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Environment

Recalculating Water Treatment Plants' Nitrogen Impact

Water Pollution: Bioavailable nitrogen levels may jump after wastewater leaves treatment plants and hits saltier rivers

by Naomi Lubick
July 9, 2010

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Effects As wastewater travels down rivers toward the ocean, the changing chemical environment could release more microbe-friendly nitrogen.
Effects As wastewater travels down rivers toward the ocean, the changing chemical environment could release more microbe-friendly nitrogen.

Nitrogen compounds in the runoff from wastewater treatment plants can feed microbes in nearby ocean ecosystems, fueling oxygen-depleted dead zones and toxic algal blooms. A new study of how the runoff's chemistry changes as it moves toward the ocean (Environ. Sci. Technol. DOI: 10.1021/es101115g) suggests that plants may release more microbe-friendly nitrogen than researchers previously thought.

Bacteria and phytoplankton feed on inorganic nitrogen molecules released in treated wastewater, such as ammonium (NH4+) and nitrite ions (NO2-). Large fluxes of these nutrients into coastal estuaries boost microbial growth, which can lead to dead zones when the organisms consume most of the water's available oxygen or algal blooms, such as red tide, when toxic phytoplankton multiply.

While microbes devour inorganic nitrogen compounds, they seem to ignore some forms of organic nitrogen such as ammonia bound to humic acid. Because of this disparity, scientists have estimated that only about half of the organic nitrogen in treatment plant runoff is bioavailable.

But Deborah Bronk of the Virginia Institute of Marine Science in Gloucester Point and her colleagues wondered if organic nitrogen became more accessible to microbes as it travels down rivers toward the ocean. After the treated wastewater, or effluent, leaves treatment plants, its chemical surroundings change from a dark, freshwater environment to a sunlit, saltwater one. The scientists hypothesized that salt ions could kick out more-loosely-bound NH4+ from humic acid and sunlight could photochemically breakdown some organic nitrogen compounds into NH4+, NO2-, and amines.  

The researchers started testing their hypothesis by collecting effluent samples from two treatment plants and mixing them with water samples from the James River in Virginia. Each river sample represented a different point along what would be the effluent's journey down an increasingly saltier river. As salinity increased, the effluent's NH4+ concentrations jumped. In one effluent sample, the salty water released almost half of the available nitrogen.

Exposing the effluent to natural light also increased bioavailable nitrogen: For one sample, nine hours of sunlight tripled the effluent's NH4+ concentration.

The total concentration of bioavailable organic nitrogen released by these processes could reach 1 mg/L, the researchers estimate. That concentration is on par with the levels of total nitrogen—bioavailable or not—that regulators allow treatment plants to release: An agreement among the states bordering the Chesapeake Bay plan to cap total nitrogen discharged from their utilities to between 3 and 8 mg/L.

So far, regulators nationwide haven't focused on organic nitrogen levels. Including those compounds in new regulations could present challenges to utilities, says Charles Bott, chief of special projects for Hampton Roads Sanitation District, a wastewater utility in Virginia Beach, Va., that sponsors some of Bronk's work. The problem, Bott says, is that removing organic compounds is not a typical treatment at plants and would be costly to add.

Also, Bott wonders if the transformations that Bronk studied are temporary: Nitrogen could cycle between inorganic and organic forms as it travels down the river. Determining how long it remains bioavailable requires more testing, Bott says. "Getting a true handle on bioavailability is still elusive," he says. "We're not there yet."

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