Ammonia Modeling for Assessing Potential Toxicity to Fish Species in the Rio Grande, 1989-2002

Increasing volumes of treated and untreated human sewage discharged into rivers around the world are likely to be leading to high aquatic concentrations of toxic, unionized ammonia (NH₃), with negative impacts on species and ecosystems. Tools and approaches are needed for assessing the dynamics of N...

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Veröffentlicht in:Ecological applications 2007-10, Vol.17 (7), p.2087-2099
Hauptverfasser: Passell, Howard D., Dahm, Clifford N., Bedrick, Edward J.
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Bedrick, Edward J.
description Increasing volumes of treated and untreated human sewage discharged into rivers around the world are likely to be leading to high aquatic concentrations of toxic, unionized ammonia (NH₃), with negative impacts on species and ecosystems. Tools and approaches are needed for assessing the dynamics of NH₃. This paper describes a modeling approach for first-order assessment of potential NH₃ toxicity in urban rivers. In this study daily dissolved NH₃ concentrations in the Rio Grande of central New Mexico, USA, at the city of Albuquerque's treated sewage outfall were modeled for 1989-2002. Data for ammonium (${\rm{NH}}_4 ^ + $) concentrations in the sewage and data for discharge, temperature, and pH for both sewage effluent and the river were used. We used State of New Mexico acute and chronic NH₃- N concentration values (0.30 and 0.05 mg/L NH₃-N, respectively) and other reported standards as benchmarks for determining NH₃ toxicity in the river and for assessing potential impact on population dynamics for fish species. A critical species of concern is the Rio Grande silvery minnow (Hybognathus amarus), an endangered species in the river near Albuquerque. Results show that NH₃ concentrations matched or exceeded acute levels 13%, 3%, and 4% of the time in 1989, 1991, and 1992, respectively. Modeled NH₃ concentrations matched or exceeded chronic values 97%, 74%, 78%, and 11% of the time in 1989, 1991, 1992, and 1997, respectively. Exceedences ranged from 0% to 1% in later years after enhancements to the wastewater treatment plant. Modeled NH₃ concentrations may differ from actual concentrations because of NH₃ and ${\rm{NH}}_4 ^ + $ loss terms and additive terms such as mixing processes, volatilization, nitrification, sorbtion, and ${\rm{NH}}_4 ^ - $ uptake. We conclude that NH₃ toxicity must be considered seriously for its potential ecological impacts on the Rio Grande and as a mechanism contributing to the decline of the Rio Grande fish community in general and the. Rio Grande silvery minnow specifically. Conclusions drawn for the Rio Grande suggest that NH₃ concentrations may be high in rivers around the world where alkaline pH values are prevalent and sewage treatment capabilities are poorly developed or absent.
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We used State of New Mexico acute and chronic NH₃- N concentration values (0.30 and 0.05 mg/L NH₃-N, respectively) and other reported standards as benchmarks for determining NH₃ toxicity in the river and for assessing potential impact on population dynamics for fish species. A critical species of concern is the Rio Grande silvery minnow (Hybognathus amarus), an endangered species in the river near Albuquerque. Results show that NH₃ concentrations matched or exceeded acute levels 13%, 3%, and 4% of the time in 1989, 1991, and 1992, respectively. Modeled NH₃ concentrations matched or exceeded chronic values 97%, 74%, 78%, and 11% of the time in 1989, 1991, 1992, and 1997, respectively. Exceedences ranged from 0% to 1% in later years after enhancements to the wastewater treatment plant. Modeled NH₃ concentrations may differ from actual concentrations because of NH₃ and ${\rm{NH}}_4 ^ + $ loss terms and additive terms such as mixing processes, volatilization, nitrification, sorbtion, and ${\rm{NH}}_4 ^ - $ uptake. We conclude that NH₃ toxicity must be considered seriously for its potential ecological impacts on the Rio Grande and as a mechanism contributing to the decline of the Rio Grande fish community in general and the. Rio Grande silvery minnow specifically. 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We used State of New Mexico acute and chronic NH₃- N concentration values (0.30 and 0.05 mg/L NH₃-N, respectively) and other reported standards as benchmarks for determining NH₃ toxicity in the river and for assessing potential impact on population dynamics for fish species. A critical species of concern is the Rio Grande silvery minnow (Hybognathus amarus), an endangered species in the river near Albuquerque. Results show that NH₃ concentrations matched or exceeded acute levels 13%, 3%, and 4% of the time in 1989, 1991, and 1992, respectively. Modeled NH₃ concentrations matched or exceeded chronic values 97%, 74%, 78%, and 11% of the time in 1989, 1991, 1992, and 1997, respectively. Exceedences ranged from 0% to 1% in later years after enhancements to the wastewater treatment plant. Modeled NH₃ concentrations may differ from actual concentrations because of NH₃ and ${\rm{NH}}_4 ^ + $ loss terms and additive terms such as mixing processes, volatilization, nitrification, sorbtion, and ${\rm{NH}}_4 ^ - $ uptake. We conclude that NH₃ toxicity must be considered seriously for its potential ecological impacts on the Rio Grande and as a mechanism contributing to the decline of the Rio Grande fish community in general and the. Rio Grande silvery minnow specifically. 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In this study daily dissolved NH₃ concentrations in the Rio Grande of central New Mexico, USA, at the city of Albuquerque's treated sewage outfall were modeled for 1989-2002. Data for ammonium (${\rm{NH}}_4 ^ + $) concentrations in the sewage and data for discharge, temperature, and pH for both sewage effluent and the river were used. We used State of New Mexico acute and chronic NH₃- N concentration values (0.30 and 0.05 mg/L NH₃-N, respectively) and other reported standards as benchmarks for determining NH₃ toxicity in the river and for assessing potential impact on population dynamics for fish species. A critical species of concern is the Rio Grande silvery minnow (Hybognathus amarus), an endangered species in the river near Albuquerque. Results show that NH₃ concentrations matched or exceeded acute levels 13%, 3%, and 4% of the time in 1989, 1991, and 1992, respectively. Modeled NH₃ concentrations matched or exceeded chronic values 97%, 74%, 78%, and 11% of the time in 1989, 1991, 1992, and 1997, respectively. Exceedences ranged from 0% to 1% in later years after enhancements to the wastewater treatment plant. Modeled NH₃ concentrations may differ from actual concentrations because of NH₃ and ${\rm{NH}}_4 ^ + $ loss terms and additive terms such as mixing processes, volatilization, nitrification, sorbtion, and ${\rm{NH}}_4 ^ - $ uptake. We conclude that NH₃ toxicity must be considered seriously for its potential ecological impacts on the Rio Grande and as a mechanism contributing to the decline of the Rio Grande fish community in general and the. Rio Grande silvery minnow specifically. Conclusions drawn for the Rio Grande suggest that NH₃ concentrations may be high in rivers around the world where alkaline pH values are prevalent and sewage treatment capabilities are poorly developed or absent.</abstract><cop>United States</cop><pub>Ecological Society of America</pub><pmid>17974343</pmid><doi>10.1890/06-1293.1</doi><tpages>13</tpages></addata></record>
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source Jstor Complete Legacy; MEDLINE; Wiley Online Library Journals Frontfile Complete
subjects Ammonia
Ammonia - analysis
Ammonia - toxicity
ammonium
Animals
Cyprinidae
Ecological modeling
endangered species
Fish
Freshwater
Freshwater ecology
Freshwater fishes
Hybognathus amarus
Hydrogen-Ion Concentration
long-term trends
Minnows
Models, Theoretical
New Mexico
Nitrogen
Quaternary Ammonium Compounds - analysis
Rio Grande silvery minnow
Rivers
Sewage
Species
Temperature
USA
Waste Disposal, Fluid
wastewater
Water Pollutants, Chemical - analysis
Water Pollutants, Chemical - toxicity
Water quality
title Ammonia Modeling for Assessing Potential Toxicity to Fish Species in the Rio Grande, 1989-2002
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