surfactant on water filtering by bivalves. It is concluded that the proposed approach will be helpful in better assessing environmental and ecological hazards from anthropogenic effects on biota, including effects of man-made chemicals polluting ecosystems. The following key issues were presented and analyzed in the paper: 1. The traditional approach to classification of chemicals according to their environmental hazards. 2. A new approach to the analysis of hazards of anthropogenic effects on the biota. 3. An example of applying the new approach to the analysis of environmental and ecological hazards.
The paper was cited by international experts, e.g., in the paper: R. Grande ; S. Di Pietro; E. Di Campli; S. Di Bartolomeo; B. Filareto; L. Cellini. Bio-toxicological assays to test water and sediment quality. Journal of Environmental Science and Health, Part A, Volume 42, Issue 1 2007 (January), pages 33 – 38 [Affiliation of the Authors: Rossella Grande a; Stefania Di Pietro ab; Emanuela Di Campli a; Soraya Di Bartolomeo a; Barbara Filareto b; Luigina Cellini a;
a Department of Biomedical Sciences, University “G. d'Annunzio,”, Chieti, Italy;
b Agency for the Protection of Environment, Pescara, Italy] DOI: 10.1080/10934520601015446; http://www.informaworld.com/smpp/content~content=a768424372&db=all;
Keywords: environmental hazards, chemical pollution, man-made effects, anthropogenic impact, self-purification of water, filter-feeders, surfactants, detergents, bivalves, aquatic ecosystems, algae, water quality, water filtration, biological effects of xenobiotics, pollutants, bioaccumulation, toxicity, ecosystem stability, biota, criteria, biospheric processes, marine mussels, Mytilus edulis, bioassay, environmental science, ecotoxicology,
1. INTRODUCTION
One of the important tasks in preventing and mitigating changes in the biosphere is to perform an objective analysis of the hazards of a great many man-made impacts and disturbances on the state of the biota (the world-wide diversity of ecosystems, populations, and organisms). The multitude, diversity, and scale of anthropogenic effects has been described and analyzed in a number of publications (e.g., Yablokov & Ostroumov [1983], [1985], [1991]; Bezel’ et al [1994]; Krivolutskii [1994]). This paper is based on such papers as well as on our previous publications (Ostroumov [2000a], [2000b ], [2001]).
Studying the multiplicity of characteristics of anthropogenic factors affecting organisms and ecosystems (Flerov [1989]; Yablokov & Ostroumov [1991]; Bezel’ et al [1994]; Alimov [2000]; Wetzel [2001]), researchers try to identify and analyze the most important parameters and criteria characterizing negative anthropogenic effects (Yablokov & Ostroumov [1991]; Krivolutskii [1994]), including the effects of chemicals (xenobiotics; pollutants) (Ostroumov [1986]; Filenko [1988]; Telitchenko & Ostroumov [1990]; Malakhov & Medvedeva, [1991]). Currently the development and systematization of these criteria are far from completion.
The aim of this paper is to contribute to developing approaches to improvement of a system of criteria of ecological hazards of anthropogenic effects on the biota and to consider some new experimental data on the effects of surfactant xenobiotics on living organisms.
2. THE TRADITIONAL APPROACH TO CLASSIFICATION OF CHEMICALS ACCORDING TO THEIR ENVIRONMENTAL HAZARDS
Approaches to establishing the criteria of ecological hazards of man-made chemicals have been developed in terms of the estimation of toxic contamination of ecosystems and assessment of effects of xenobiotics on organisms (e.g., Flerov [1989]; Yablokov & Ostroumov [1991]; Filenko [1988]; Telitchenko & Ostroumov [1990]; Malakhov & Medvedeva [1991]. The classification of chemicals according to their environmental and ecological hazards now accepted in the European Union is based on the following three criteria (e.g., de Bruijin & Struijs, [1997]).
(1) Acute toxicity estimated from LC50 for the three groups of organisms: fish, algae, and daphnia.
(2) Susceptibility of the substance to biological decomposition in water. This is determined with the use of laboratory tests under aerobic conditions. Substances are decomposed by microorganisms, and their decomposition is accompanied by oxygen consumption. If a substance is quickly decomposed (oxidized) by microorganisms, it is not considered to be hazardous to the environment. Exceptions are compounds with a high acute toxicity (with an LC50 less than 10 mg/l) and a high bioaccumulation potential (see the next criterion).
(3) The substance’s capacity for bioaccumulation. This capacity is considered to be hazardously high if the bioaccumulation factor (BCF) is higher than 100, or the logarithm of the distribution coefficient of the substance in the octanol–water system (logPow) is higher than 3.
A disadvantage of this set of criteria is an underestimation of other aspects of ecological hazards due to contamination of a water body with the given chemical, e.g., the hazard of a decrease in water O2 concentration due to oxygen consumption by microorganisms during oxidation of xenobiotics. Behavioral changes in living organisms because of interaction of the pollutant with their receptors (Flerov [1989]; Ostroumov [1991]) is also beyond the scope of this system of criteria. Behavioral changes may occur in the absence of bioaccumulation (i.e., when the substance is not hazardous according to criterion 3). Changes in behavior may result in migration of certain species from the ecosystem (emigration) and, hence, to a decrease in biodiversity.
Therefore, more comprehensive sets of criteria should be developed.
3. A NEW APPROACH TO THE ANALYSIS OF HAZARDS OF ANTHROPOGENIC EFFECTS ON THE BIOTA
In some studies, anthropogenic effects on the natural environment were classified on the basis of the approach of considering the levels of biological organization (Yablokov & Ostroumov [1983]; Yablokov & Ostroumov [1985]; Yablokov & Ostroumov [1991]) . We suggest a new approach to developing a set of principles for the analysis of man-made effects (Table 1), in which anthropogenic effects on the biota are systematized based on the basis of a similar, but not identical approach (Ostroumov [2000a], [2000b], [2001]).
A characteristic feature of the system of principles and criteria shown in Table 1 is the division of the multiplicity of anthropogenic effects into orderly groups according to four levels of biota disturbance. Most of the traditionally studied toxic effects (an increased mortality, ontogenetic disturbances, organ pathology, etc.) fall in the group corresponding to the level of individual and population responses (level 1). Alterations in primary productivity, water concentration of chlorophyll, etc., correspond to the level of aggregated responses (level 2). Alterations at the level of ecosystem stability and integrity (level 3) are important but have not been sufficiently studied. These are, among others, disturbances in the self-purification capacity of water systems (Ostroumov et al. [1997]; Ostroumov, [1998]), i.e., their ability to sustain the parameters of the aquatic environment. The last group (level 4) comprises alterations in the contribution of ecosystems to biospheric processes, including biogeochemical flows of chemical elements (C, N, P, and S).
This approach agrees with the views of some other authors (Filenko [1988]; Stroganov [1976]) and is useful for developing a new, more adequate system of estimation and classification of anthropogenic effects, including environmental pollutants, with respect to ecological hazards.
An important constituent of the proposed system for analysis of ecological hazards is estimation of hazardous effects on the stability and integrity of an ecosystem, e.g., the hazard due to weakening the relationship between plankton and benthos. If an anthropogenic effect weakens this relationship in a given ecosystem, the consequences are expected to be unfavorable [13] (Ostroumov et al. [1997]). An example of such a situation is the decrease in the water filtration rate and elimination of seston by some filter-feeding organisms, such as bivalves, because their filtration activity is one of the important mechanisms for maintaining the plankton–benthos coupling. It would be important to estimate the possible effect of pollutants on the molluscan filtration activity.
Filtration of water and absorption of phyto- and bacterioplankton and other suspended matter by molluscs, as well as formation and excretion of fecal and pseudofecal pellets are important for processes occurring in an aquatic ecosystem (Ostroumov et al. [1997]; Ostroumov [2001]). Inhibition of filtration by pollutants (xenobiotics) may, in turn, induce other disturbances at several organizational levels (see Table 1) of the ecosystem. Examples of such disturbances are a decrease in water filtration by other hydrobionts, decrease in water transparency and the resultant decrease in penetration of photosynthetically active radiation and ultraviolet light, deterioration of the conditions for phytobenthos, excessive growth of phyto- and bacterioplankton, disturbances in the regulation of the composition of the algal–bacterial community, increase in detritus formation and siltage of benthic habitats, imbalance of the food web of phytoplankton consumers, decrease in the population growth of filter feeding organisms, decrease in the number of planktophagous larvae and deformation of the food web, and decrease in organic carbon deposition and concentration in bottom sediments (Ostroumov et al. [1997]; Ostroumov [2001]).
4. EXAMPLE OF APPLYING THE NEW APPROACH TO THE ANALYSIS OF ENVIRONMENTAL AND ECOLOGICAL HAZARDS
An important question is whether surfactants, which heavily contaminate environment and have not been sufficiently studied with respect to possible effects on organisms, may suppress filtration (Ostroumov [1986]); Telitchenko, Ostroumov [1990]; Ostroumov [1998]).
Data obtained in experiments on Mytilus edulis, M. galloprovincialis and some other marine and freshwater molluscs indicate that synthetic surfactants may disturb the plankton–benthos coupling (Ostroumov [1998], [2000a], [2000b], [2001]). Some surfactants, such as a nonionic surfactant Triton X-100 (TX100; an alkylphenol derivative), decrease the rates of water filtration and elimination of algae from water by mussels Mytilus edulis (Table 2). In the presence of 0.5 mg/l TX100, the concentration of algal cells after 90 min of filtration was 1092 cells per 0.5 ml of water versus 532 cells per 0.5 ml of water in the control sample (Table 2). In other words, an excess of algae as a result of filtration suppression was more than twofold (205%). If the TX100 concentration was increased to 2 mg/l, the concentration of algae after filtration was 2635 cells per 0.5 ml versus 556 cells per 0.5 ml in the control sample, i.e., the excess was almost fivefold (474 %). Thus, the inhibition increased with an increase in the surfactant concentration. These results are in excellent agreement with the data on the effects of other chemical compounds [13], including various surfactants, detergents, and other pollutants (Ostroumov et al. [1997]; Ostroumov [2000a], [2000b], [2001]). Recently new similar results were discovered while studying effects of the cationic surfactant tetradecyltrimetyhylammonium bromide on marine mussels (Ostroumov, Widdows, in preparation).
The system of criteria shown in Table 1 simplifies and systematizes the analysis of the ecological role and consequences of man-made disturbances of a given physiological function (in this case, disturbance of water filtration by molluscs). If we go sequentially from level to level, the suggested system will make it possible to follow the range of ecological consequences of a primary man-made disturbance at an individual level that manifests itself at higher levels of biological or ecological organization in an ecologically hazardous form.
In the given example, the change in the organism’s physiological activity (water filtration) is the directly observable effect of the xenobiotic (surfactant). However, we can estimate the ecological hazards more accurately if we consider the processes occurring at level 3 (a decrease in the seston elimination from water and a decrease in the plankton–benthos coupling) and at level 4 (a decrease in the formation and excretion of the pellets formed from the algal cells that have been removed from water).
Many other examples (Filenko [1988]; Flerov [1989]; Telitchenko & Ostroumov [1990]; Malakhov & Medvedeva [1991]; Yablokov & Ostroumov [1991]; Bezel’ et al [1994]) confirm the usefulness and effectiveness of the approach proposed (Table 1) for the analysis of ecological hazards of anthropogenic effects on the biota. More detail is given in our books recently published (Ostroumov [2000a], [2001]) as well as in the experimental article (Ostroumov [2002]).
5. CONCLUSION
The proposed level–block approach to the analysis of ecological hazards of anthropogenic alterations in ecosystems allows the multiplicity of anthropogenic effects on the biota to be efficiently systematized. This approach may be used to develop new objective criteria for estimation and classification of ecological and environmental hazards produced by anthropogenic effects on the biota, including the hazards produced by man-made chemicals that pollute the biosphere.
ACKNOWLEDGMENTS
I am grateful to P. Donkin and N.N.Kolotilova for collaboration, V.I. Artyukhova, D.A. Krivolutskii, Yu.I. Chernov, V.A. Abakumov, and A.O. Kasumyan for fruitful discussion and comments on the material, to Prof. Peter Wangersky for helpful advice.
This study was supported in part by the MacArthur Foundation. Collection of some data was supported by the EERO.
REFERENCES
Alimov A.F. [2000], Elements of Aquatic Ecosystem Function Theory. Nauka Press, St.Peterburg.
Bezel’, V.S., Bol’shakov, V.N., and Vorobeichik, E.L., [1994], Populyatsionnaya ekotoksikologiya (Population Ecotoxicology), Nauka Press, Moscow.
de Bruijn, J. and Struijs, J., [1997], Biodegradation in chemical substances policy. Biodegradation Kinetics, Brussels: SETAC-Europe, pp. 33–45.
Filenko, O.F., [1988], Vodnaya toksikologiya (Water Toxicology), Moscow University Press, Chernogolovka.
Flerov, B.A., [1989], Ekologo-fiziologicheskie aspekty toksikologi presnovodnykh zhivotnykh (Ecological and Physiological Aspects of Toxicology in Freshwater Animals), Nauka Press, Leningrad.
Krivolutskii, D.A., [1994], Pochvennaya fauna v ekotoksikologicheskom kontrole (Soil Fauna in the Ecological Control), Nauka Press, Moscow.
Malakhov, V.V. and Medvedeva, L.A., [1991], Embrional’noe razvitie dvustvorchatykh mollyuskov v norme i pri vozdeistvii tyazhelykh metallov (Embryonic Development of Bivalve Mollusks in the Norm and under Exposure to Heavy Metals), Nauka Press, Moscow.
Ostroumov, S.A., [1986], Vvedenie v biokhimicheskuyu ekologiyu (Introduction to the Biochemical Ecology), Moscow University Press, Moscow. –176 p.
Ostroumov, S.A., [1991], Responses of test-organisms to a quaternary ammonium compound. Vodnye Resursy (Water Resources). 2: 112-116. (in Russian, with English abstract)
Ostroumov S.A. [1998], Biological filtering and ecological machinery for self-purification and bioremediation in aquatic ecosystems: towards a holistic view. Rivista di Biologia/ Biology Forum. 91: 247-258.13.
Ostroumov, S.A., Donkin, P., and Staff, F., [1997], Effects of surfactants on mussels Mytilus edulis. Vestnik Moskovskogo Universitteta. Serija Biologiya (Bulletin of Moscow University. Series Biology.) 3 : 30 - 36. (in Russian with English abstract).
Ostroumov S.A. [2002], Inhibitory analysis of top-down control: new keys to studying eutrophication, algal blooms, and water self-purification. Hydrobiologia. 469: 117-129.
Ostroumov, S.A., [2000a], Biological effects of surfactants in connection with the anthropogenic impact on the biosphere. MAX Press, Moscow. 116 p.
Ostroumov S. A. [2000b], Criteria of Ecological Hazards Due to Anthropogenic Effects on the Biota: Searching for a System. Doklady Biological Sciences, Vol. 371: 204–206. (Translated from the Russian edition: Ostroumov, S.A., [2000] Doklady Akademii Nauk, 371 ( No. 6): 844–846).
Ostroumov, S.A., [2001], Biological effects of surfactants on organisms. MAX Press, Moscow. 334 p.
Stroganov, N.S., [1976], Obshchaya ekologiya. Biotsenologiya. Gidrobiologiya (General Ecology. Biocenology. Hydrobiology), Vol. 3: Vodnaya toksikologiya (Water Toxicology), VINITI Press, Moscow, pp. 5–47.
Telitchenko, M.M. and Ostroumov, S.A., [1990], Vvedenie v problemy biokhimicheskoi ekologii (Introduction to the Problem of Biochemical Ecology), Nauka Press, Moscow.
Wetzel R. [2001], Limnology. Academic Press, San-Diego et al.
Yablokov, A.V. and Ostroumov, S.A., [1983], Okhrana prirody: problemy i perspektivy (Protection of Nature: Problems and Prospects), Lespromizdat Press, Moscow.
Yablokov, A.V. and Ostroumov, S.A., [1985], Urovni okhranyzhivoi prirody (Levels of the Protection of Living Nature), Nauka Press, Moscow.
Yablokov, A.V. and Ostroumov, S.A., [1991]. Conservation of Living Nature and Resources: Problems, Trends and Prospects. Springer Press, Berlin.
Table 1. The level–block approach to the analysis of ecological hazards of anthropogenic effects on the biota . (After Ostroumov [2000a], [2000b], [2001], with some modifications)
Table 2. Amount of algae Isochrysis galbana in flasks containing mussels Mytilus edulis after 90 min of water filtration by the molluscs in the presence or absence of Triton X-100 (TX100, 0.5 mg/l). (After Ostroumov [2000b], with some changes).
Ostroumov S. A. Anthropogenic effects on the biota: towards a new system of principles and criteria for analysis of ecological hazards. Rivista di Biologia / Biology Forum. 2003. 96: 159-170. [ISSN 0035-6050] www.ncbi.nlm.nih.gov/pubmed/12852181; http://www.tilgher.it/(ekdo002s40etdh55stgyltvf)/index.aspx?lang=eng&tpr=4&act=abs&id=650; |
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Элементы теории биоконтроля качества воды: фактор экологической безопасности источников водоснабжения (=Elements of the theory of biocontrol of water quality: a factor in the ecological safety of the sources of water)
(публикация автора на scipeople)
Остроумов С.А.
- Химическая и биологическая безопасность. , 2009
Остроумов С.А. Элементы теории биоконтроля качества воды: фактор экологической безопасности источников водоснабжения (=Elements of the theory of...
Остроумов С.А. Элементы теории биоконтроля качества воды: фактор экологической безопасности источников водоснабжения (=Elements of the theory of biocontrol of water quality: a factor in the ecological safety of the sources of water) // Химическая и биологическая безопасность. 2008. № 5-6. с.36-39. Библиогр. 22 назв.
[http://www.cbsafety.ru/rus/saf_41_3.asp] УДК 574.6: 574.635: 602.7: 626.
119234, Москва, Ленгоры, Московский гос. университет им. М.В. Ломоносова, биологический факультет.
РЕФЕРАТ: Представлена новая теория биомеханизмов самоочищения воды, изложенная в книге автора «Гидробионты в самоочищении вод и биогенной миграции элементов» (М.: МАКС Пресс, 2008, 200 с.). Гидробионты активно участвуют в процессах, ведущих к очищению воды. В них участвуют почти все группы живых организмов, что анализируется в статье с различных сторон. При разработке теории были использованы результаты опытов автора, изучавшего воздействие поллютантов на живые организмы. Изложенная теория служит инновационной основой для создания новых экотехнологий очищения воды и повышения ее качества с использованием водных организмов. Представлены и обоснованы новые основные концепции, в том числе понятия и термины: biomachinery, экзометаболизм, экологические хеморегуляторы, экологические хемомедиаторы, макросимбиотические системы и другие. Новые результаты автора по выявлению свойства синтетических поверхностно-активных веществ (ПАВ) подавлять фильтрацию воды двустворчатыми моллюсками были признаны научным открытием и отмечены Дипломом за научное открытие № 274. Теория вносит вклад в научные основы укрепления экологической безопасности водных экосистем (водоемов и водотоков), которые служат источниками водоснабжения.
Ostroumov S.A. Elements of the theory of biocontrol of water quality: a factor in the ecological safety of the sources of water. // Chemical and Biological Safety (=Himicheskaja i biologicheskaja bezopasnost' , Moscow). 2008. No. 5-6. p.36-39. ABSTRACT: A new theory for the biomechanisms for water self-purification is presented in the author’s book ‘Aquatic Organisms in Water Self-Purification and Biogenic Migration of Elements’ (2008, 200 p.). Hydrobionts (aquatic organisms) are actively involved in various processes leading to water purification. Almost all main groups of organisms are involved, which is discussed and analyzed in the paper. In the theory, the results of the author's experiments on the effects of various pollutants on aquatic organisms were used. The theory is an innovative basis for new ecological technologies to clean water and to upgrade its quality by using aquatic organisms. New fundamental concepts were introduced and discussed, including the concepts and terms: biomachinery, exometabolism, ecological chemoregulators, ecological chemomediators, macrosymbiotic system and others. The new authors’s results on the surfactant-induced inhibition of water filtration by bivalves were recognized as a scientific discovery. As a result, the author was awarded Diploma for Scientific Discovery No. 274. The theory is a contribution to the scientific basis for environmental safety of the aquatic ecosystems (aquatic bodies and streams) that serve as sources of water supply.
Ключевые слова: качество воды, водные экосистемы, самоочищение воды, загрязнение; загрязняющие вещества, поллютанты, ксенобиотики, синтетические химические вещества, биотестирование, экологическая опасность, инновации, экологическая безопасность, источники водоснабжения, устойчивое использование, водные ресурсы, ресурсы пресной воды, морские, поверхностные водные экосистемы, новая концепция, экзометаболизм, биотрансформации, биодеградация, разложение, водоемы, водотоки, хеморегуляторы, макросимбиотические системы, биогенная миграция элементов, научное открытие № 274, антропогенное воздействие, экология, геохимия, репарация, поверхностно-активные вещества, ПАВ, детергенты, моющие средства, фильтраторы, биоконтроль, самоочистительный потенциал экосистемы, фитотехнология, фиторемедиация, экобиотехнология.
Key words: Water quality, aquatic ecosystems, water self-purification, pollution; pollutants, xenobiotics, synthetic chemicals, bioassays, biotesting, ecological hazards, innovations, environmental safety, sources of water supply, sustainable use, aquatic resources, freshwater, marine, surface aquatic ecosystems, new concept of exometabolism, pollutants, biotransformation, biodegradation, destruction, water bodies, streams, chemoregulators, macrosymbiotic system, biogenic migration of elements, scientific discovery No. 274, anthropogenic impact, ecology, geochemistry, repair, biomachinery, surfactants, tensides, detergents, filter-feeders, biocontrol, self-purification potential of ecosystems, phytotechnology, phytoremediation, ecobiotechnology.
Остроумов С.А. Элементы теории биоконтроля качества воды: фактор экологической безопасности источников водоснабжения (=Elements of the theory of biocontrol of water quality: a factor in the ecological safety of the sources of water) // Химическая и биологическая безопасность. 2008. № 5-6. с.36-39.
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The synecological approach to the problem of eutrophication (=Синэкологические основы решения проблемы эвтрофирования)
(публикация автора на scipeople)
Ostroumov S.A. (Остроумов С.А.)
- Doklady Biological Sciences , 2009
Ostroumov S.A. The synecological approach to the problem of eutrophication. - Doklady Biological Sciences, Vol. 381, 2001, p. 559–562. http://scipeople.com/uploads/materials/4389/Danbio6_2001v381n5.E.eutrophication.pdf [Translated from Doklady...
Ostroumov S.A. The synecological approach to the problem of eutrophication. - Doklady Biological Sciences, Vol. 381, 2001, p. 559–562. http://scipeople.com/uploads/materials/4389/Danbio6_2001v381n5.E.eutrophication.pdf [Translated from Doklady Akademii Nauk (DAN), Vol. 381, No. 5, 2001, p. 709–712. Original Russian Text Copyright © 2001 by Ostroumov S.A.] ISSN 0012-4966. DOI 10.1023/A:1013378505630
ABSTRACT: The author describes his vision of the new solution to the problem of eutrophication. This new vision is based on a synecological approach. In the paper, the author proposes a new two-component solution in order to protect the aquatic ecosystem from eutrophication. First, it is essential to reduce the input of nutrients. Second, it is equally important to reduce the input of the pollutants which weaken the potential of the ecosystem for removing the biomass of phytoplankton by filter-feeders. Those pollutants include surfactants, detergents, and some other compounds. Because synecology is one of key approaches in our analysis, this concept of counteracting eutrophication can be called a synecological solution to the problem. New experimental results: the detergent ‘Fairy’ inhibited the filtration rate of mussels Mytilus galloprovincialis; this complements the earlier data of the author on how detergents affect filter-feeders.
--KEY WORDS: danger of chemical pollution, hazards, xenobiotics, synthetic surface-active agents, surfactants, synthetic laundry detergents, heavy metals, mixtures, eutrophication, water filtration, clearance rate, invertebrates, pellets, filter-feeders, suspension feeders, bivalves, molluscs, rotifers, mussels, Mytilus edulis, Mytilus galloprovincialis, Crassostrea gigas, Dreissena, Unio, phytoplankton, zooplankton, algae, Daphnia, aquatic ecosystems, sustainable use of water resources, environmental safety, control of pollution and eutrophication, a new approach to solving the problem, man-made reservoirs.
--Остроумов С.А. Синэкологические основы решения проблемы эвтрофирования // Доклады академии наук (ДАН). 2001. том 381. № 5. С.709-712.
РЕФЕРАТ. Видение автором нового решения проблемы эвтрофирования основывается на синэкологическом подходе. Автор предлагает новый подход - двухкомпонентное решение в целях защиты водных экосистем от эвтрофирования. Оба компонента в равной степени важны и должны реализовываться (применяться на практике) одновременно. Во-первых, необходимо снизить поступление биогенов. Во-вторых, равным образом важно снизить поступление поллютантов, которые ослабляют потенциальную способность экосистем удалять биомассу фитопланктона благодаря активности фильтраторов. Эти поллютанты включают в себя поверхностно-активные вещества, детергенты и некоторые другие. Детергент Fairy ингибировал фильтрационную активность мидий Mytilus galloprovincialis, что дополняет ранее полученные данные автора о том, как детергенты воздействуют на фильтраторов. Поскольку синэкология – один из ключевых подходов в нашем анализе проблемы, эта концепция противодействия эвтрофирования может быть названа синэкологическим решением проблемы.
--Ключевые слова: опасность химического загрязнения, ксенобиотики, синтетические поверхностно-активные вещества (ПАВ), детергенты, синтетические моющие средства (СМС), тяжелые металлы, смесевые препараты, эвтрофикация, фильтрация воды, беспозвоночные, пеллеты, фильтраторы, двустворчатые моллюски, коловратки, мидии, Mytilus edulis, Mytilus galloprovincialis, Сrassostrea gigas, Dreissena, Unio, фитопланктон, зоопланктон, Daphnia, водные экосистемы, устойчивое использование водных ресурсов, экологическая безопасность, борьба с загрязнением и эвтрофикацией, новый подход к решению проблемы.
http://sites.google.com/site/bioeffectsofsurfactants/
http://sites.google.com/site/surfactantinhibitfilterfeed02/
http://sites.google.com/site/3surfactantsfiltrationmytilus/
http://sites.google.com/site/ostroumovsergei/
http://sites.google.com/site/bioticupgradewaterquality2008/
http://sites.google.com/site/ostroumovsa/
http://sites.google.com/site/biochemicalecology/
http://sites.google.com/site/ostroumovsapublicationsineng/
http://sites.google.com/site/ostroumovsapublicationsruen/
http://sites.google.com/site/ostroumovsergei/publications-that-cited-saostroumov
http://sites.google.com/site/biosphereostroumov/home
http://sites.google.com/site/ecologytobemostcitedtomorrow/home
http://sites.google.com/site/ecologytobemostcitedtomorrow/list-of-publications-by-sa-ostroumov
http://scipeople.ru/users/2943391/
The synecological approach to the problem of eutrophication. - Doklady Biological Sciences, Vol. 381, 2001, p. 559–562. [Translated from Doklady Akademii Nauk (DAN), Vol. 381, No. 5, 2001, p. 709–712. Original Russian Text Copyright © 2001 by Ostroumov S.A.] |