El Nino and the Southern Oscillation (ENSO) |
http://psbsgi1.nesdis.noaa.gov:8080/gifs/sst.gif Experimental SST Anomaly Charts |
I chose to work with the El Nino group because of former work with remote sensing in the GLOBE Global Positioning System (GPS) work which produced the 1996 teacher resources for GLOBE GPS, and because of an interest in earth's energy systems. The research project was completed using data from Internet sources.
Procedure: Internet data were collected (see Links to Data page) and compared with area climate data.
Climate Data:
The Southern Oscillation Index graphs 1947 to 1998, measures the El Nino & La Nina ocean pressures, and provides an index of intensities of each event. Those events, however, do not match precisely the NOAA El Nino events on their distribution maps. From those U.S. distribution maps, for El Nino events (1914, 1918, 1940, 1941, 1957, 1963, 1965, 1972, 1982, 1986, 1987, 1991, and 1994), Georgia has been impacted in the following ways:
| Months | Precipitation | Temperature |
| November-December | Wet | Somewhat warmer to warmer |
| January-March | Normal in North Georgia,
Somewhat wet in South Georgia |
North Georgia cold,
South and East central Georgia very cold |
Year Temperature Averages Precipitation Averages
| Month | November | December | January | February | March | November | December | January | February | March |
| Period Normal | 55.3 | 47.7 | 44.7 | 48.1 | 55.8 | 3.23 | 4.26 | 4.75 | 4.65 | 5.20 |
| 1914-15 | 53.6 | 45.1 | 45.8 | 48.8 | 47.8 | 4.73 | 4.35 | 5.74 | 3.88 | 2.53 |
| 1918-19 | 54.1 | 51.6 | 47.3 | 48.9 | 58.2 | 4.37 | 6.14 | 4.80 | 6.67 | 4.18 |
| 1940-41 | 54.8 | 51.4 | 47.5 | 43.6 | 50.2 | 3.68 | 3.99 | 1.69 | 2.21 | 4.52 |
| 1941-42 | 55.1 | 50.2 | 45.7 | 43.8 | 54.8 | 1.59 | 7.30 | 4.59 | 4.49 | 7.95 |
| 1957-58 | 56.4 | 48.1 | 41.4 | 40.8 | 52.2 | 6.70 | 2.85 | 3.45 | 4.50 | 5.12 |
| 1963-43 | 53.9 | 39.9 | 44.2 | 44.1 | 55.1 | 3.40 | 3.98 | 8.46 | 6.35 | 6.76 |
| 1965-66 | 56.5 | 47.6 | 41.8 | 47.0 | 53.0 | 1.91 | 2.53 | 6.29 | 6.92 | 5.03 |
| 1972-73 | 53.9 | 52.4 | 45.5 | 45.7 | 59.9 | 3.88 | 6.40 | 5.82 | 4.97 | 7.08 |
| 1982-83 | 57.2 | 53.3 | 42.6 | 47.6 | 54.1 | 3.68 | 6.20 | 4.44 | 5.77 | 7.11 |
| 1986-87 | 61.0 | 48.9 | 44.6 | 47.6 | 55.2 | 6.27 | 4.61 | 7.60 | 5.78 | 5.45 |
| 1987-88 | 57.0 | 51.2 | 46.2 | 52.3 | 55.2 | 2.96 | 2.54 | 5.15 | 4.11 | 3.46 |
| 1991-92 | 52.4 | 51.0 | 46.2 | 52.3 | 55.2 | 1.77 | 3.49 | 6.24 | 5.4 | 5.16 |
| 1994-95 | 59.2 | 51.0 | 46.5 | 47.9 | 58.9 | 2.92 | 3.37 | 4.52 | 6.23 | 3.25 |
Generally, the hypothesis is affirmed, but there are more data sets that need to be analyzed. The Pacific Sea Surface Temperatures need to be correlated with the Southern Oscillation Index, then compared with all the precipitation and temperature data for Georgia, before final conclusions can effectively drawn.
Each teacher made a presentation to colleagues at the Institute, often sharing teaching materials, resources, or leading colleagues in activities. The following was made based upon research done at the Air Quality Laboratory at Georgia Institute of Technology.
Key words: ozone, photochemical smog, VOCs, NOx
With the first free radical oxygen being produced from the decomposition of the oxygen (O2) molecule or another type of molecule containing oxygen, by uv light or some other high energy activity, such as lightening or manufacturing.
Ozone naturally decomposes, reforming oxygen molecules in an oxygen cycle, unless additional pollutants are present in the atmosphere. A chemical that can increase the productivity of ozone in the troposphere is NO, nitric oxide. Combustion produces NO from atmospheric nitrogen and oxygen:
Nitric oxide will react with oxygen to form nitrogen peroxide, NO2, also called nitrogen dioxide. The ratio of NO and NO2 is referred to as NOx, because there is an equilibrium between the NO and NOx:
The NO2 will also decompose with uv radiation (<430nm), forming a free radical oxygen, which can then, form ozone according to reaction [1], above. The decomposition is:
The NOx levels are typically low enough, however, that ozone is not formed. Further, the nitrogen oxides will also react with water molecules in the atmosphere, forming relatively short lived acids (HNO2, nitrous acid, and HNO3, nitric acid), both of which can precipitate as acid rains, within a few days. Thus, the NOx is not particularly problematic in clean air environments, with ozone production increasing in a linear fashion as NOx increases.
However, if carbon compound pollutants are added to the atmosphere, the NOx production of ozone will increase in a nonlinear fashion, even growing exponentially. Those compounds (called collectively, volatile organic compounds or VOCs) include:
where M could be any number of atmospherically produced compounds.
Depletion of the ozone and ozone precursors occur with the production of several water soluble compounds, including several acids (inorganic and organic), hydrogen peroxide (H2O2), and organic peroxides. These compounds dissolve in cloud droplets and precipitate out of the atmosphere.
Ozone also correlates with concentrations of CO and SO2, which are not ozone precursors. The suggested rationale for such correlation is that emissions of CO and SO2 from industrial sources also emit non methane hydrocarbons (NMHC) and NOx, which are ozone precursors.
Vegetation in both urban and rural regions is a significant producer of VOC’s and atmospheric nitric oxide (NO) is produced by fertilized, cultivated soils and lightening. However, all atmospheric ozone precursors increase significantly from motorized vehicles, from combustion processes, and from industrialization. Thus, industrialized regions can suffer from a decided increase in tropospheric ozone production.
Reduction in NOx has been found to decrease ozone levels, which can be accomplished by improved combustion techniques. Even reduction of highway grades has been found to diminish precursor emissions from trucks, for example.
Woodrow
Wilson
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