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Journal articles on the topic 'Biological impacts'

To see the other types of publications on this topic, follow the link: Biological impacts.

Author: Grafiati

Published: 10 December 2022

Last updated: 19 February 2023

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1

Feldmann, Rodney M. "On impacts and extinction: biological solutions to biological problems." Journal of Paleontology 64, no. 1 (January 1990): 151–54. http://dx.doi.org/10.1017/s0022336000042347.

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There appears to be an overwhelming urge in the study of earth sciences currently to discover the “cosmic generality.” Certainly, no observational and descriptive aspects of the study of earth history can be concluded until one has placed the observations into a broader context. On the other hand, there are not very many “cosmic generalities” and few lasting generalizations have been developed before the basic data have been gathered. When generalizations do precede observations, the former fall into the category of testable hypotheses or speculations, depending upon the overall plausibility of the ideas and the generosity of the reader.

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2

Klein, Sabra L., Santosh Dhakal, Rebecca L. Ursin, Sharvari Deshpande, Kathryn Sandberg, and Franck Mauvais-Jarvis. "Biological sex impacts COVID-19 outcomes." PLOS Pathogens 16, no. 6 (June 22, 2020): e1008570. http://dx.doi.org/10.1371/journal.ppat.1008570.

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3

Howarth, Francis G. "Environmental Impacts of Classical Biological Control." Annual Review of Entomology 36, no. 1 (January 1991): 485–509. http://dx.doi.org/10.1146/annurev.en.36.010191.002413.

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4

Sun, Gui-Quan, Xue-Zhi Li, Yi Wang, Amit Chakraborty, Zhen Wang, and Yong-Ping Wu. "Impacts of Climate Change on Biological Dynamics." Discrete Dynamics in Nature and Society 2016 (2016): 1–2. http://dx.doi.org/10.1155/2016/9046107.

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5

Almaas, E. "Biological impacts and context of network theory." Journal of Experimental Biology 210, no. 9 (May 1, 2007): 1548–58. http://dx.doi.org/10.1242/jeb.003731.

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6

Ellis, Colin A., Slavé Petrovski, and Samuel F. Berkovic. "Epilepsy genetics: clinical impacts and biological insights." Lancet Neurology 19, no. 1 (January 2020): 93–100. http://dx.doi.org/10.1016/s1474-4422(19)30269-8.

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7

Mclaren, D. J., and W. D. Goodfellow. "Geological and Biological Consequences of Giant Impacts." Annual Review of Earth and Planetary Sciences 18, no. 1 (May 1990): 123–71. http://dx.doi.org/10.1146/annurev.ea.18.050190.001011.

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8

Mack, Michelle C., and Caria M. D'Antonio. "Impacts of biological invasions on disturbance regimes." Trends in Ecology & Evolution 13, no. 5 (May 1998): 195–98. http://dx.doi.org/10.1016/s0169-5347(97)01286-x.

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9

Crystal-Ornelas, Robert, Emma J. Hudgins, Ross N. Cuthbert, Phillip J. Haubrock, Jean Fantle-Lepczyk, Elena Angulo, Andrew M. Kramer, et al. "Economic costs of biological invasions within North America." NeoBiota 67 (July 29, 2021): 485–510. http://dx.doi.org/10.3897/neobiota.67.58038.

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Invasive species can have severe impacts on ecosystems, economies, and human health. Though the economic impacts of invasions provide important foundations for management and policy, up-to-date syntheses of these impacts are lacking. To produce the most comprehensive estimate of invasive species costs within North America (including the Greater Antilles) to date, we synthesized economic impact data from the recently published InvaCost database. Here, we report that invasions have cost the North American economy at least US$ 1.26 trillion between 1960 and 2017. Economic costs have climbed over recent decades, averaging US$ 2 billion per year in the early 1960s to over US$ 26 billion per year in the 2010s. Of the countries within North America, the United States (US) had the highest recorded costs, even after controlling for research effort within each country ($5.81 billion per cost source in the US). Of the taxa and habitats that could be classified in our database, invasive vertebrates were associated with the greatest costs, with terrestrial habitats incurring the highest monetary impacts. In particular, invasive species cumulatively (from 1960–2017) cost the agriculture and forestry sectors US$ 527.07 billion and US$ 34.93 billion, respectively. Reporting issues (e.g., data quality or taxonomic granularity) prevented us from synthesizing data from all available studies. Furthermore, very few of the known invasive species in North America had reported economic costs. Therefore, while the costs to the North American economy are massive, our US$ 1.26 trillion estimate is likely very conservative. Accordingly, expanded and more rigorous economic cost reports are necessary to provide more comprehensive invasion impact estimates, and then support data-based management decisions and actions towards species invasions.

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10

Castro-Guedes, Camila Fediuk de, and Lúcia Massutti de Almeida. "ENVIRONMENTAL IMPACTS OF ARTHROPODS AS BIOLOGICAL CONTROL AGENTS." Oecologia Australis 21, no. 02 (November 2017): 268–79. http://dx.doi.org/10.4257/oeco.2017.2103.04.

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11

Cohn, Jeffrey P. "Gauging the Biological Impacts of the Greenhouse Effect." BioScience 39, no. 3 (March 1989): 142–46. http://dx.doi.org/10.2307/1311022.

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12

Cullen, J. M. "Biological control and impacts on non-target species." Proceedings of the New Zealand Plant Protection Conference 50 (August 1, 1997): 195–201. http://dx.doi.org/10.30843/nzpp.1997.50.11352.

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13

HUEY, Raymond B., Lauren B. BUCKLEY, and Weiguo DU. "Biological buffers and the impacts of climate change." Integrative Zoology 13, no. 4 (July 2018): 349–54. http://dx.doi.org/10.1111/1749-4877.12321.

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14

Kako, Koichiro, Jun-Dal Kim, and Akiyoshi Fukamizu. "Emerging impacts of biological methylation on genetic information." Journal of Biochemistry 165, no. 1 (September 14, 2018): 9–18. http://dx.doi.org/10.1093/jb/mvy075.

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15

Clark, Graeme C., Nicholas R. Casewell, Christopher T. Elliott, Alan L. Harvey, Andrew G. Jamieson, Peter N. Strong, and Andrew D. Turner. "Friends or Foes? Emerging Impacts of Biological Toxins." Trends in Biochemical Sciences 44, no. 4 (April 2019): 365–79. http://dx.doi.org/10.1016/j.tibs.2018.12.004.

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16

Cripps, Gemma, Stephen Widdicombe, John I. Spicer, and Helen S. Findlay. "Biological impacts of enhanced alkalinity in Carcinus maenas." Marine Pollution Bulletin 71, no. 1-2 (June 2013): 190–98. http://dx.doi.org/10.1016/j.marpolbul.2013.03.015.

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17

Stoms, David M., Stephanie L. Dashiell, and Frank W. Davis. "Siting solar energy development to minimize biological impacts." Renewable Energy 57 (September 2013): 289–98. http://dx.doi.org/10.1016/j.renene.2013.01.055.

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18

Wiesebron, Lauren E., John K. Horne, and A. Noble Hendrix. "Characterizing biological impacts at marine renewable energy sites." International Journal of Marine Energy 14 (June 2016): 27–40. http://dx.doi.org/10.1016/j.ijome.2016.04.002.

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19

Stramma, Lothar, Sunke Schmidtko, Lisa A. Levin, and Gregory C. Johnson. "Ocean oxygen minima expansions and their biological impacts." Deep Sea Research Part I: Oceanographic Research Papers 57, no. 4 (April 2010): 587–95. http://dx.doi.org/10.1016/j.dsr.2010.01.005.

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20

Fraser, Ceridwen I., Raisa Nikula, Daniel E. Ruzzante, and Jonathan M. Waters. "Poleward bound: biological impacts of Southern Hemisphere glaciation." Trends in Ecology & Evolution 27, no. 8 (August 2012): 462–71. http://dx.doi.org/10.1016/j.tree.2012.04.011.

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21

Keller, David P., Iris Kriest, Wolfgang Koeve, and Andreas Oschlies. "Southern Ocean biological impacts on global ocean oxygen." Geophysical Research Letters 43, no. 12 (June 25, 2016): 6469–77. http://dx.doi.org/10.1002/2016gl069630.

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22

Downing, Keith. "A GENERAL MIGRATION MODEL FOR BIOLOGICAL IMPACT ASSESSMENT." International Oil Spill Conference Proceedings 1995, no. 1 (February 1, 1995): 906–8. http://dx.doi.org/10.7901/2169-3358-1995-1-906.

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ABSTRACT To develop a tool to quantify the potential biological impacts of oil spills in the Barents Sea marginal ice zone, a generalized migration model, driven by biological field data, was made to reproduce detailed movement patterns of individuals within a population. This model (MIGMOD) has been coupled to the natural resource impact model system to provide a complete set of working tools for environmental impact assessment.

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23

Convey, Peter, and Lloyd S. Peck. "Antarctic environmental change and biological responses." Science Advances 5, no. 11 (November 2019): eaaz0888. http://dx.doi.org/10.1126/sciadv.aaz0888.

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Antarctica and the surrounding Southern Ocean are facing complex environmental change. Their native biota has adapted to the region’s extreme conditions over many millions of years. This unique biota is now challenged by environmental change and the direct impacts of human activity. The terrestrial biota is characterized by considerable physiological and ecological flexibility and is expected to show increases in productivity, population sizes and ranges of individual species, and community complexity. However, the establishment of non-native organisms in both terrestrial and marine ecosystems may present an even greater threat than climate change itself. In the marine environment, much more limited response flexibility means that even small levels of warming are threatening. Changing sea ice has large impacts on ecosystem processes, while ocean acidification and coastal freshening are expected to have major impacts.

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24

Zhou, Yongchao, Yan Ma, Lei Fang, and Yiping Guo. "Impacts of biological activities on erosion of sewer sediments." Proceedings of the Institution of Civil Engineers - Water Management 169, no. 1 (February 2016): 43–52. http://dx.doi.org/10.1680/wama.14.00134.

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25

Weiming, He. "Biological invasions: Are their impacts precisely knowable or not?" Biodiversity Science 28, no. 2 (2020): 253–55. http://dx.doi.org/10.17520/biods.2020008.

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26

Rosenzweig, Cynthia, David Karoly, Marta Vicarelli, Peter Neofotis, Qigang Wu, Gino Casassa, Annette Menzel, et al. "Attributing physical and biological impacts to anthropogenic climate change." Nature 453, no. 7193 (May 2008): 353–57. http://dx.doi.org/10.1038/nature06937.

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27

Osborn, Dan. "The breadth of climate change impacts on biological systems." Emerging Topics in Life Sciences 3, no. 2 (April 30, 2019): 107–13. http://dx.doi.org/10.1042/etls20180114.

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Abstract Human activity is driving climate change. This is affecting and will affect many aspects of life on earth. The breadth of its impacts is very wide and covers human, animal and plant health, and also the planet's biodiversity and the services that deliver benefits to people from natural capital. Finding solutions to the challenge of climate change will require multidisciplinary action in which the life sciences have a major role to play as this issue of Emerging Topics in Life Sciences indicates. More process and mechanistic knowledge could underpin solutions or even provide early warning of impacts. Any solutions will need to be developed and deployed in ways that gain and maintain public support.

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28

May, M. "LIFE SCIENCE TECHNOLOGIES: Big biological impacts from big data." Science 344, no. 6189 (June 12, 2014): 1298–300. http://dx.doi.org/10.1126/science.344.6189.1298.

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29

Vo, Thuy Thi Bich, Binh Thi Nguyen Le, Hai Van Nong, Hyun Yang, and Eui-Bae Jeung. "Environmental Chemical-Dioxin Impacts on Biological Systems: A Review." Journal of Embryo Transfer 28, no. 2 (June 30, 2013): 95–111. http://dx.doi.org/10.12750/jet.2013.28.2.95.

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30

Jobling, Malcolm. "Environmental Impacts of Aquaculture (Sheffield Biological Sciences, Vol. 5)." Fish and Fisheries 2, no. 2 (June 2001): 173. http://dx.doi.org/10.1046/j.1467-2979.2001.00039-2.x.

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31

Brown, J. C., V. D. Jolley, and R. E. Terry. "Iron: Impacts of some genetic mutations on biological development." Journal of Plant Nutrition 15, no. 10 (October 1992): 2109–26. http://dx.doi.org/10.1080/01904169209364461.

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32

Nyberg, Kevin G., and Richard W. Carthew. "Out of the testis: biological impacts of new genes." Genes & Development 31, no. 18 (September 15, 2017): 1825–26. http://dx.doi.org/10.1101/gad.307496.117.

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33

Frenot, Yves, Steven L. Chown, Jennie Whinam, Patricia M. Selkirk, Peter Convey, Mary Skotnicki, and Dana M. Bergstrom. "Biological invasions in the Antarctic: extent, impacts and implications." Biological Reviews 80, no. 1 (February 2005): 45–72. http://dx.doi.org/10.1017/s1464793104006542.

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34

Gaston, Kevin J., Thomas W. Davies, Sophie L. Nedelec, and Lauren A. Holt. "Impacts of Artificial Light at Night on Biological Timings." Annual Review of Ecology, Evolution, and Systematics 48, no. 1 (November 2, 2017): 49–68. http://dx.doi.org/10.1146/annurev-ecolsys-110316-022745.

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35

Sheldon, Kimberly S., and Michael E. Dillon. "Beyond the Mean: Biological Impacts of Cryptic Temperature Change." Integrative and Comparative Biology 56, no. 1 (April 13, 2016): 110–19. http://dx.doi.org/10.1093/icb/icw005.

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36

Bandari, Anashe. "Water exchange in magnesium’s hydration shells impacts biological processes." Scilight 2020, no. 24 (June 12, 2020): 241109. http://dx.doi.org/10.1063/10.0001471.

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37

GOTSCH, NIKOLAUS, URS BERNEGGER, and PETER RIEDER. "Impacts of future biological-technological progress on arable farming." European Review of Agricultural Economics 20, no. 1 (1993): 19–34. http://dx.doi.org/10.1093/erae/20.1.19.

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38

Sciberras, Josette, Raymond Zammit, and Patricia Vella Bonanno. "The European framework for intellectual property rights for biological medicines." Generics and Biosimilars Initiative Journal 10, no. 4 (December 15, 2021): 172–83. http://dx.doi.org/10.5639/gabij.2021.1004.022.

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Introduction: The Pharmaceutical Strategy for Europe (2020) proposes actions related to intellectual property (IP) rights as a means of ensuring patients’ access to medicines. This review aims to describe and discuss the European IP framework and its impact on accessibility of biological medicines and makes some recommendations. Methods: A non-systematic literature review on IP for biological medicines was conducted. Data on authorizations and patent and exclusivity expiry dates of biological medicines obtained from the European Medicines Agency’s (EMA) website and literature was analysed quantitatively and qualitatively. Results: The analysis showed that as at end July 2021, 1,238 medicines were authorized in Europe, of which 332 (26.8%) were biological medicines. There were only 55 biosimilars for 17 unique biologicals. There is an increasing trend in biological authorizations but signifi cant delays in submission of applications for marketing authorization of biosimilars, with no signifi cant diff erences in the time for assessment for marketing authorization between originator biologicals and biosimilars. For some of the more recent biosimilars, applications for authorization were submitted prior to patent and exclusivity expiry. COVID vaccines confi rmed the impact of knowledge transfer on accessibility, especially when linked to joint procurement. Discussion: IP protects originator products and impacts the development of biosimilars. Strategies to improve competition in the EU biological market are discussed. Pricing policies alone do not increase biosimilar uptake since patients are switched to second generation products. Evergreening strategies might be abusing the IP framework, and together with trade secrets and disproportionate prices compared to R & D and manufacturing costs lead to an imbalance between market access and innovation. Conclusion: The European Pharmaceutical Strategy should focus on IP initiatives that support earlier authorization of biosimilars of new biologicals. Recommendations include knowledge sharing, simplifi cation of the regulatory framework and transparency of prices and R & D costs.

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39

Buchori, Damayanti. "Dampak non-target dari pengendalian hayati spesies asing terhadap ekosistem." Jurnal Entomologi Indonesia 4, no. 1 (February 23, 2017): 54. http://dx.doi.org/10.5994/jei.4.1.54.

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Non target impact of classical biological control of exotic species in the ecosystem. Classical biological control has been hailed as a successful control method of many exotic species of pests. However, recently this method of control has been questioned due to several cases of non target impact. Non target impact can occur two ways, i.e. direct non target impact when there is a host shift of the bioagents (e.g. changes in preferences), and the indirect non target impact which can occur through, among others, food web subsides that will change the overall interactions of many species within an ecosystem. The aim of this paper is to understand the interactions between introduced exotic agents (e.g. insects) toward local diversity, e.g. what are the implications of the interactions toward local biodiversity? Are there non target and indirect impacts of these introductions in Indonesia? The discussions covers the concept of biological control and conservation issues that should be taken into consideration, particularly in the context of insect conservation and impacts of classical biological control on island diversity.

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40

DUDLEY, J. P., and M. H. WOODFORD. "Bioweapons, bioterrorism and biodiversity: potential impacts of biological weapons attacks on agricultural and biological diversity." Revue Scientifique et Technique de l'OIE 21, no. 1 (April 1, 2002): 125–37. http://dx.doi.org/10.20506/rst.21.1.1328.

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41

Dickey, James W. E., Neil E. Coughlan, Jaimie T. A. Dick, Vincent Médoc, Monica McCard, Peter R. Leavitt, Gérard Lacroix, Sarah Fiorini, Alexis Millot, and Ross N. Cuthbert. "Breathing space: deoxygenation of aquatic environments can drive differential ecological impacts across biological invasion stages." Biological Invasions 23, no. 9 (April 30, 2021): 2831–47. http://dx.doi.org/10.1007/s10530-021-02542-3.

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AbstractThe influence of climate change on the ecological impacts of invasive alien species (IAS) remains understudied, with deoxygenation of aquatic environments often-overlooked as a consequence of climate change. Here, we therefore assessed how oxygen saturation affects the ecological impact of a predatory invasive fish, the Ponto-Caspian round goby (Neogobius melanostomus), relative to a co-occurring endangered European native analogue, the bullhead (Cottus gobio) experiencing decline in the presence of the IAS. In individual trials and mesocosms, we assessed the effect of high, medium and low (90%, 60% and 30%) oxygen saturation on: (1) functional responses (FRs) of the IAS and native, i.e. per capita feeding rates; (2) the impact on prey populations exerted; and (3) how combined impacts of both fishes change over invasion stages (Pre-invasion, Arrival, Replacement, Proliferation). Both species showed Type II potentially destabilising FRs, but at low oxygen saturation, the invader had a significantly higher feeding rate than the native. Relative Impact Potential, combining fish per capita effects and population abundances, revealed that low oxygen saturation exacerbates the high relative impact of the invader. The Relative Total Impact Potential (RTIP), modelling both consumer species’ impacts on prey populations in a system, was consistently higher at low oxygen saturation and especially high during invader Proliferation. In the mesocosm experiment, low oxygen lowered RTIP where both species were present, but again the IAS retained high relative impact during Replacement and Proliferation stages at low oxygen. We also found evidence of multiple predator effects, principally antagonism. We highlight the threat posed to native communities by IAS alongside climate-related stressors, but note that solutions may be available to remedy hypoxia and potentially mitigate impacts across invasion stages.

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42

Underwood, AJ. "Beyond BACI: Experimental designs for detecting human environmental impacts on temporal variations in natural populations." Marine and Freshwater Research 42, no. 5 (1991): 569. http://dx.doi.org/10.1071/mf9910569.

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Biological effects of environmental impacts are usually defined simplistically in terms of changes in the mean of some biological variable. Many types of impact do not necessarily change long-run mean abundances. Here, designs for detection of environmental impact are reviewed and some of their shortcomings noted. New sampling designs to detect impacts that cause changes in temporal variance in abundance of populations, rather than their means, are described. These designs are effective at distinguishing pulse and press episodes of disturbance and could be used for other variables of interest (size, reproductive state, rate of growth, number of species, etc.) for monitoring. The designs require sampling different time-scales before and after a proposed development that might cause impact. Cases are discussed in which there is a single control location. Inadequacies of this approach for detection of environmental impact are mentioned, with some discussion of the consequences for management of impacts that cause temporal change rather than alterations of the mean abundance of a population.

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43

Blaustein, Richard. "Global Human Impacts." BioScience 58, no. 4 (April 1, 2008): 376. http://dx.doi.org/10.1641/b580419.

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44

Aljubori, Nemah. "The Biological and Psychological Impacts of Drug Addiction: A Review." Vol.3, No.2 3, no. 2 (April 22, 2020): 4–11. http://dx.doi.org/10.32441/aajms.3.2.2.

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45

Brown, Dennis F., and John A. Arway. "BIOLOGICAL IMPACTS OF OIL AND GAS DEVELOPMENT IN NORTHWEST PENNSYLVANIA." International Oil Spill Conference Proceedings 1987, no. 1 (April 1, 1987): 624A. http://dx.doi.org/10.7901/2169-3358-1987-1-624a.

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46

Zettlemoyer, Meredith A., and Megan L. DeMarche. "Dissecting impacts of phenological shifts for performance across biological scales." Trends in Ecology & Evolution 37, no. 2 (February 2022): 147–57. http://dx.doi.org/10.1016/j.tree.2021.10.004.

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47

Sampadi, Bharath, Leon H. F. Mullenders, and Harry Vrieling. "Phosphoproteomics Sample Preparation Impacts Biological Interpretation of Phosphorylation Signaling Outcomes." Cells 10, no. 12 (December 3, 2021): 3407. http://dx.doi.org/10.3390/cells10123407.

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The influence of phosphoproteomics sample preparation methods on the biological interpretation of signaling outcome is unclear. Here, we demonstrate a strong bias in phosphorylation signaling targets uncovered by comparing the phosphoproteomes generated by two commonly used methods—strong cation exchange chromatography-based phosphoproteomics (SCXPhos) and single-run high-throughput phosphoproteomics (HighPhos). Phosphoproteomes of embryonic stem cells exposed to ionizing radiation (IR) profiled by both methods achieved equivalent coverage (around 20,000 phosphosites), whereas a combined dataset significantly increased the depth (>30,000 phosphosites). While both methods reproducibly quantified a subset of shared IR-responsive phosphosites that represent DNA damage and cell-cycle-related signaling events, most IR-responsive phosphoproteins (>82%) and phosphosites (>96%) were method-specific. Both methods uncovered unique insights into phospho-signaling mediated by single (SCXPhos) versus double/multi-site (HighPhos) phosphorylation events; particularly, each method identified a distinct set of previously unreported IR-responsive kinome/phosphatome (95% disparate) directly impacting the uncovered biology.

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48

Knight, J. D. "Frequency of field pea in rotations impacts biological nitrogen fixation." Canadian Journal of Plant Science 92, no. 6 (November 2012): 1005–11. http://dx.doi.org/10.4141/cjps2011-274.

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Knight, J. D. 2012. Frequency of field pea in rotations impacts biological nitrogen fixation. Can. J. Plant Sci. 92: 1005–1011. Economic, environmental and energy concerns about the use of nitrogen (N) fertilizers in crop production have prompted the examination of increasing the frequency of pulses in crop rotations to capitalize on biological nitrogen fixation (BNF). Plots from a field experiment established in 1998 at the Agriculture and Agri-Food Canada Research Farm at Scott, SK, were sampled in 2008, 2009 and 2010. Rotations that included pea every year (continuous pea), every second year (pea-wheat), every third year (pea-canola-wheat) and every fourth year (canola-wheat-pea-wheat) were evaluated for BNF using the enriched15N isotope dilution technique. Nitrogen from BNF in the seed and straw, total above-ground N, seed and straw yield and soil available N and P were evaluated. In 2 of 3 yr, the highest BNF occurred in the two most diverse rotations. Continuous cropping of pea resulted in drastically low BNF in 2008 and 2009. Nitrogen derived from atmosphere in the continuous pea was 15% compared with an average of approximately 55% across all other rotations in these 2 yr. The reduction in BNF was not due to lower productivity in the continuous pea rotation, nor from higher initial soil inorganic N levels inhibiting BNF. In the third year of the study (2010), the more than double the normal precipitation received during the growing season stimulated BNF in pea in the continuous pea rotation. Determining whether the rotation effects on BNF are due to N mineralization of the previous years’ crop residues requires further investigation.

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49

Dormaar, Johan F., and Walter D. Willms. "Rangeland Management Impacts on Soil Biological Indicators in Southern Alberta." Journal of Range Management 53, no. 2 (March 2000): 233. http://dx.doi.org/10.2307/4003289.

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50

Лаптев, А., A. Laptev, Д. Бугай, D. Bugay, Анатолий Александров, Anatoliy Aleksandrov, Валерий Ларионов, and Valeriy Larionov. "Impacts of Environmental and Biological Factors on Complex Technical Systems." Safety in Technosphere 6, no. 4 (December 18, 2017): 21–30. http://dx.doi.org/10.12737/article_5a28ffd347e557.03010714.

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The analysis of climate change in the Russian Federation has been carried out. It has been shown that the major climate change is occurring in the Arctic zone — increased emissions of carbon dioxide and methane, deep permafrost thawing. Due to the change of climatic conditions, improvement of the ecological situation and wide use of biological cleaning systems for a treatment of industrial and household effluents a change of biological systems is taking place. Natural selection of microorganisms capable to use as a nutritious substratum such previously inert materials as polyethylene and polypropylene is intensified. The change of climatic conditions in which complex technical systems are operated, and the impact of biological and ecological factors on these systems dictate the need for revision of approaches to creation, design and operation of appropriate technical means. Actions for standardization of procedure for products climatic qualification taking into account the influence of newly forming climatic, ecological and biological conditions will allow considerably reduce economic losses from corrosion, aging and biodeterioration of complex technical systems. The work has been carried out in the frame of implementation of complex research area 18 “Climatic Tests for Safety Provision and Protection from Corrosion, Aging and Biodeterioration of Materials, Constructions and Complex Technical System in Natural Environments” (“Strategic Areas for Development of Materials and Their Treatment Technologies for the Period until 2030”).

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