Relevant bibliographies by topics / Periphyton

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  1. Journal articles
  2. Dissertations / Theses
  3. Books
  4. Book chapters
  5. Conference papers
  6. Reports

Academic literature on the topic 'Periphyton'

Author: Grafiati
Published: 4 June 2021
Last updated: 29 July 2024

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Journal articles on the topic "Periphyton"

1

Saikia, SK, and DN Das. "Diversity and productivity (Chlorophyll-a and Biomass) of periphyton on natural and artificial substrates from wetland ecosystem." Journal of Wetlands Ecology 5 (December 28, 2011): 1–9. http://dx.doi.org/10.3126/jowe.v5i0.4624.

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Periphyton from rice-fish environment of Apatani Plateau, Arunachal Pradesh, India was studied for diversity and productivity (Chlorophyll-a and biomass) on artificial (glass slide) and natural (rice stem) substrates. Periphyton from rice stems, especially, from cultivars locally known as ‘Amo’ were collected from a depth of 7.0-8.0 cm from surface water and 5.0 cm above from the field bottom. Glass slides (15 × 18cm) were fitted in periphyton sampler and fixed at different depths. The rice fish environment was found to harbor rich periphytic diversity throughout the whole cropping season of 2002 and 2003. Total 88 genera of periphytic microalgae were reported from the environment with an order of preference of Chlorophyceae>Bacillariophyceae>Cyanophyceae. The Shannon Wienner diversity (H´) and evenness (J) indices of periphyton from rice stems indicated tendencies of Chlorophycea and Cyanophyceae to exhibit periphytic life on rice stems, whereas Bacillariophyceae preferred glass slide. Dry matter (DM) and Ash free dry matter (AFDM) values reflected the affinity of non algal periphytic resource to associate on both rice stems and glass slide. The results of periphytic Chl-a from rice stem was significantly higher to glass slides and show selectivity of algal periphytic resource to colonize on rice stem. Its sudden decline during late aquatic phase on rice stem explains heterotrophic nature of rice fish environment. The rice stems as natural substrate, thus, exhibited a rich ground for periphyton growth in rice fields of Apatani Plateau. It also stands as potential candidate to be used as a source for organic nutrients in the form of periphyton for aquaculture. Key words: Apatani plateau; Rice-fish; Common carp; Periphyton; Rice stemDOI: http://dx.doi.org/10.3126/jowe.v5i0.4624 J Wet Eco 2011 (5): 1-9
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Anishchenko, Olesya, Michail Gladyshev, Elena Kravchuk, Elena Ivanova, Iliada Gribovskaya, and Nadezhda Sushchik. "Seasonal variations of metal concentrations in periphyton and taxonomic composition of the algal community at a Yenisei River littoral site." Open Life Sciences 5, no. 1 (February 1, 2010): 125–34. http://dx.doi.org/10.2478/s11535-009-0060-y.

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AbstractThe concentrations of metals K, Na, Ca, Mg, Fe, Mn, Zn, Cu, Ni, Pb, Co and Cr, in the water and periphyton (epilithic algal communities) were studied at a site in the middle stream of the Yenisei River (Siberia, Russia) during three years using monthly sampling frequencies. Despite considerable seasonal variations in aquatic concentrations of some metals, there was no correlation between metal contents in the water and in periphyton. Seasonal concentration variations of some metals in periphyton were related to the species (taxonomic) composition of periphytic microalgae and cyanobacteria. Enhanced levels of Ni and Co in periphyton in late autumn, winter, and early spring were likely caused by the predominance of cyanobacteria in the periphytic community, and annual maximum levels of K in periphyton in late spring and early summer were attributed to the domination of Chlorophyta, primarily Ulothrix zonata.
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Souza, Mariane Lima de, and Carla Ferragut. "Influence of substratum surface roughness on periphytic algal community structure in a shallow tropical reservoir." Acta Limnologica Brasiliensia 24, no. 4 (April 12, 2013): 397–407. http://dx.doi.org/10.1590/s2179-975x2013005000004.

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AIM: This study aimed to evaluate the algal periphytic community structure on substrates with differing surface roughness in early and longer-term colonization; METHODS: Periphyton was sampled after 30 days (June 24 to July 24, 2008) and 5 days (July 07 to July 12, 2010) substrate exposure during dry season. Plastic slides were used as artificial substrate. Treatments were smooth surface (control), low roughness, medium roughness and high roughness. Samples were collected for limnological condition and periphyton (chlorophyll-a, AFDM, algal biovolume and density, species richness and diversity) analysis; RESULTS: Periphytic biomass, algal density and biovolume had no significant difference among treatments after 30 and 5 days colonization time. Taxonomic similarity was the lowest among treatments and the greatest difference occurred between control and treatments with roughness surface. Bacillariophyceae biovolume decreased with increasing surface roughness. Adherence forms, algal classes and species descriptors were significantly different after 5 days colonization time, especially in medium e high roughness surface. In the colonization advanced phase only species descriptors differ among treatments. Periphytic algae with pads and stalks for adherence decreased with increasing surface roughness. CONCLUSION: Substrate physical properties had little or no influence on periphyton biomass accumulation, total density and biovolume in this study, but algal assemblages were sensitive to changes in the microtopography. More studies are needed to increase understanding of the relation substrate-periphyton in tropical ecosystems.
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Tonkin, Jonathan D., Russell G. Death, and José Barquín. "Periphyton control on stream invertebrate diversity: is periphyton architecture more important than biomass?" Marine and Freshwater Research 65, no. 9 (2014): 818. http://dx.doi.org/10.1071/mf13271.

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There is little consensus on the form of the periphyton biomass–macroinvertebrate diversity relationship in streams. One factor that these relationships do not account for is the growth form of primary producers. We (1) examined the periphyton biomass–macroinvertebrate diversity relationship in 24 streams of Cantabria, Spain, in July 2007, and (2) determined whether this relationship was underpinned, and better explained, by specific responses to the growth form of the periphyton community. We hypothesised that macroinvertebrate diversity would be a log-linear function of periphyton biomass and would respond differently to two coarse divisions of the periphytic community; i.e. positively to %cover of non-filamentous algae and negatively to %cover of streaming filamentous algae. There was no relationship between benthic periphyton biomass and macroinvertebrate diversity in these streams but, as predicted, this relationship was underpinned by responses to the growth form of periphyton community. Generally, macroinvertebrate diversity responded positively to %cover of non-filaments and negatively to %cover of streaming filaments, although results were variable. These findings suggest that periphyton biomass–macroinvertebrate diversity relationships in streams can be underpinned by interactions with specific growth forms of periphyton. We suggest that further research is required to develop robust thresholds of %cover of filamentous algae cover that would benefit managers wishing to minimise negative effects of eutrophication on stream communities.
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Lakatos, Gyula, Ildikó Mátrai, János Kundrát, and István Gyulai. "The Mass Ratio of the Epiphytic Periphyton of the Nyéki-Holt-Duna." Landscape & Environment 10, no. 3-4 (September 19, 2016): 232–41. http://dx.doi.org/10.21120/le/10/3-4/17.

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The knowledge of the periphytic structure is important for the fact that the composition of epiphytic periphyton indicates the ecologically different habitats, the biological state of water-quality and its changes. Plants like reed, great bulrush, saligot, pondweed, and water-rose separately were collected from the different sampling sites for the epiphytic periphyton examination. We performed the comparability of the monitoring systems based on the periphyton category (mass), the group (ash%), the type (chl-a%), and the character (AI), and we used the biological indicators to determine the ecological state. Taking into consideration the examined years and the results of the analysis of the mass and the chemical composition of the periphyton, by means of the NTPI, the overweight of the good ecological state is characteristic of the Nyéki-Holt-Danube.
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Andreeva, N. A. "Monitoring the composition of periphyton and epiliton cyanobacteria in the coastal shallow water (Black Sea, Sevastopol)." Monitoring systems of environment, no. 1 (March 28, 2022): 74–80. http://dx.doi.org/10.33075/2220-5861-2022-1-74-80.

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During 2017–2021 a study of the composition of periphytic cyanobacteria in the coastal waters of the bays of Sevastopol was carried out. The composition of cyanobacteria in the periphyton and epilithon varied over the years in the range of 4–7 and 2–8 forms, respectively. Over the entire period, 16 system-atic units have been identified, which are representatives of 7 orders: Chroococcales, Chroococcidiop-sidales, Synechococcales, Pleurocapsales, Oscillatoriales, Nostocales and Stigonematales. The absolute dominants in the periphyton of the glasses were cyanobacteria of the order Oscillatoriales, and oscillatory and Pleurocapsa in the epilithon. 11 strains of cyanobacteria have breen isolated from periphyton and epilithon.
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Fernandes, V. O., and F. A. Esteves. "The use of indices for evaluating the periphytic community in two kinds of substrate in Imboassica Lagoon, Rio de Janeiro, Brazil." Brazilian Journal of Biology 63, no. 2 (May 2003): 233–43. http://dx.doi.org/10.1590/s1519-69842003000200008.

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Biological indices based on the biomass (dry weight, ash content, and chlorophyll-a) of the periphyton in a natural (submersed leaves of Typha domingensis Pers) and in an artificial (plastic hoses) substrate were compared, in experiments performed in summer and winter, in two sampling stations of Imboassica Lagoon, Macaé, Rio de Janeiro. The periphytic community exhibited low biomass at the beginning and end of the experiments, and moderate biomass in the intermediate period of the experiment, whatever the kind of substrate, sampling station, and season. In both seasons, there was a spatial variation regarding the degree of trophy of the periphyton, due to the difference of nutrient availability among the sampling stations. The alternation of inorganic and organic periphyton, as well as of their heterotrophic, hetero-autotrophic, auto-heterotrophic and, autotrophic character was due to changes in the abiotic factors of the sampling periods. The Lakatos index proved more sensitive than the Autotrophic Index to variations in the composition of the periphytic community.
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Saikia, S. K., and D. N. Das. "Potentiality of Periphyton-based Aquaculture Technology in Rice-fish Environment." Journal of Scientific Research 1, no. 3 (August 29, 2009): 624–34. http://dx.doi.org/10.3329/jsr.v1i3.2114.

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Periphyton is being used traditionally as rich aquatic feed for fishes throughout the countries like Cambodia, West Africa, Srilanka, India and Bangladesh. In waterlogged rice environment, it can be judiciously utilized as feed source introducing periphytophagous fish. Studies supported rice straw as suitable substrate for periphyton growth. The study of gut content of Common carp (Cyprinus carpio L.) from a periphyton-based rice-fish culture system in Apatani Plateau of Arunachal Pradesh, India showed maximum of 60 genera of microflora and fauna with periphytic in nature. The farmers from this rice-fish culture practice are gaining an average fish production of 500kg ha-1 180 day-1 without employing any supplementary feed. Better selection and determination of appropriate stocking density of periphytophagous fish in waterlogged rice-fields might extend the rice-fish culture towards a sustainable and self-substrating periphyton based aquaculture (SSPBA) practice. Keywords: Periphyton; Sustainable agriculture; Rice-fish; Self-substrating; Common carp; Apatani plateau. © 2009 JSR Publications. ISSN: 2070-0237 (Print); 2070-0245 (Online). All rights reserved. DOI: 10.3329/jsr.v1i3.2114 J. Sci. Res. 1 (3), 624-634 (2009)
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Bari, M. A., M. I. Hossain, and M. A. J. Miah. "Synthesis of Acryclic Acid Ethyl Ester from Aldehydes Catalyzed by Copper Triflates." Journal of Scientific Research 1, no. 3 (August 29, 2009): 635–40. http://dx.doi.org/10.3329/jsr.v1i3.2473.

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Periphyton is being used traditionally as rich aquatic feed for fishes throughout the countries like Cambodia, West Africa, Srilanka, India and Bangladesh. In waterlogged rice environment, it can be judiciously utilized as feed source introducing periphytophagous fish. Studies supported rice straw as suitable substrate for periphyton growth. The study of gut content of Common carp (Cyprinus carpio L.) from a periphyton-based rice-fish culture system in Apatani Plateau of Arunachal Pradesh, India showed maximum of 60 genera of microflora and fauna with periphytic in nature. The farmers from this rice-fish culture practice are gaining an average fish production of 500kg ha-1 180 day-1 without employing any supplementary feed. Better selection and determination of appropriate stocking density of periphytophagous fish in waterlogged rice-fields might extend the rice-fish culture towards a sustainable and self-substrating periphyton based aquaculture (SSPBA) practice. Keywords: Periphyton; Sustainable agriculture; Rice-fish; Self-substrating; Common carp; Apatani plateau. © 2009 JSR Publications. ISSN: 2070-0237 (Print); 2070-0245 (Online). All rights reserved. DOI: 10.3329/jsr.v1i3.2114 J. Sci. Res. 1 (3), 624-634 (2009)
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Santhiya, A. Anix Vivek, S. Athithan, B. Ahilan, J. Stephen, Sampath Kumar, and A. Srinivasan. "Evaluation of periphyton quantity on different natural substrates in Earthen lined pond." Journal of Applied and Natural Science 9, no. 3 (September 1, 2017): 1630–36. http://dx.doi.org/10.31018/jans.v9i3.1413.

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Experiments were conducted in outdoor earthen lined pond to study periphyton quantity on three types of natural substrates such as split bamboo pole, coconut coir and coconut shell, which was placed inside the earthen lined pond filled with seawater for duration of 45 days. Observations were made in every 15th day for growth of periphyton both qualitatively and quantitatively on the three natural substrates and physico-chemical properties of selected pond water such as transparency, water temperature, salinity, pH, Dissolved oxygen, Ammonia (NH3-N), Nitrite (NO2-N), Nitrate (NO3-N), BOD and Chlorophyll ‘a’ were recorded during periphyton samplings. The periphy-ton quantity (34562 ± 671 cells / cm2) observed for coconut coir was higher than the split bamboo pole (33104 ± 810 cells / cm2), and coconut shell (21194 ± 872 cells / cm2) in the final day of the experiment. One way ANOVA of the data collected clearly affirmed that significant differences were observed (P < 0.05) in periphyton quantity among the three substrates tested. A total 16 phyto-periphytic microalgae (Bacillariophyceae – 10 types, Dinophyceae – 4 types and Cyanophyceae – 2 types) and 10 Zoo-periphyton (Copepod- 4 types, Meroplankton – 4 types and Tintin-nidae – 2 types) were recorded from these three substrates. Among the different phyto-periphytic microalgae, Bacil-lariophyceae group were found to be more (Split bamboo pole – 72%, Coconut coir – 73% and Coconut shell – 71%) on three substrates studied. Further, coconut coir was found to be best substrate than split bamboo pole and coconut shell, which can be utilized by fin and shellfishes as natural food.
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Dissertations / Theses on the topic "Periphyton"

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Carr, Genevieve Margaret. "Prediction of periphyton in rivers." Thesis, University of Ottawa (Canada), 2004. http://hdl.handle.net/10393/29083.

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Periphyton communities are often the dominant primary producers and an important energy source to higher trophic levels in rivers and streams. Empirical models of periphyton biomass (chlorophyll a) that have high predictive power are generally lacking. The goal of this research was to assess and improve the predictability of periphyton in rivers. A historical river monitoring data set from Alberta showed that, in general, land use in the drainage basin was a good surrogate for instream nutrient concentrations in regression models of periphyton biomass. Land use explained up to 34% of the variability in chlorophyll a whereas models based on instream nutrients explained up to 24% of the variability in chlorophyll a . A field study showed that bacterial abundance in periphyton explained an additional 26 to 29% of residual variance of chlorophyll a, after taking nutrients into account. The relationships between algal and bacterial abundance and production estimates were positive, suggesting bacteria and algae coexist in a mutually dependent association. The sampling design for bacteria in the field study was based on the relationships between sample means and variances of published bacterial abundance and production data. The number of replicates needed to sample periphytic bacterial abundance and production was determined from these relationships. A meta-analysis of published periphyton regression models was used to evaluate model predictive power. Once corrected for the number of observations, terms, and sampling replicates in the models, predictive power of periphyton models has not improved over the last 30 years. Geographic extent of the study area and the type of predictor variables used also had almost no effect on predictive power. The theoretical limit of model precision has approximately been reached for models predicting temporally averaged periphyton biomass. In contrast, residual variances of models predicting instantaneous mean chlorophyll a were, on average, 4.5 times higher than theoretical pure error. Precision of temporal mean models will only be improved by obtaining more precise estimates of mean chlorophyll a. Models that predict instantaneous chlorophyll a may be made more precise by including variables that better reflect the recent site history.
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Filiz, Nur. "Impacts Of Nutrients On Periphyton Growth And Periphyton-macroinvertebrates Interactions In Shallow Lakes: A Mesocosm Experiment." Master's thesis, METU, 2012. http://etd.lib.metu.edu.tr/upload/12614911/index.pdf.

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Periphyton biomass on artificial strips was observed monthly to see the impacts of nutrient differences on periphyton and periphyton-macroinvertebrates interaction. The experiment was conducted for four months in a mesocosm which were runned at six countries at the same time and with the same steps. Eight enclosures at two meters depth were used that four of them had high nutrient level and the other four had low nutrient level. Sediment, macrophyte, fish, plankton, benthic invertebrates and water were added at the same time and with the same way in all of the countries. Periphyton growth which formed on artificial 32 cm2 strips for June, July, August and September were brushed to filtered mesocosm water and dry mass, ash free dry mass, phosphorus content and chlorophyl-a concentrations were measured. Grazer pressure on the periphyton was observed with a laboratory experiment for July, August and September months. At the end of the mesocosm experiment macrophytes and fish were harvested. Macrophytes&rsquo
dry mass and fish&rsquo
abundance were measured. Moreover at the end of the experiment epiphyton was also measured. Three kajak cores were taken from sediment for macroinvertebrates at the end of the experiment and identified. All physical features of mesocosm enclosures and PVI data were recorded for every 2 weeks. Periphyton biomass was higher concentrations in HN enclosures than LN tanks. Only dry mass of periphyton biomass showed the opposite because of the marl deposition in LN tanks. This finding was also reinforced by epiphyton samples which was taken at the end of the experiment. LN enclosures had the more abundance of macroinvertebrate. The groups we found in sediment which had big grazer effect on periphyton such as gastropods and Chironomidae. Grazer experiment showed that grazer effect on periphyton increased in time. Although this raise, periphyton growth also increased in LN enclosures with nutrient increasing. This may be indicate that nutrient effect has a stronger effect than grazer pressure on periphyton. As it is explained before in the beginning of the experiment all of the conditions were the same except nutrient level. Thus, bottom-up effect changed the top-down control and at the end of the experiment we saw the more periphyton less macroinvertebrate and more fish in HN tanks while the opposite was seen in LN tanks.
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Hayward, Shirley. "Periphyton growth in the Waipara River, North Canterbury." Thesis, University of Canterbury. Environmental Science, 2003. http://hdl.handle.net/10092/1315.

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Periphyton was monitored monthly at four sites on the Waipara River from July 1999 to January 2002. Interactions with river flows, nutrients and invertebrates were examined to determine how these factors controlled periphyton development. Comparison of the Waipara River to other New Zealand streams indicated that periphyton biomass at the uppermost site (Site 1) was generally low to moderate. Further downstream, moderate to high biomass occurred at sites 2 and 4. Biomass at Site 3 was generally low, although some very high values occurred on occasions. Periphyton biomass at sites 2 and 4 exceeded periphyton guidelines for the protection of aesthetic/recreational values at least once during each full year monitored. In contrast, the guidelines were rarely exceeded at Site 1. Dissolved inorganic nutrients were generally poor indicators of the nutrient status of the river because of plant uptake. Cellular N and P values indicated nutrient enrichment at sites 2 and 4, which correspondingly had the highest biomass values. Conductivity tended to positively correlate with temporal and spatial patterns in periphyton biomass and was useful as a surrogate indicator of nutrient supply regimes. It correlated negatively with river flows, indicating higher nutrient concentrations may occur during reduced flows. Notable differences occurred in biomass development between periods of contrasting flow regimes. In particular, annual mean and maximum biomass at the three downstream sites was considerably higher during a period of low stable flows compared to a period of higher base flows. However, at the uppermost site, differences in biomass between these periods were much less pronounced. Invertebrate densities increased significantly with increasing periphyton biomass at the three downstream sites. There was little indication that invertebrates had any major control on periphyton biomass at these sites. However, at the uppermost site, although the invertebrate densities were generally much lower than at the other sites, they are more likely to have a controlling influence on periphyton biomass. Overall, the nutrient supply regime of the Waipara River is the primary controller on biomass development. Flow regimes (both frequency of disturbance and extent of low flows) operate as secondary controls of biomass.
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Stone, Mark Charles. "Natural stream flow fields measurements and implications for periphyton /." Online access for everyone, 2005. http://www.dissertations.wsu.edu/Dissertations/Spring2005/m%5Fstone%5F042705.pdf.

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Scott, J. Thad Doyle Robert D. "Periphyton-nutrient dynamics in a gradient-dominated freshwater marsh ecosystem." Waco, Tex. : Baylor University, 2006. http://hdl.handle.net/2104/5036.

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Davis, Clinton J. "Periphyton dynamics and environmental associations Truckee River, CA-NV, USA /." abstract and full text PDF (free order & download UNR users only), 2007. http://0-gateway.proquest.com.innopac.library.unr.edu/openurl?url_ver=Z39.88-2004&rft_val_fmt=info:ofi/fmt:kev:mtx:dissertation&res_dat=xri:pqdiss&rft_dat=xri:pqdiss:1447636.

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Bessom, Stephanie Marie. "Availability and Toxicity of Nickel to Lotic Periphyton and Macroinvertebrates." Wright State University / OhioLINK, 2008. http://rave.ohiolink.edu/etdc/view?acc_num=wright1229483842.

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Hollingsworth, Emily K. "The Spatial Heterogeneity of Periphyton in Eight Southeastern Ohio Streams: How Far Can One Sample Take You?" Ohio : Ohio University, 2007. http://www.ohiolink.edu/etd/view.cgi?ohiou1181835600.

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Jasrotia, Puja. "Characterization of nitrogenase gene distribution and activity in WCA-2A periphyton." [Gainesville, Fla.] : University of Florida, 2005. http://purl.fcla.edu/fcla/etd/UFE0011864.

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Simmons-Ferguson, Heather Elizabeth. "Total and organic mercury in periphyton from a Precambrian shield lake." Thesis, National Library of Canada = Bibliothèque nationale du Canada, 1997. http://www.collectionscanada.ca/obj/s4/f2/dsk3/ftp04/mq21700.pdf.

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Books on the topic "Periphyton"

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Sharapova, T. A. Zooperifiton vnutrennikh vodoemov Zapadnoĭ Sibiri. Novosibirsk: Nauka, 2007.

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Protasov, A. A. Presnovodnyĭ perifiton. Kiev: Nauk. dumka, 1994.

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Azim, M. E., M. C. J. Verdegem, A. A. van Dam, and M. C. M. Beveridge, eds. Periphyton: ecology, exploitation and management. Wallingford: CABI, 2005. http://dx.doi.org/10.1079/9780851990965.0000.

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1970-, Azim M. E., ed. Periphyton: Ecology, exploitation, and management. Wallingford, Oxfordshire, UK: CABI Pub., 2005.

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Bahls, Loren L. Periphyton bioassessment methods for Montana streams. Helena, Mont: Water Quality Bureau, Dept. of Health and Environmental Sciences, 1993.

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Limited, Boojum Reserach. Periphyton growth studies at South Bay. Toronto, Ont: Boojum Research, 1991.

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Skalʹska︠i︡a, I. A. Зооперифитон водоемов бассейна Верхней Волги. Rybinsk: In-t biologii vnutrennikh vod, 2002.

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Weber, Erich E. An assessment of biological integrity and impairment of aquatic life in the Clark Fork River and its major tributaries based on the structure and composition of algae associations in the periphyton community during August 1993. Helena]: The Dept.?, 1995.

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Weber, Erich E. An assessment of water quality in the Clark Fork River and its major tributaries, based on the structure and composition of summer algae associations in the periphyton community. Helena]: The Dept.?, 1991.

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Weber, Erich E. An assessment of biological integrity and impairment of aquatic life in the Clark Fork River and its major tributaries based on the structure and composition of algae associations in the periphyton community during August 1994. Helena]: The Dept.?, 1996.

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Book chapters on the topic "Periphyton"

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Putz, Rainer, and Wolfgang J. Junk. "Phytoplankton and Periphyton." In Ecological Studies, 207–22. Berlin, Heidelberg: Springer Berlin Heidelberg, 1997. http://dx.doi.org/10.1007/978-3-662-03416-3_10.

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Vermaat, J. E. "Periphyton removal by freshwater micrograzers." In Lake Veluwe, a Macrophyte-dominated System under Eutrophication Stress, 213–49. Dordrecht: Springer Netherlands, 1994. http://dx.doi.org/10.1007/978-94-011-2032-6_13.

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Brock, James T., Todd V. Royer, Eric B. Snyder, and Steven A. Thomas. "Periphyton metabolism: A chamber approach." In The Controlled Flood in Grand Canyon, 217–23. Washington, D. C.: American Geophysical Union, 1999. http://dx.doi.org/10.1029/gm110p0217.

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Sorokin, Yuri I. "Benthic Microflora, Periphyton and Plant Associations." In Ecological Studies, 127–60. Berlin, Heidelberg: Springer Berlin Heidelberg, 1995. http://dx.doi.org/10.1007/978-3-642-80046-7_5.

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Bąkowska, Martyna, Natalia Mrozińska, Monika Szymańska, Nikol Kolárová, and Krystian Obolewski. "Periphyton Inhabiting Reeds in Polish Water Ecosystems." In The Handbook of Environmental Chemistry, 1–25. Cham: Springer International Publishing, 2019. http://dx.doi.org/10.1007/978-3-030-12139-6_1.

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Planas, D., and G. Moreau. "Reaction of Lotic Periphyton to Experimental Acidification." In Acidic Precipitation, 681–86. Dordrecht: Springer Netherlands, 1986. http://dx.doi.org/10.1007/978-94-009-3385-9_69.

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Vermaat, J. E., and M. J. M. Hootsmans. "Periphyton dynamics in a temperature-light gradient." In Lake Veluwe, a Macrophyte-dominated System under Eutrophication Stress, 193–212. Dordrecht: Springer Netherlands, 1994. http://dx.doi.org/10.1007/978-94-011-2032-6_12.

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Falace, Annalisa, and Guido Bressan. "‘Periphyton’ Colonization: Principles, Criteria and Study Methods." In Artificial Reefs in European Seas, 435–49. Dordrecht: Springer Netherlands, 2000. http://dx.doi.org/10.1007/978-94-011-4215-1_26.

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Cazaubon, Arlette, Thierry Rolland, and Mohammed Loudiki. "Heterogeneity of periphyton in French Mediterranean rivers." In Space Partition within Aquatic Ecosystems, 105–14. Dordrecht: Springer Netherlands, 1995. http://dx.doi.org/10.1007/978-94-011-0293-3_9.

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Smolar-Žvanut, Nataša, and Aleksandra Krivograd Klemenčič. "The Impact of Altered Flow Regime on Periphyton." In Ecohydraulics, 229–43. Chichester, UK: John Wiley & Sons, Ltd, 2013. http://dx.doi.org/10.1002/9781118526576.ch13.

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Conference papers on the topic "Periphyton"

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Hajnal, Eva, Jozsef Lakner, and Csilla Stenger-Kovacs. "Species abundance distribution model for real periphyton samples." In 2012 IEEE 10th International Symposium on Applied Machine Intelligence and Informatics (SAMI). IEEE, 2012. http://dx.doi.org/10.1109/sami.2012.6208990.

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Stone, Mark C., Rollin H. Hotchkiss, and Ryan Morrison. "The Influence of Successional Development on Periphyton Scour Resistance." In World Water and Environmental Resources Congress 2005. Reston, VA: American Society of Civil Engineers, 2005. http://dx.doi.org/10.1061/40792(173)588.

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Naranjo, Ramon, Carol Kendall, and Michael R. Rosen. "GROUNDWATER NUTRIENT SUPPLY TO NEARSHORE PERIPHYTON IN ULTRA-OLIGOTROPHIC LAKE TAHOE." In GSA Connects 2021 in Portland, Oregon. Geological Society of America, 2021. http://dx.doi.org/10.1130/abs/2021am-371006.

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Liang, Xia, and Xiaoping Li. "Responses of Phytoplankton and Periphyton to Environmental Variations in Urbanizing Tidal Rivers." In 2008 2nd International Conference on Bioinformatics and Biomedical Engineering. IEEE, 2008. http://dx.doi.org/10.1109/icbbe.2008.1050.

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Raymond S. Avery, Brian E. Haggard, Marty D. Matlock, and Stephanie M. Williamson. "Nutrient Limitation of Phytoplankton and Periphyton at Lake Eucha, Northeast Oklahoma, USA." In 2004, Ottawa, Canada August 1 - 4, 2004. St. Joseph, MI: American Society of Agricultural and Biological Engineers, 2004. http://dx.doi.org/10.13031/2013.16205.

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Washburn, Spencer, Scott Brooks, Melissa Cregger, Alyssa Carrell, Grace Schwartz, and Dwayne Elias. "Understanding the Effects of Nutrient Concentration on Mercury Cycling within Fluvial Periphyton." In Goldschmidt2021. France: European Association of Geochemistry, 2021. http://dx.doi.org/10.7185/gold2021.6323.

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Richard Carey, George Vellidis, Richard Lowrance, and Catherine Pringle. "Nutrient Enrichment and Stream Periphyton Growth in the Southern Coastal Plain of Georgia." In 2005 Tampa, FL July 17-20, 2005. St. Joseph, MI: American Society of Agricultural and Biological Engineers, 2005. http://dx.doi.org/10.13031/2013.19021.

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Bowes, M. J., J. T. Smith, K. Lehmann, and A. C. Singer. "Investigating periphyton biofilm response to changing phosphorus concentrations in UK rivers using within-river flumes." In BHS 3rd International Conference. British Hydrological Society, 2010. http://dx.doi.org/10.7558/bhs.2010.ic54.

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Brooks, Scott, Grace Schwartz, Todd Olsen, and Katherine Muller. "Ecosystem Controls on Methylmercury Production by Periphyton Biofilms in a Contaminated Stream: Implications for Predictive Modeling." In Goldschmidt2020. Geochemical Society, 2020. http://dx.doi.org/10.46427/gold2020.267.

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Delos Reyes, Miguel Joaquin R., Luigi R. Salgado, May R. Sybal, Nino Rigo Emil G. Lim, Gerardo L. Augusto, Aristotle T. Ubando, and Alvin B. Culaba. "Design, Fabrication, and Testing of a Fully Automated Harvesting Machine for Lab-lab (Periphyton Algal Mat)." In 2019 IEEE 11th International Conference on Humanoid, Nanotechnology, Information Technology, Communication and Control, Environment, and Management ( HNICEM ). IEEE, 2019. http://dx.doi.org/10.1109/hnicem48295.2019.9072809.

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Reports on the topic "Periphyton"

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Raffel, Ann. Methyl Halide Production by Calcareous Periphyton Mats from the Florida Everglades. Portland State University Library, January 2000. http://dx.doi.org/10.15760/etd.1523.

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Honea, Jonathan. The Periphyton Community of a Second Order Subalpine Stream Following Salmon Carcass Decomposition. Portland State University Library, January 2000. http://dx.doi.org/10.15760/etd.7233.

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Bunn, Amoret L., Terri B. Miley, Paul W. Eslinger, Charles A. Brandt, and Bruce A. Napier. Uranium in the Near-shore Aquatic Food Chain: Studies on Periphyton and Asian Clams. Office of Scientific and Technical Information (OSTI), December 2007. http://dx.doi.org/10.2172/1048622.

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Jay, Elizabeth A. Effect of snails (Elimia clavaeformis) on phosphorus cycling in stream periphyton and leaf detritus communities. Office of Scientific and Technical Information (OSTI), January 1993. http://dx.doi.org/10.2172/10102867.

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Bowers, J. A., M. A. Toole, and Y. van Duyn. Steel Creek primary producers: Periphyton and seston, L-Lake/Steel Creek Biological Monitoring Program, January 1986--December 1991. Office of Scientific and Technical Information (OSTI), February 1992. http://dx.doi.org/10.2172/10106918.

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St-Cyr, L., A. Cattaneo, R. Chassé, and C. G. J. Fraikin. Technical evaluation of monitoring methods using microphytes, phytoplankton and periphytin to assess the impacts of mine effluents on the aquatic enviroment. Natural Resources Canada/ESS/Scientific and Technical Publishing Services, 1997. http://dx.doi.org/10.4095/306937.

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Periphyton communities in streams of the Ozark Plateaus and their relations to selected environmental factors. US Geological Survey, 2003. http://dx.doi.org/10.3133/wri024210.

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Relation of periphyton and benthic invertebrate communities to environmental factors and land use at selected sites in part of the upper Mississippi River basin, 1996-98. US Geological Survey, 2003. http://dx.doi.org/10.3133/wri034121.

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Effects of hardened low-water crossings on stream habitat, water quality, and periphyton in four streams at the Fort Polk Military Reservation, Vernon Parish, Louisiana, October 1998 through November 1999. US Geological Survey, 2002. http://dx.doi.org/10.3133/wri024291.

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Water quality of selected effluent-dependent stream reaches in southern Arizona as indicated by concentrations of periphytic chlorophyll a and aquatic-invertebrate communities. US Geological Survey, 1998. http://dx.doi.org/10.3133/wri984199.

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