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Related Concept Videos

Freshwater Microbial Ecology01:24

Freshwater Microbial Ecology

Freshwater systems such as streams, rivers, and lakes exhibit distinct physical and biological characteristics that influence their microbial communities. These environments are broadly categorized into lotic systems—those with flowing waters like streams and most rivers—and lentic systems, which include still or slow-moving waters such as lakes, ponds, and marshes.In lentic systems, phytoplankton drive primary production, generating autochthonous organic carbon. In contrast, lotic systems...
Microbial Wastewater Treatment01:30

Microbial Wastewater Treatment

Microbial communities in aquatic ecosystems play a key role in the natural breakdown of contaminants introduced through domestic and industrial effluents. Acting as biological catalysts, these microbes change and mineralize a wide range of organic and inorganic pollutants under different redox conditions.In oxygen-rich surface waters, aerobic heterotrophs lead organic matter breakdown, using oxygen as the terminal electron acceptor to efficiently oxidize substrates to carbon dioxide and water.
Microbes and Other Elemental Cycles01:24

Microbes and Other Elemental Cycles

Microbial activity plays a pivotal role in the biogeochemical cycling of iron and manganese, especially at the redox gradients characteristic of stratified aquatic environments. These cycles are driven by microbial transformations between oxidized and reduced forms of the metals, allowing organisms to exploit them for metabolic energy and structural purposes.Iron Cycling Across Redox GradientsIn neutral, oxygen-rich surface waters, iron is predominantly found in its oxidized, insoluble ferric...
Marine Microbial Ecology01:30

Marine Microbial Ecology

Marine microbial ecosystems are shaped by distinct physicochemical limits, including high salinity, low nutrient availability, and fluctuating oxygen levels. These conditions favor smaller microbial cell sizes, which maximize their surface-to-volume ratio for efficient nutrient uptake.Microbial activity and community composition are closely linked to biogeochemical cycles, particularly in dynamic environments like estuaries, where halotolerant microbes thrive in response to variable salinity...
Microbial Growth Measurement: Indirect Methods01:27

Microbial Growth Measurement: Indirect Methods

Estimating microbial growth is essential for understanding population dynamics and environmental adaptations. Indirect methods provide valuable insights by measuring parameters such as turbidity, metabolic activity, and biomass, enabling efficient and reproducible assessments.During exponential growth, microbial cells scatter light proportionally to their biomass, a principle used in turbidity measurements. About one million cells per milliliter produce detectable scattering, which a...
Primary Production01:06

Primary Production

The total amount of energy acquired by primary producers in an ecosystem is called gross primary production (GPP). However, of this energy, producers use some for metabolic processes, and some is lost as heat, decreasing the amount of energy available to the next trophic level. The remaining usable amount of energy is called the net primary productivity (NPP). In terrestrial ecosystems, NPP is driven by climate, while light penetration and nutrient availability drive NPP in aquatic ecosystems.

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Updated: Jun 2, 2026

Understanding Dissolved Organic Matter Biogeochemistry Through In Situ Nutrient Manipulations in Stream Ecosystems
09:38

Understanding Dissolved Organic Matter Biogeochemistry Through In Situ Nutrient Manipulations in Stream Ecosystems

Published on: October 29, 2016

Light-mediated thresholds in stream-water nutrient composition in a river network.

Jacques C Finlay1, James M Hood, Michael P Limm

  • 1Department of Ecology, Evolution and Behavior, University of Minnesota, St. Paul, Minnesota 55108, USA. jfinlay@umn.edu

Ecology
|May 13, 2011
PubMed
Summary

River nutrient composition changes downstream due to watershed and in-stream processes. Larger rivers showed decreased phosphorus and increased nitrogen, shifting from nitrogen to phosphorus limitation.

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Last Updated: Jun 2, 2026

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The Benthic Exchange of O2, N2 and Dissolved Nutrients Using Small Core Incubations

Published on: August 3, 2016

Area of Science:

  • Ecology
  • Hydrology
  • Biogeochemistry

Background:

  • River solute composition is shaped by watershed inputs and in-stream processes.
  • Downstream changes in nutrient dynamics are not well understood, especially the balance between watershed loading and in-channel transformations.

Purpose of the Study:

  • To investigate how longitudinal changes in environmental conditions affect water-column nutrient composition in a river system.
  • To differentiate the impacts of watershed loading versus in-channel processes on nutrient dynamics from headwaters to larger downstream reaches.

Main Methods:

  • Studied a forested river watershed with a mediterranean hydrologic regime during summer base flow.
  • Collected water samples across a network of sites, from small headwater streams to larger downstream river sections.
  • Analyzed nutrient concentrations (nitrogen, phosphorus, silica, dissolved organic carbon) and stoichiometry.

Main Results:

  • Headwater streams (small watershed area) exhibited consistent nutrient concentrations and low dissolved nitrogen (N) to phosphorus (P) ratios (~2).
  • Larger streams (>100 km2 watershed area) showed significant shifts: P and silica decreased by >50%, while dissolved organic carbon and N increased 3-6 times.
  • Downstream N:P ratios increased to 46, indicating a shift from potential N limitation to potential P limitation.

Conclusions:

  • Increasing light availability and algal production in larger downstream sections drive significant alterations in nutrient concentration and stoichiometry.
  • In-channel processes, particularly algal photosynthesis and nitrogen fixation, play a crucial role in modifying nutrient dynamics downstream.
  • The study highlights a transition in nutrient limitation from headwaters to larger rivers, mediated by ecological processes within the stream network.