Atmospheric deposition control

If necessary, EPA is required to promulgate regulations to control the atmospheric deposition of hazardous air pollutant to surface and coastal waters. 

Title rV Acid Deposition Control - As we all know, acid rain occurs when sulfur dioxide and nitrogen oxide emissions are transformed in the atmosphere and return to the earth in rain, fog, or snow. Approximately 20 million tons of SOj are emitted annually in the United States, mostly from the burning of fossil fuels by electric... 

Wildlife indicators of mercury exposure and trends are important elements of a comprehensive approach to assess mercury in the environment and the monitoring of trends that may assist regulators and the regulated community in long-term evalnation of the need and usefulness of mercury somce controls. It is important to understand, however, that bioindicator data alone are insufficient to answer snch critical qnestions as identification of mercniy sonrces, or the relative importance of local, regional, and global inputs of mercury somces to atmospheric deposition and errvirorrmerrtal loading in specific areas. 

Th, Co, and, in some locations, Fe. Surfece-water enrichments are usually caused by rapid rates of supply to the mixed layer via atmospheric deposition or river runoff. Removal usually occurs through relatively rapid precipitation into or adsorption onto sinking particles. Trace elements controlled by scavenging tend to have short (100 to lOOOy) residence times. Since these residence times are less than the mixing time of the ocean, significant geographic gradients are common. 

Lake Superior. Historical accumulation rates, homolog compositions (from PCA) and atmospheric deposition rates all indicated a primarily atmospheric source to Lake Superior and the control lakes, with an additional TeCDF and PnCDF contribution to Lake Superior in the 1950s and 1960s. The authors were unable to conclude confidently that paper mills were the source of elevated PCDF, although it was stated that the homolog composition was consistent with bleached kraft mill discharge. The PCDF source in Lake Superior decreased after 1980. 

The Great Lakes have served as a focal point for PCB research. This research has provided an understanding of the processes controlling fate and transport of PCBs, and has led to the development of models than can be applied to other contaminants and water bodies. The processes of atmospheric deposition and net sediment accumulation are described adequately in these models, but the exchange at the sediment-water interface and seasonal depositional patterns need further improvements. While concentrations have declined in air, water and sediments over the last decade, trends in fish indicate a slowing or stopping of such a decline. Thus future research efforts should address the bioaccumulation process and foodweb dynamics, and the physical processes mentioned above. 

Clathrate hydrates have been found to occur naturally in large quantities. Around 120 X 10 m (at STP) of methane is estimated to be trapped in deposits of the deep ocean floor [10]. Clathrate hydrates are also suspected to occur in large quantities on some outer planets, moons, and trans-Neptunian objects [11]. In the petroleum industry, hydrocarbon clathrate hydrates are a cause of problems because they can form inside gas pipelines, often resulting in plugging. Deep sea deposition of carbon dioxide clathrate hydrate has been proposed as a method to remove this greenhouse gas from the atmosphere and control climate change [12]. 

At various facilities that process uranium for defense programs, uranium is released to the atmosphere under controlled conditions, resulting in deposition on the soil and surface waters. Monitoring data from the area surrounding the Fernald Environmental Management Project (formerly the Fernald Feed Materials Production Center) showed that soil contained uranium released from the facility (Stevenson and Hardy 1993). 

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