acid rain l.
Skip this Video
Loading SlideShow in 5 Seconds..
Acid Rain PowerPoint Presentation
Download Presentation
Acid Rain

Loading in 2 Seconds...

play fullscreen
1 / 23

Acid Rain - PowerPoint PPT Presentation

  • Uploaded on

Acid Rain. RUSSELL R. DICKERSON. Sandstone portal Figure on Herten Castle in Ruhr district of Germany. Sculpted 1702; photographed in 1908. Same sandstone portal figure photographed in 1969. ACID DEPOSITION See Turco, Ch. 9 Finlayson-Pitts & Pitts, Part 6 Seinfeld & Pandis Ch. 20

I am the owner, or an agent authorized to act on behalf of the owner, of the copyrighted work described.
Download Presentation

Acid Rain

An Image/Link below is provided (as is) to download presentation

Download Policy: Content on the Website is provided to you AS IS for your information and personal use and may not be sold / licensed / shared on other websites without getting consent from its author.While downloading, if for some reason you are not able to download a presentation, the publisher may have deleted the file from their server.

- - - - - - - - - - - - - - - - - - - - - - - - - - E N D - - - - - - - - - - - - - - - - - - - - - - - - - -
Presentation Transcript
acid rain

Acid Rain



Sandstone portal Figure on Herten Castle in Ruhr district of Germany. Sculpted 1702; photographed in 1908.



See Turco, Ch. 9

Finlayson-Pitts & Pitts, Part 6

Seinfeld & Pandis Ch. 20


The industrial revolution greatly increased the amount of acid in the atmosphere. These acids accelerate the rate of “weathering” of both natural and man-made materials. (Figures of sandstone Madonna). Today we will discuss what acid deposition is, what its effects are, the chemistry and physics of formation and transport, and who is responsible for it.



As early as 1852, R. A. Smith analyzed rain that near the industrial city of Manchester, England and found that urban aerosol particles tend to be composed primarily of sulfuric acid, but as the air is transported away from sources over more rural areas, the acid is neutralized by absorption of ammonia.

urban → suburban → rural

H₂SO₄ + NH₃ → (NH₄)HSO₄ (+NH₃) → (NH₄)₂SO₄

sulfuric acid → ammonium bisulfate → ammonium sulfate

Throughout the early part of the twentieth century, European scientists documented the sources and effects of atmospheric acids. It was not until 1958 that acidity of precipitation in the US was characterized (Junge and Werby, 1958)



wet deposition

dry deposition

occult deposition



Soils (Figure) have colloidal molecules (clay particles) that have a layer of negative charge. They hold positively charged cations such as , Al³⁺, K⁺, Mg²⁺, and Ca²⁺. Some of these cations are essential plant nutrients (K⁺, Mg²⁺, Ca²⁺), while Al³⁺ is toxic. Hydrogen ions from acid deposition replace these cations on the outer layer of colloidal molecules. The metal ions are then dissolved and leached into solution and can be washed away from the soil and into surface or ground water. Soil fertilitiy is reduced and aluminum ions can replace calcium in the fish’s gills. Acidity can also come from oxidation (weathering) of sulfur-rich mine tailings, and from nitrification of ammonium.


A soils capacity to exchange base ions for those in solution (cation exchange capacity) is a measure of potential fertility. The impact of acids on soil fertility depends on the structure and composition of the clays in the soil. Maryland has serveral geological regimes with varying sensitivities to acid deposition (Figure).

Forests can be especially sensitive to nutrient loss. In Europe in 1993 abou ta quarter of the trees have died or are more than 25% defoliated. This “Waldsterben” or “forest death” has been attributed at, least in part, to environmental degradation from a combination of acid deposition, ground-level ozone, and excess nutrification, primarily nitrogen. In the US, loss of forests has been so dramatic, although several species including ash and oak are sensitive to acidification of soils.


Lakes and Streams

The sensitivity surface waters depends critically on their neutralizing or buffering capacity. Alkaline materials such as CaCO₃, and MgCO₃ can neutralize acids.

The surface of the American Midwest is predominantly limestone (CaCO₃), and lakes and streams have high neutralizing capacity. In the East granite dominates; soils and surface waters lacking buffering capacity, are highly sensitive to acidification.


Salt Waters

The Ocean is strongly pH buffered, has a high sulfate content naturally, and is relatively insensitive to “acid rain.” Over much of the ocean, however, nitrate is the limiting nutrient for biological activity. Addition of nitrogen from the atmosphere can increase primary productivity, and the consequences reverberate throughout the ecosystem. The Chesapeake Bay is particularly sensitive to excess nutrients. Additional nitrate or ammonium from atmospheric deposition to the Bay or its watershed contributes to the problem of excess eutrophication. Nitrate allows thick beds of aquatic layers of the waters. Loss of higher animals follows.



The Taj Mahal, the friezes on the Parthenon, the Madonna in Herten, Germany, and the Lincoln Memorial are made of marble. Marble, a particular crystalline form of calcite (CaCO₃), and sandstone (grains of sand held together by calcite), are subject to attack by sulfuric acid.

CaSO₄ is gypsum, which is 100 times more soluble than CaCO₃. Many priceless historic structures have been lost to acid deposition.

On a more pragmatic note, the rate of corrosion of galvanized (zinc coated) steel is 0.62 um/yr in the Adirondacks, 1.01 in Washington, DC, and 1.47 in Stubenville, OH.


Covered already in Lectures 1 and 9.



Primarily power generation and ore smelting (pie charts).

For example nickel is mined as nickel sulfide, NiS. In smelting, it is heated in air (Sudbury, Canada).

The molecular weight of nickel is 57 g/mole, so smelting produces more than a ton of SO₂ for each ton of nickel produced.

d) Formation and Composition

Gas Phase production of nitric acid:

OH + NO₂ + M → HNO₃ + M

Aqueous phase production of nitric acid:

NO₂ + O₃ → NO₃ + O₂

NO₃ + NO₂ + M = N₂O₅ + M

N₂O₅ + H₂O(l) → 2HNO₃(aq)


This process is important only at night, and when air temperatures are low because the formation of N₂O₅ is reversible, and the equilibrium coefficient is highly temperature dependent. Also, NO₃ is rapidly photolyzed by visible radiation.

NO₃ + hv → NO₂ + O

Gas Phase production of sulfuric acid:

OH + SO₂ + M → HOSO₂ + M

Aqueous phase production of sulfuric acid:

SO₂ + H₂O₂ → H₂SO₄

Lifetime and Transport

Wet vs dry deposition


Problem Solving

  • European community requirements: 2.0 g/m3 and 0.4 g/m3 if coal is 0.5 to 7% S by weight, can such goals be met by buying low sulfur coal??
  • Calculate the pH of a solution of 10 μM and 10 μm
  • From the mean pH of 4.1, and the assumption of equal molar nitrate and sulfate, estimate the molarity of nitric and sulfuric acids in College Park.
  • Estimate the rate of dry deposition for a give PBL height, and concentration of H₂SO₄ and HNO₃.
  • If rainout plus washout is 50% efficient, what would have to be precipitation frequency for there to be equivalent amounts of wet and dry acid deposition?
patterns of so 2 and no x emissions in eastern u s

NOx: transportation,

power plants

SO2: coal-fired power plants

global sulfur budget flux terms in tg s yr 1
GLOBAL SULFUR BUDGET(flux terms in Tg S yr-1)


t = 3.9d


t = 1.3d













6 dry

44 wet



27 dry

20 wet


t = 1.0d






depletion of base cations from acid rain hubbard brook experimental forest new hampshire
DEPLETION OF BASE CATIONS FROM ACID RAIN(Hubbard Brook Experimental Forest, New Hampshire)
questions on acid rain

1. A dinosaur extinction theory suggests that massive heating of theEarth's atmosphere in the path of a falling asteroid would have led toextremely acid rain, killing the land vegetation and hence thedinosaurs' food supply. What acid would have been involved?

2. Nitrate deposited by acid rain can fertilize the biosphere. Explain why.