Gotowe bibliografie tematyczne / Eutrophication

Gotowa bibliografia na temat „Eutrophication”

Autor: Grafiati
Data publikacji: 4 czerwca 2021
Data aktualizacji: 31 lipca 2024

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Artykuły w czasopismach na temat "Eutrophication"

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O'Sullivan, P. E. "Eutrophication". International Journal of Environmental Studies 47, nr 3-4 (marzec 1995): 173–95. http://dx.doi.org/10.1080/00207239508710958.

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Hobson, Louis A. "Surf eutrophication?" Marine Pollution Bulletin 16, nr 12 (grudzień 1985): 499. http://dx.doi.org/10.1016/0025-326x(85)90385-6.

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Ellis, Derek. "Surf eutrophication?" Marine Pollution Bulletin 16, nr 11 (listopad 1985): 425–26. http://dx.doi.org/10.1016/0025-326x(85)90391-1.

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Wood, Brian, i D. Harper. "Eutrophication of Freshwaters." Journal of Ecology 81, nr 4 (grudzień 1993): 831. http://dx.doi.org/10.2307/2261685.

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Fulweiler, R. W., N. N. Rabalais i A. S. Heiskanen. "The eutrophication commandments". Marine Pollution Bulletin 64, nr 10 (październik 2012): 1997–99. http://dx.doi.org/10.1016/j.marpolbul.2012.07.025.

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Bunt, J. S. "Marine coastal eutrophication". Aquatic Botany 49, nr 4 (marzec 1995): 275–76. http://dx.doi.org/10.1016/0304-3770(95)90022-5.

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Martínez‐Girón, Rafael, i Cristina Martínez‐Torre. "Eutrophication in histopathology". Histopathology 75, nr 1 (6.05.2019): 137–38. http://dx.doi.org/10.1111/his.13852.

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Burkholder, JoAnn M., David A. Tomasko i Brant W. Touchette. "Seagrasses and eutrophication". Journal of Experimental Marine Biology and Ecology 350, nr 1-2 (listopad 2007): 46–72. http://dx.doi.org/10.1016/j.jembe.2007.06.024.

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Pearson, Tom. "Marine coastal eutrophication". Journal of Experimental Marine Biology and Ecology 176, nr 1 (marzec 1994): 141–43. http://dx.doi.org/10.1016/0022-0981(94)90202-x.

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Pan, Jun, Yang Liu, Chang Hong Li i Juan Wang. "Eutrophication Assessment of Reservoir Based on Matter-Element and Extension". Advanced Materials Research 599 (listopad 2012): 229–32. http://dx.doi.org/10.4028/www.scientific.net/amr.599.229.

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The eutrophication of medium-sized reservoirs in Shenyang is assessed to explore the feasibility of matter-element and extension using in assessing the eutrophication of water. The evaluation standard is established with related factors, and the eutrophication level is determined by correlation degree. The results show that, assessing eutrophication of water with this method, can not only determine the eutrophication level exactly, but also reflects the changing trend of the water. It is more appropriate than other methods in eutrophication assessment.
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Rozprawy doktorskie na temat "Eutrophication"

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Miroshnichenko, Y. V. "Eutrophication". Thesis, Сумський державний університет, 2013. http://essuir.sumdu.edu.ua/handle/123456789/31125.

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Aquatic plants need two essential nutrients for growth: phosphorus and nitrogen. They receive these nutrients through a process known as eutrophication, in which water bodies accumulate plant nutrients. In a healthy lake both nutrients occur in limited amounts, restricting plant growth. However, human factors can dramatically increase the concentration of plant nutrients in water bodies, a phenomenon known as “cultural eutrophication”. The rise in eutrophic events has been attributed to the rapid increase in intensive agricultural practices, industrial activities, and population growth which together have increased nitrogen and phosphorus flows in the environment. When you are citing the document, use the following link http://essuir.sumdu.edu.ua/handle/123456789/31125
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Petriyako, N. V. "Eutrophication". Thesis, Sumy State University, 2014. http://essuir.sumdu.edu.ua/handle/123456789/45134.

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The process of eutrophication is natural. For many lakes, as they age over centuries, there is a buildup of nutrients, sediment, and plant material, which slowly fill the lake basin. Eventually, the process ends and the basin becomes colonized by terrestrial vegetation. The timing of natural eutrophication is highly variable and depends on the characteristics of the basin, watershed, and climate.
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Cairns, Stefan H. 1949. "Eutrophication Monitoring and Prediction". Thesis, University of North Texas, 1993. https://digital.library.unt.edu/ark:/67531/metadc277850/.

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Changes in trophic status are often related to increases or decreases in the allocthonous inputs of nutrients from changes in land use and management practices. Lake and reservoir managers are continually faced with the questions of what to monitor, how to monitor it, and how much change is necessary to be considered significant. This study is a compilation of four manuscripts, addressing one of these questions, using data from six reservoirs in Texas.
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Malmaeus, Jan Mikael. "Predictive Modeling of Lake Eutrophication". Doctoral thesis, Uppsala University, Department of Earth Sciences, 2004. http://urn.kb.se/resolve?urn=urn:nbn:se:uu:diva-4625.

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This thesis presents predictive models for important variables concerning eutrophication effects in lakes. The keystone is a dynamic phosphorus model based on ordinary differential equations. By calculating mass fluxes of phosphorus into, within and out from a lake, the concentrations of different forms of phosphorus in different compartments of the lake are estimated.

The dynamic phosphorus model is critically tested and several improvements are presented, including two new compartments for colloidal phosphorus, a sub-model for suspended particulate matter (SPM) and new algorithms for lake outflow, water mixing, diffusion, water content and organic content of accumulation sediments are implemented. Predictions with the new version show good agreement against empirical data in five tested lakes.

The sub-model for SPM uses the same driving variables as the basic phosphorus model, so the inclusion of this model as a sub-model does not require any additional variables. The model for SPM may also be used as a separate model giving monthly predictions of suspended particulate matter in two water compartments and one compartment with SPM available for resuspension in ET-sediments.

Empirical data from Lake Erken (Sweden) and Lake Balaton (Hungary) are used to evaluate the variability in settling velocity of SPM. It is found that the variability is substantial and may be accounted for by using a dimensionless moderator for SPM concentration. Empirical data from accumulation area sediments in Lake Erken are used to develop a model for the dynamics of phosphorus sedimentation, burial and diffusion in the sediments. The model is shown to provide reasonable monthly predictions of four functional forms of phosphorus at different sediment depths.

Simulations with the lake phosphorus model using two different climate scenarios indicate that lakes may respond very differently to climate change depending on their physical character. Lake Erken, with a water retention time of 7 years, appears to be much more sensitive than two basins of Lake Mälaren (Sweden) with substantially shorter retention times. The implication would be that in eutrophic lakes with long water retention times, eutrophication problems may become serious if the future becomes warmer. This will be important in contexts of lake management when remedial measures against lake eutrophication have to be taken.

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Lemley, Daniel Alan. "Assessing symptoms of eutrophication in estuaries". Thesis, Nelson Mandela Metropolitan University, 2015. http://hdl.handle.net/10948/3427.

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Water quality and ecological integrity of estuaries reflect activities within the entire upstream catchment. Much emphasis has been placed on the response of estuaries to anthropogenic stressors through the use of monitoring programmes. Key to the success of these programmes is the use of indicators as they transform data into useful information. The ultimate aim of this study was to identify eutrophic symptoms in selected estuaries in the Gouritz Water Management Area (WMA) using a multi-metric classification method. The study sites included the permanently open Duiwenhoks, Goukou, Gouritz, and Kaaimans estuaries, as well as the temporarily open/closed Hartenbos, Klein Brak, Great Brak, Gwaing, and Goukamma estuaries. Initially, the “pressure” associated with all the estuaries in the Gouritz WMA was determined (e.g. total daily nutrient loads and changes in river inflow affecting flushing time) using long-term flow and water quality monitoring data provided by the Department of Water Affairs (DWA). Subsequently, the “state” of the selected estuaries was assessed using a variety of indicators, including: inorganic nutrients (~ N and P), phytoplankton, epiphytes and microphytobenthos. Estuaries with longer flushing time suggested greater vulnerability to eutrophication. For example, the Gwaing (281.11 kg DIN d-1; 78.85 kg DIP d-1) and Hartenbos (38.33 kg DIN d-1; 21.51 kg DIP d-1) estuaries generally received the highest daily inorganic nutrient loads. However, at the time of sampling, the Hartenbos Estuary had a longer flushing time (i.e. weeks) compared to the Gwaing Estuary (i.e. couple of days). Field data confirmed the greater vulnerability to eutrophication associated with longer flushing times, as the indicators measured in the Hartenbos Estuary exceeded all the proposed ‘thresholds’ of a eutrophic system (~ overall ‘Poor’ condition). The Great Brak Estuary (~ overall ‘Fair’ condition) provided an interesting example where eutrophic symptoms were only detected when assessing the microalgal primary producers (i.e. high biomass and low diversity). Furthermore, the need to distinguish between naturally and anthropogenically induced symptoms was highlighted. One such scenario was noted in the Kaaimans Estuary, where its natural hydro-morphological characteristics (i.e. steep banks, low river inflow, and deep/narrow channel) led to the possible exaggeration of its overall eutrophic condition, i.e. received a ‘Fair’ rather than ‘Good’ rating, arising from ‘Poor’ ratings for dissolved oxygen and benthic diatom diversity. Overall, this study demonstrated the importance of adopting a holistic approach when assessing the condition and trophic status of estuaries. Studies such as these allow for the detection of vulnerable and degraded systems, which can provide important information with regards to the identification of management priorities.
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Tuzun, Ilhami. "Eutrophication and its control by biomanipulation". Thesis, University of Essex, 1993. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.386919.

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Bryhn, Andreas Christoffer. "Quantitative Understanding and Prediction of Lake Eutrophication". Doctoral thesis, Uppsala universitet, Institutionen för geovetenskaper, 2008. http://urn.kb.se/resolve?urn=urn:nbn:se:uu:diva-8593.

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Many lakes around the world have been exposed to increased nutrient input from anthropogenic sources such as sewage discharge and runoff from fertilised agricultural areas. This has led to eutrophication, manifested as intensified algal blooms, murky waters, oxygen depleted lake bottoms, and alterations of considerable parts of the foodweb. However, many of these lakes have also recovered, due to improved nutrient abatement techniques and to an improved quantitative scientific understanding of eutrophication and its causes. General, predictive models have played a crucial role in the latter development, as they have made it possible to quantitatively assess expected ecosystem changes from various planned actions against eutrophication. The present thesis has been aimed at improving the domain of validity and predictive power of a general, dynamic total phosphorus (TP) model (LakeMab) and to provide the basis for constructing a similar model for total nitrogen (TN). Among the findings in the thesis is that dissolved nitrogen gas is probably always available in excess for nitrogen fixation and nitrogen modelling in eutrophication contexts. Two papers have laid the ground for improved nutrient modelling in calcareous lakes, where sedimentation is particularly pronounced. Static models for predicting concentrations of particulate phosphorus, nitrogen, and organic carbon have been presented that may be incorporated into sedimentation algorithms in dynamic nutrient models. Boundary conditions for various flux algorithms have made it possible to greatly expand the domain of LakeMab for TP. The typical uncertainty of TP concentration values is 17% when predicted with LakeMab, whereas the uncertainty in predictions using older, static models is about twice as high. LakeMab may be very useful for resolving practical issues such as predicting climate-induced eutrophication and drawing up operational guidelines for achieving good water quality as prescribed by, e.g., the European Water Framework Directive.
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Wittenberg, Mark. "Effects of eutrophication on juvenile scleractinian corals". Thesis, McGill University, 1991. http://digitool.Library.McGill.CA:80/R/?func=dbin-jump-full&object_id=60552.

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This study investigates effects of eutrophication on settlement, abundance, mortality and community structure of soleractinian corals on fringing reefs on the west coast of Barbados, W.I. Juvenile abundance was lower, but juvenile size larger, on eutrophic than less eutrophic reefs. The lower abundance results at least in part from a higher juvenile mortality on eutrophic reefs. Algae were more abundant and grazers (Diadema antillarum and herbivorous fish) less abundant on eutrophic reefs. Juvenile community structure on all reefs, and adult community structure on eutrophic reefs, was dominated by type 1 corals (high recruitment, high natural mortality). Type 2 corals (low recruitment, low natural mortality) were common in adult communities on less eutrophic reefs. Settlement of coral recruits on artificial substrates was lower on more eutrophic reefs.
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Maier, Gerald. "Nutrients and eutrophication in the Taw estuary". Thesis, University of Plymouth, 2009. http://hdl.handle.net/10026.1/2369.

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Increased inputs of nutrients to estuaries and coastal waters can cause undesirable effects associated with eutrophication, including nuisance and toxic algal blooms, reduced amenity value, changes in species composition, bottom anoxia and fish kills. The main sources of nutrients to estuaries are river runoff, sewage discharges, atmospheric inputs and possibly submarine groundwater discharges. For the UK, estuarine eutrophication has been shown to occur in at least 16 estuaries (including the Taw in North Devon). Consequently, these systems have been designated as '(Potential) Problem Area' under the OSPAR Common Procedure for the Identification of Eutrophication and also as a 'Eutrophic Water' under the EU's Nitrates Directive and I or a 'Sensitive Area (Eutrophic)' under the Urban Wastewater Treatment Directive or both. Significant reductions in N and P inputs have been realized following application of the EU's Urban Waste Water Treatment Directive. Atmospheric NOx and NHx emissions have also decreased and are expected to decrease further as implementation of existing legislation continues and new controls are introduced for activities such as shipping. The Nitrates Directive was introduced to tackle N discharges from agriculture but little change in N loads to estuaries has been recorded. Using the Taw Estuary as an example, data routinely collected by the Environment Agency for England and Wales (EA) over the period 1990-2004 were interrogated to identify the drivers of excessive algal growth. The estuary was highly productive with chlorophyll a concentrations regularly exceeding 100 µg Lˉ¹ , mostly during periods of low freshwater input from the River Taw when estuarine water residence times were longest. The reported approach demonstrates the value of applying conventional statistical analyses in a structured way to existing monitoring data and is recommended as a useful tool for the rapid assessment of estuarine eutrophication. However, understanding of primary production dynamics in the Taw was constrained because of the low temporal resolution, heterogeneity and gaps in the EA data. Therefore, a temporal high resolution monitoring campaign was conducted in summer 2008 to document the development and decline of three algal blooms. The significance of long water residence times following low freshwater inflow and neap tides was confirmed. During peaks in chlorophyll a concentration (max. 226 µg Lˉ¹ ) , nutrient limitation switched from P to Si and persisted for more than 2 weeks in the outer estuary. Signs of ammonium and phosphate ( <0.2 µM) and silicate ( <2 µM) depletion were also observed. Using multivariate statistics, five distinct sets of environmental conditions present in the Taw at different stages of algal growth were identified and directly linked to freshwater inflow. UK Climate Impacts Programme scenarios predict a 30-50% decrease in Q95 flows (the flow which is exceeded 95% of the time) of rivers in south Britain by 2050. Under the current nutrient regime, this is likely to severely increase the severity and duration of symptoms of eutrophication in the Taw and favour potentially hazardous phytoplankton groups instead of diatoms. To mitigate future eutrophication events in the Taw, it is recommended to further reduce N and P inputs. It is also crucial to perform a detailed assessment of potential climate change consequences for the Taw Estuary and similar systems.
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Schneider, Jana. "Biomanipulation for eutrophication control in running waters". Doctoral thesis, Saechsische Landesbibliothek- Staats- und Universitaetsbibliothek Dresden, 2016. http://nbn-resolving.de/urn:nbn:de:bsz:14-qucosa-198843.

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A good ecological status of streams and rivers is crucial for maintaining ecological functionality of running waters. Worldwide eutrophication threatens to change structure and function of freshwater ecosystems (Dodds et al., 2008). To reduce the symptoms of eutrophication in streams and rivers an additional approach, besides the reduction of external nutrient inputs from catchment areas, is needed. Therefore the goal has been set to transfer the approach of biomanipulation, which is widely accepted as tool in water quality management in lakes and reservoirs, to streams. The objective of this study was accordingly to analyse and evaluate some crucial preconditions for top-down control of stream food webs. For that purpose the present thesis examined effects of fish predation (stone loach and gudgeon) on grazer-periphyton interaction in small streams by assessing predator avoidance by benthic grazers, effects of benthic grazers on periphyton community composition during fish presence/absence and the possibility of top-down control on algal biomass by benthivorous fish.
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Książki na temat "Eutrophication"

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Harper, David. Eutrophication of Freshwaters. Dordrecht: Springer Netherlands, 1992. http://dx.doi.org/10.1007/978-94-011-3082-0.

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Hinga, Kenneth R. Marine eutrophication review. Silver Spring, MD: U.S. Dept. of Commerce, National Oceanic and Atmospheric Administration, Coastal Ocean Office, 1995.

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de Jong, Folkert. Marine Eutrophication in Perspective. Berlin, Heidelberg: Springer Berlin Heidelberg, 2006. http://dx.doi.org/10.1007/3-540-33648-6.

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Andersen, J. H., i D. J. Conley, red. Eutrophication in Coastal Ecosystems. Dordrecht: Springer Netherlands, 2009. http://dx.doi.org/10.1007/978-90-481-3385-7.

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Scholten, Martin C. Th, Edwin M. Foekema, Henno P. Van Dokkum, Nicolaas H. B. M. Kaag i Robbert G. Jak. Eutrophication Management and Ecotoxicology. Berlin, Heidelberg: Springer Berlin Heidelberg, 2005. http://dx.doi.org/10.1007/b137902.

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Th, Scholten M. C., red. Eutrophication management and ecotoxicology. Berlin: Springer, 2005.

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Mitchell, P. Lake Wabamun eutrophication study. [Edmonton, Alta.?]: Water Quality Control Branch, Pollution Control Division, Environmental Protection Services, Alberta Environment, 1985.

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Jørgensen, Bo Barker, i Katherine Richardson, red. Eutrophication in Coastal Marine Ecosystems. Washington, D. C.: American Geophysical Union, 1996. http://dx.doi.org/10.1029/ce052.

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Ansari, Abid A., Sarvajeet Singh Gill, Guy R. Lanza i Walter Rast, red. Eutrophication: causes, consequences and control. Dordrecht: Springer Netherlands, 2011. http://dx.doi.org/10.1007/978-90-481-9625-8.

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Håkanson, Lars, i Andreas C. Bryhn. Eutrophication in the Baltic Sea. Berlin, Heidelberg: Springer Berlin Heidelberg, 2008. http://dx.doi.org/10.1007/978-3-540-70909-1.

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Części książek na temat "Eutrophication"

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Butusov, Mikhail, i Arne Jernelöv. "Eutrophication". W SpringerBriefs in Environmental Science, 57–68. New York, NY: Springer New York, 2013. http://dx.doi.org/10.1007/978-1-4614-6803-5_7.

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Ellis, K. V., G. White i A. E. Warn. "Eutrophication". W Surface Water Pollution and its Control, 219–34. London: Macmillan Education UK, 1989. http://dx.doi.org/10.1007/978-1-349-09071-6_9.

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Henderson, Andrew D. "Eutrophication". W Life Cycle Impact Assessment, 177–96. Dordrecht: Springer Netherlands, 2015. http://dx.doi.org/10.1007/978-94-017-9744-3_10.

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Boyd, Claude E. "Eutrophication". W Water Quality, 311–22. Cham: Springer International Publishing, 2019. http://dx.doi.org/10.1007/978-3-030-23335-8_15.

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Kennish, Michael J. "Eutrophication". W Encyclopedia of Estuaries, 304–11. Dordrecht: Springer Netherlands, 2015. http://dx.doi.org/10.1007/978-94-017-8801-4_2.

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Hoagland, Kyle D., i Thomas G. Franti. "Eutrophication". W Fresh Water and Watersheds, 45–48. Second edition. | Boca Raton: CRC Press, [2020] | Revised edition of: Encyclopedia of natural resources. [2014].: CRC Press, 2020. http://dx.doi.org/10.1201/9780429441042-7.

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Hudon, Christiane. "Eutrophication". W Encyclopedia of Aquatic Ecotoxicology, 491–98. Dordrecht: Springer Netherlands, 2013. http://dx.doi.org/10.1007/978-94-007-5704-2_46.

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Jin, Haiyan, Dewang Li i Zhenming Zheng. "Eutrophication". W Encyclopedia of Ocean Engineering, 477–80. Singapore: Springer Nature Singapore, 2022. http://dx.doi.org/10.1007/978-981-10-6946-8_312.

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Jin, Haiyan, Dewang Li i Zhenming Zheng. "Eutrophication". W Encyclopedia of Ocean Engineering, 1–4. Singapore: Springer Singapore, 2021. http://dx.doi.org/10.1007/978-981-10-6963-5_312-1.

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van Beusekom, Justus E. E. "Eutrophication". W Handbook on Marine Environment Protection, 429–45. Cham: Springer International Publishing, 2017. http://dx.doi.org/10.1007/978-3-319-60156-4_22.

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Streszczenia konferencji na temat "Eutrophication"

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Asfandiyarova, L. R., I. V. Ovsyannikova, Z. M. Kuramshina i G. V. Khakimova. "ANALYSIS OF GREENHOUSE GAS EMISSIONS FROM A RESERVOIR SURFACE". W INNOVATIVE TECHNOLOGIES IN SCIENCE AND EDUCATION. ООО «ДГТУ-Принт» Адрес полиграфического предприятия: 344003, г. Ростов-на-Дону, пл. Гагарина,1., 2023. http://dx.doi.org/10.23947/itse.2023.39-42.

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The article studies the relationship between greenhouse gas emissions and the level of eutrophication and toxicity of a water body by monitoring the spatio-temporal level of eutrophication of surface waters of the Pavlovsk reservoir, and determines the eutrophication coefficient, which takes into account the combined effect of eutrophication and toxication. Mathematical processing of data on the content of climatically active gases obtained from field measurements was carried out.
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Qin, Wang, Xu Zong-xue, Jiang Xia i Gao Ji-xi. "Eutrophication in the Yuyuantan Lake". W 2011 International Conference on Computer Distributed Control and Intelligent Environmental Monitoring (CDCIEM). IEEE, 2011. http://dx.doi.org/10.1109/cdciem.2011.318.

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P. L. Barnes. "Kansas Lake Eutrophication TMDL Program". W 2005 Tampa, FL July 17-20, 2005. St. Joseph, MI: American Society of Agricultural and Biological Engineers, 2005. http://dx.doi.org/10.13031/2013.18945.

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Shadwell, Keana, Aubry Sapp, Joe Ogsbury i Robin Young. "Session 2.3 How Red Tide in Florida indicates global eutrophication problems and how we can fix them". W The 4th Global Virtual Conference of the Youth Environmental Alliance in Higher Education. Michigan Technological University, 2022. http://dx.doi.org/10.37099/mtu.dc.yeah-conference/dec2021/all-events/12.

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This project focuses on the UN’s SDG14: Life Below Water, target 14.1. Eutrophication is a big problem to ecosystems and communities, as it kills wildlife, creates imbalances in the trophic system, and degrades water quality. The Red Tide in Florida is an important example of pollution-caused eutrophication that is indicative of eutrophication problems globally. Luckily, there are solutions that we can work together to implement on a nationwide and international level, including policy change to regulate agriculture monitoring algal bloom, finding alternatives for fertilizers, and funding research. SDG Theme: SDG 14 – Life below water Type: E-poster
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Lewandowski, Joerg, Karin Meinikmann, Gunnar Nutzmann i Donald O. Rosenberry. "LACUSTRINE AND SUBMARINE GROUNDWATER DISCHARGE FUEL EUTROPHICATION". W GSA Annual Meeting in Denver, Colorado, USA - 2016. Geological Society of America, 2016. http://dx.doi.org/10.1130/abs/2016am-276558.

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Pin, Desmond Chan Min, Xinxin Guo, Ke Wang, Lee-Muei Chng, Lai-Peng Wong i Xingmin Zhao. "Assessment of water eutrophication in Kampar, Malaysia". W INTERNATIONAL SYMPOSIUM ON GREEN AND SUSTAINABLE TECHNOLOGY (ISGST2019). AIP Publishing, 2019. http://dx.doi.org/10.1063/1.5126557.

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AGAFITEI, Alina. "CONTROLLING THE PROCESS OF EUTROPHICATION IN LAKES". W 19th SGEM International Multidisciplinary Scientific GeoConference EXPO Proceedings. STEF92 Technology, 2019. http://dx.doi.org/10.5593/sgem2019/3.1/s12.014.

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Ai, Jiaoyan, Haiyang Xu, Yajuan Cai, Sizhi Wu i Zengqiang Lei. "Prediction Analysis of Artificial Landscape Water Eutrophication". W 2016 International Conference on Education, Sports, Arts and Management Engineering. Paris, France: Atlantis Press, 2016. http://dx.doi.org/10.2991/icesame-16.2016.230.

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Newton, J., A. Devol i W. Ruef. "Measuring nitrate fluxes to assess estuarine eutrophication". W OCEANS 2009. IEEE, 2009. http://dx.doi.org/10.23919/oceans.2009.5422345.

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Shiva Kumar, G., P. Lakshmi Sruthi, P. Rajasekhar i Feza Karaer. "Eutrophication assessment of a shallow lake using GIS". W 2014 International Conference on Computer and Communications Technologies (ICCCT). IEEE, 2014. http://dx.doi.org/10.1109/iccct2.2014.7066701.

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Raporty organizacyjne na temat "Eutrophication"

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Martinez-Guerra, Edith, Luke Gurtowski i Carina Jung. Eutrophication management via iron-phosphorus binding. Engineer Research and Development Center (U.S.), wrzesień 2020. http://dx.doi.org/10.21079/11681/38260.

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Cerco, Carl F., Mark R. Noel i Sung-Chan Kim. Three-Dimensional Eutrophication Model of Lake Washington, Washington State. Fort Belvoir, VA: Defense Technical Information Center, sierpień 2004. http://dx.doi.org/10.21236/ada427041.

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Doncheva, Valentina, Ognyana Hristova i Boryana Dzhurova. Thresholds for Eutrophication Indicators in the Bulgarian Black Sea Coastal Zone. "Prof. Marin Drinov" Publishing House of Bulgarian Academy of Sciences, lipiec 2019. http://dx.doi.org/10.7546/crabs.2019.07.05.

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Cerco, Carl F. Combining the ICM Eutrophication Model with the SEDZLJ Sediment Transport Model. Fort Belvoir, VA: Defense Technical Information Center, sierpień 2012. http://dx.doi.org/10.21236/ada572122.

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Whitledge, T. E. Nationwide review of oxygen depletion and eutrophication in estuarine and coastal waters: Executive summary. Office of Scientific and Technical Information (OSTI), wrzesień 1985. http://dx.doi.org/10.2172/6157099.

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Dagget, Steven. Evidence for the Eutrophication of Selected Coastal Dunal Lakes: Historical Comparison of Indices for Nutrient Enrichment. Portland State University Library, styczeń 2000. http://dx.doi.org/10.15760/etd.6607.

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Lips, Urmas, Oliver Samlas, Stella-Theresa Stoicescu, Vasily Korabel i Jun She. Assessment of the benefits of the BOOS-HELCOM integrated system and recommendations for transfer this to other sea areas. EuroSea, 2023. http://dx.doi.org/10.3289/eurosea_d6.6.

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This report summarises demonstrated benefit from integrating BOOS and HELCOM observations with CMEMS observations, including i) improved observation data accessibility by BOOS, CMEMS INSTAC and EMODnet, ii) improved quality of frequently updated CMEMS reanalysis, and iii) improved quality and update frequency of eutrophication assessment in the Baltic Sea based on the reanalysis. Also, feasibility for extending this approach to other regional seas, other indicators, and fishery advice applications is analysed and recommendations from the workshop on “Full value chain integration for monitoring and assessment” are provided. (EuroSea Deliverable, D6.6)
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Tillman, Dorothy H., i Carl F. Cerco. Recreating the 1950's Chesapeake Bay: Use of a Network Model to Guide the Application of a Eutrophication Model. Fort Belvoir, VA: Defense Technical Information Center, sierpień 2009. http://dx.doi.org/10.21236/ada508342.

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Schmidt, Mark. Dynamics and variability of POC burial in depocenters of the North Sea (Skagerrak), Cruise No. AL561, 2.08.2021 – 13.08.2021, Kiel – Kiel, APOC. GEOMAR Helmholtz Centre for Ocean Research Kiel, 2021. http://dx.doi.org/10.3289/cr_al561.

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The AL561 cruise was conducted in the framework of the project APOC (“Anthropogenic impacts on Particulate Organic Carbon cycling in the North Sea”). This collaborative project between GEOMAR, AWI, HEREON, UHH, and BUND is to understand how particulate organic carbon (POC) cycling contributes to carbon sequestration in the North Sea and how this ecosystem service is compromised and interlinked with global change and a range of human pressures include fisheries (pelagic fisheries, bottom trawling), resource extraction (sand mining), sediment management (dredging and disposal of dredged sediments) and eutrophication. The main aim of the sampling activity during AL561 cruise was to recover undisturbed sediment from high accumulation sites in the Skagerrak/Kattegat and to subsample sediment/porewater at high resolution in order to investigate sedimentation transport processes, origin of sediment/POC and mineralization processes over the last 100- 200 years. Moreover, the actual processes of sedimentation and POC degradation in the water column and benthic layer will be addressed by sampling with CTD and Lander devices. In total 9 hydroacoustic surveys (59 profiles), 4 Gravity Corer, 7 Multicorer, 3 Lander and 4 CTD stations were successfully conducted during the AL561 cruise. - (Alkor-Berichte ; AL561)
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Mitchell, Brian G., Amir Neori, Charles Yarish, D. Allen Davis, Tzachi Samocha i Lior Guttman. The use of aquaculture effluents in spray culture for the production of high protein macroalgae for shrimp aqua-feeds. United States Department of Agriculture, styczeń 2013. http://dx.doi.org/10.32747/2013.7597934.bard.

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The FAO has projected a doubling in world demand for seafood during the 21 ed from aquaculture of marine fish and shrimps fed primarily on fishmeal-based aquafeeds. However, current practices of high intensity monoculture of shrimp in coastal ponds and fish in offshore pens have been strongly criticized as being ecologically and socially unsustainable. This view derives from un- checked eutrophication of coastal marine ecosystems from fish farm effluents, and the destruction of coastal estuarine ecosystems by shrimp farm constructions, plus aquaculture’s reliance on wild-caught small fish - which are excellent food for humans, but instead are rendered into fishmeal and fish oil for formulating aquafeeds. Fishmeal-sparing and waste- reduction aquafeeds can only delay the time when fed aquaculture product are priced out of affordability for most consumers. Additionally, replacement of fishmeal protein and fish oil by terrestrial plant sources such as soybean meal and oil directly raises food costs for human communities in developing nations. New formulations incorporating sustainably-produced marine algal proteins and oils are growing in acceptance as viable and practical alternatives. This BARD collaborative research project investigated a sustainable water-sparing spray/drip culture method for producing high-protein marine macrophyte meals for incorporation into marine shrimp and fish diets. The spray culture work was conducted at laboratory-scale in the USA (UCSD-SIO) using selected Gracilariaand Ulvastrains isolated and supplied by UCONN, and outdoors at pilot-scale in Israel (IOLR-NCM) using local strains of Ulvasp., and nitrogen/phosphorus-enriched fish farm effluent to fertilize the spray cultures and produce seaweed biomass and meals containing up to 27% raw protein (dry weight content). Auburn University (USA) in consultation with TAMUS (USA) used the IOLR meals to formulate diets and conduct marine shrimp feeding trials, which resulted in mixed outcomes, indicating further work was needed to chemically identify and remove anti-nutritional elements present in the IOLR-produced seaweed meals.
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