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What Goes Up is a American comedy-drama film directed by Jonathan Glatzer and starring Hilary Duff, Steve Coogan, Josh Peck, Olivia Thirlby, and Molly.
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The authors declare no competing financial interest. Who needs environmental monitoring? Frontiers Ecol. Reflections on a vision for integrated research and monitoring after 15 years. Google Scholar There is no corresponding record for this reference.

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Surface water quality is improving due to declining atmospheric N deposition. American Chemical Society. Long-term surface water nitrate and atm. Statistical anal. NOx emission control programs during the same time period. Nitrate-N concn.

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Surface waters are thus responding to declining atm. N deposition in much the same way they responded to declining sulfur deposition-although only one watershed showed a relation. Application of a kinetic N satn.

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Further redns. Have U.

Surface waters responded to the Clean Air Act Amendments? Kahl, Jeffrey S. Nearly 20 years of data from regional USEPA programs specifically designed to meet the congressional assessment requirements of the Clean Air Act CAA and amendments, including long-term, site-specific records and long-term repeat surveys of statistical populations, are presented. Topics covered include: location; relating emissions and deposition; status of surface water chem.

National Academies Press , Water Resour. The 1. The only reversals in long-term concn. While management practices likely have slowed increases in groundwater nitrate concns. Spreading dead zones and consequences for marine ecosystems.

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Science , , — , DOI: American Association for the Advancement of Science. A review concerning spreading dead zones hypoxia; extremely low dissolved O2 concns. Topics discussed include: global nature of eutrophication-induced hypoxia; degree of hypoxia; progression of hypoxia; ecosystem responses; missing biomass; recovery; and prospects for change. Cost of reactive nitrogen release from human activities to the environment in the United States.

IOP Publishing Ltd. Leakage of reactive nitrogen N from human activities to the environment can cause human health and ecol. Often these harmful effects are not reflected in the costs of food, fuel, and fiber that derive from N use. Spatial analyses of damage costs attributable to source at management relevant scales could inform decisions in areas where anthropogenic N leakage causes harm. We used recently compiled data describing N inputs in the conterminous United States US to assess potential damage costs assocd. We estd.


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Survey Hydrol. Unit Codes; HUC8s with published coeffs.

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We scaled these N leakage ests. Eutrophication of freshwater ecosystems and respiratory effects of atm. N pollution were important across HUC8s. However, significant data gaps remain in our ability to fully assess N damages, such as damage costs from harmful algal blooms and drinking water contamination. While a no.

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Nitrogen inputs drive nitrogen concentrations in U. Streams and rivers during summer low flow conditions. Total Environ. Bellmore, R. Elsevier B. Many studies have quantified the relationship between N loads to streams in terms of N mass and N inputs to watersheds; however, N concns.

In this study, we examd. N fixation, and point sources , land cover characteristics, and stream network characteristics, including stream size and the extent of lakes and reservoirs. N concn. Median watershed N inputs were N concns. Land cover characteristics were also important predictors, with wetland cover muting the effect of agricultural N inputs on N concns. In contrast, stream variables showed little correlation with N concns.

This suggests that terrestrial factors that can be managed, such as agricultural N use practices and wetland or riparian areas, control the spatial variability in stream N concns. Sources and transformations of nitrate from streams draining varying land uses: Evidence from dual isotope analysis. American Society of Agronomy. Knowledge of key sources and biogeochem. We applied dual isotope anal. Samples were collected monthly at a range of flow conditions for 15 mo during and analyzed for NO3- concns. Samples from two forested watersheds indicated that NO3- derived from nitrification was dominant at baseflow.

NO3- transported to the stream during some high flows. Mixing of two or more distinct sources may have affected the seasonal isotope patterns obsd. In a mixed land use watershed of large drainage area, none of the source and process patterns obsd. These results emphasize that observations at watersheds of a few to a few hundred km2 may be necessary to adequately quantify the relative roles of various NO3- transport and process patterns that contribute to streamflow in large basins. Tracking nonpoint source nitrogen pollution in human-impacted watersheds. Kaushal, Sujay S.

We combined watershed N mass balances and stable isotopes to study fate and transport of nonpoint N in forest, agricultural, and urbanized watersheds at the Baltimore Long-Term Ecol. Research site. N transformations were also obsd. C inputs.

Overall, nonpoint sources such as atm. There were large changes in nitrate sources as a function of runoff, and anticipating source changes in response to climate and storms will be crit. Alternative futures of dissolved inorganic nitrogen export from the Mississippi River Basin: Influence of crop management, atmospheric deposition, and population growth. Biogeochemistry , , 1 — 15 , DOI: Atmospheric inputs of nitrogen, carbon, and phosphorus across an urban area: Unaccounted fluxes and canopy influences.

Earth's Future , 6 2 , — , DOI: Rates of atm. While past studies show elevated rates of inorg.