Friday Jan. 22, 2010
click here to download today's notes in a more printer friendly format

Today's musical selection: about the best version of Stand By Me that I've ever heard.


All of the names on the Experiment, Scientific Paper, and Book Report Signup Lists are now online. 


Today:
Tropospheric ozone and photochemical smog (aka Los Angeles-type smog) with a demonstration
and probably a little bit about natural production and destruction of stratospheric ozone
Sulfur dioxide and London-type smog

We'll finish up air pollution next Monday

Before discussing tropospheric ozone, which is a pollutant, a quick reminder that there is both "good" and "bad" ozone. 

Ozone has a Dr. Jekyll and Mr. Hyde personality.  Ozone in the stratosphere (the ozone layer) is beneficial, it absorbs dangerous high energy ultraviolet light (which would otherwise reach the ground and cause skin cancer, cataracts, and many other problems).

Ozone in the troposphere is bad, it is a pollutant.  That is the stuff we will first be concerned with today.  Tropospheric ozone is a key component of photochemical smog (also known as Los Angeles-type smog)

We'll be making some photochemical smog as a class demonstration.  This will require ozone (and a hydrocarbon of some kind).  We'll use the simple stratospheric recipe for making ozone in the demonstration rather than the more complex tropospheric process (4-step process shown below).


At the top of this figure you see that a more complex series of reactions is responsible for the production of tropospheric ozone.  The production of tropospheric ozone begins with nitric oxide (NO).  NO is produced when nitrogen and oxygen in air are heated (in an automobile engine for example) and react.  The NO can then react with oxygen to make nitrogen dioxide, the poisonous brown-colored gas we made in class.  Sunlight can dissociate (split) the nitrogen dioxide molecule producing atomic oxygen (O) and NO.  O and O2 react in a 4th step to make ozone (O3).  Because ozone does not come directly from an automobile tailpipe or factory chimney, but only shows up after a series of reactions, it is a secondary pollutant.   Nitric oxide would be the primary pollutant in this example.

NO is produced early in the day (during the morning rush hour).  The concentration of NO2 peaks somewhat later.  Peak ozone concentrations are usually found in the afternoon.  Ozone concentrations are also usually higher in the summer than in the winter.  This is because sunlight plays a role in ozone production and summer sunlight is more intense than winter sunlight.

As shown in the figure below, invisible ozone can react with a hydrocarbon of some kind which is also invisible to make a product gas.  This product gas sometimes condenses to make a visible smog cloud or haze.  The cloud is composed of very small droplets or solid particles.  They're too small to be seen but they are able to scatter light - that's why you can see the cloud.

The class demonstration of photochemical smog is summarized below (a flask was used instead of the aquarium shown on the bottom of p. 16 in the photocopied class notes).  We begin by using the UV lamp to create and fill the flask with ozone.  Then a few pieces of fresh lemon peel were added to the flask.  A whitish cloud quickly became visible (colored brown in the figure below).




Next we moved on to the 2nd air pollutant that we will be discussing - sulfur dioxide.  Here's some basic information from the left hand of p. 11 in the photocopied ClassNotes.

Sulfur dioxide is produced by the combustion of sulfur containing fuels such as coal.  Combustion of fuel also produces carbon dioxide and carbon monoxide.  People probably first became aware of sulfur dioxide because it has an unpleasant smell.  Carbon dioxide and carbon monoxide are odorless.  That is why sulfur dioxide was the first pollutant people became aware of.

Volcanoes are a natural source of sulfur dioxide.



The Great London smog is still one of the two or three deadliest air pollution events in history.
Because the atmosphere was stable, SO2 emitted into air at ground level couldn't mix with cleaner air above. 
The SO2 concentration was able to build to dangerous levels. 
4000 people died during this 4 or 5 day period. 
As many as 8000 additional people died in the following weeks and months. 
Some of the photographs below come from articles published in 2002 on the 50th anniversary of the event. 

 


from:
http://news.bbc.co.uk/1/hi/uk/2542315.stm


from:
http://news.bbc.co.uk/1/hi/health/2545747.stm

from:
http://news.bbc.co.uk/1/hi/england/2543875.stm


from:
http://www.npr.org/templates/story/story.php?storyId=873954

The sulfur dioxide didn't kill people directly.   
The SO2 aggravated an existing condition of some kind and hastened their death. 
The SO2 probably also made people susceptible to bacterial infections such as pneumonia.
This link discusses the event and its health effects in more detail.

London type smog which contains sulfur dioxide and is most common during the winter is very different from photochemical or Los Angeles type smog.  Los Angeles type smog contains ozone and is most common in the summer.

Some other air pollution disasters also involved high SO2 concentrations. 
One of the deadliest events in the US occurred in 1948 in Donora, Pennsylvania.




"This eerie photograph was taken at noon on Oct. 29, 1948 in Donora, PA as deadly smog enveloped the town. 20 people were asphyxiated and more than 7,000 became seriously ill during this horrible event."
from: http://oceanservice.noaa.gov/education/kits/pollution/02history.html


from: http://www.eoearth.org/article/Donora,_Pennsylvania

"When Smoke Ran Like Water," a book about air pollution is among the books that you can check out, read, and report on to fulfill part of the writing requirements in this class (instead of doing an experiment report).  The author, Devra Davis, lived in Donora Pennsylvania at the time of the 1948 air pollution episode.

Sulfur dioxide is one of the pollutants that can react with water in clouds to form acid rain (some of the oxides of nitrogen can react with water to form nitric acid).  The formation and effects of acid rain are discussed on p. 12 in the photocopied Class Notes.


Note that clean unpolluted rain has a pH less than 7 and is slightly acidic.  This is because the rain contains dissolved carbon dioxide gas.  We will see how this happens in a class demonstration next Monday. Acid rain is often a problem in regions that are 100s even 1000s of miles from the source of that sulfur dioxide that forms the acid rain.  Acid rain in Scandinavia came from industrialized areas in other parts of Europe.


Some of the problems associated with acid rain.


There was a litle time left in the period so we covered a little information about stratospheric ozone and the ozone layer (found on pps 17-18 in the photocopied ClassNotes).


The top two equations show how ozone is produced in the stratosphere.  Ultraviolet (UV) light splits an O2 molecule into two O atoms.  One of these reacts with O2 to make O3 (ozone).

Ozone is destroyed when it absorbes UV light and is split into O and O2 (the two pieces move away from each other and don't recombine to make ozone).  O3 is also destroyed when it reacts with an oxygen atom.  Two atoms of oxygen reacting to make O2 reduce the amount of one of the raw materials needed to make O3 and thereby reduce the concentration of ozone in the ozone layer.

The bottom figure attempts to show that the ozone concentration in the stratosphere will change until the rates of production and destruction balance each other (analogous to your bank account not changing when the amount of money deposition and withdrawn are equal).

Knowing that you need O2 and UV light to make ozone, you can begin to understand why the ozone layer is found not too high, not too low, but rather in the middle of the atmosphere.



There is plenty of UV light high in the atmosphere but not much oxygen (air gets thinner at higher and higher altitude).  Near the ground there is plenty of oxygen but not as much UV light (it is absorbed by gases above the ground).  You find the optimal amounts of UV light and oxygen somewhere in between, near 25 km altitude.

This next figure lists some of the problems associated with exposure to UV light.  Thinning of the ozone layer will result in increased amounts of UV light reaching the ground.  This wasn't discussed in class.


Skin cancer and cataracts are probably the best known hazards associated with UV light.  At some point in the next week or two we'll look at how man may be damaging the ozone layer by introducing chemical compounds into the atmosphere that react with and destroy stratospheric ozone.