Effects of nutrient enrichment on algal biomass across a natural light gradient

2005 ◽  
Vol 164 (4) ◽  
pp. 449-464 ◽  
Author(s):  
W. Keith Taulbee ◽  
Scott D. Cooper ◽  
John M. Melack
2012 ◽  
Vol 19 (1) ◽  
pp. 316-326 ◽  
Author(s):  
Cecilia Laspoumaderes ◽  
Beatriz Modenutti ◽  
María Sol Souza ◽  
Marcela Bastidas Navarro ◽  
Florencia Cuassolo ◽  
...  

2007 ◽  
Vol 64 (2) ◽  
pp. 227-238 ◽  
Author(s):  
Michael J Bowes ◽  
Jim T Smith ◽  
John Hilton ◽  
Michael M Sturt ◽  
Patrick D Armitage

Nutrient modification experiments were conducted in streamside flumes to determine the concentration at which P limits algal growth in the mesotrophic River Frome, Dorset, UK. The soluble reactive P (SRP) concentration in each flume was either increased (by P addition), decreased (by precipitating P with iron(II) sulphate solution), or left unaltered (control), producing SRP concentrations ranging from 32 to 420 µ·L–1. Increasing the ambient SRP concentration did not increase epilithic algal growth, showing that the River Frome was not P limited at 109 µ SRP·L–1. In the P-stripped flumes, algal biomass declined as the SRP concentration fell below ~90 µ·L–1, with a 60% biomass reduction at <40 µ SRP·L–1. Phosphorus-diffusing periphytometers deployed in the P-stripped flumes confirmed that reduced rates of algal growth were due to P limitation rather than a physical effect of FeSO4 addition. The ~90 µ·L–1 maximum P-limiting concentration is likely to be similar for comparable nutrient-impacted rivers. This iron-stripping approach expands the existing river nutrient-enrichment methodology so that it can be used in nutrient-impacted rivers and should allow catchment managers to produce knowledge-based P reduction targets prior to introducing remediation.


Flora ◽  
2020 ◽  
Vol 268 ◽  
pp. 151626
Author(s):  
Mirko U. Granata ◽  
Francesco Bracco ◽  
Paola Nola ◽  
Rosangela Catoni

1976 ◽  
Vol 33 (7) ◽  
pp. 1553-1563 ◽  
Author(s):  
John G. Stockner ◽  
K. R. S. Shortreed

Attached algal growth in Carnation Creek and its estuary were monitored in 1974 and 1975 as part of the Carnation Creek Experimental Watershed Project. Net production on the estuary was 17.8 μg organic matter (org)∙cm−2∙day−1, and in Carnation Creek the average was 3.4 μg org∙cm−2∙day−1. Algal growth in Ritherdon Creek, located in an adjacent logged watershed, was slightly higher (4.6 μg org∙cm−2∙day−1) than the Carnation Creek average. In a streamside nutrient enrichment experiment, nitrate and phosphate concentrations in one trough were increased to twice the normal Carnation Creek values present in the control. In 35 days the nutrient-enriched trough had a total algal volume 3 times that of the control. It is suggested that extremely low nutrient concentrations (especially phosphate), and secondarily, poor light conditions under the canopy, are responsible for the paucity of algal growth in Carnation Creek. Major loss of algae from the system is caused by periodic freshets which scour the stream bed. Losses by grazing herbivorous insects were considered negligible. Dominant diatoms in Carnation Creek were Achnanthes minutissima, Synedra ulna, Hannaea arcus, Diatoma hiemale, and Eunotia pectinalis. Ulothrix sp., Draparnaldia sp., and Mougeotia sp. were the dominant filamentous green algae. Net production and algal biomass (chlorophyll a) in Carnation Creek are among the lowest ever reported in the literature.


2010 ◽  
Vol 19 (3) ◽  
pp. 367 ◽  
Author(s):  
Marta Pardos ◽  
Jaim Puértolas ◽  
Guillermo Madrigal ◽  
Enrique Garriga ◽  
Santiago De Blas ◽  
...  

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