Ozone (O₃) is one of the most chemically consequential molecules in Earth’s atmosphere – yet where it sits determines whether it’s a life-protecting shield or a public health hazard. The same three-atom molecule that blocks harmful solar radiation in the upper atmosphere becomes a lung-damaging pollutant at ground level. Understanding how ozone forms, how it gets destroyed, and how human activity has disrupted its natural balance is central to atmospheric chemistry and environmental science.

Table of Contents

Stratospheric ozone: Earth’s natural UV shield

According to NASA, stratospheric ozone is created primarily by ultraviolet radiation – when high-energy UV rays strike ordinary oxygen molecules (O₂), they split into two single oxygen atoms, which then combine with other O₂ molecules to form ozone (O₃). This process happens continuously in the stratosphere, roughly 15 to 35 kilometres above Earth’s surface.

About 90% of the ozone in the atmosphere is concentrated in the stratosphere, where ozone concentrations are greatest between about 20 and 40 kilometres altitude, ranging from about 2 to 8 parts per million. Despite this relatively low concentration, the ozone layer absorbs the portion of UV light known as UVB – a band of ultraviolet radiation with wavelengths from 280 to 320 nanometres – which is particularly effective at damaging DNA and is a cause of melanoma and other types of skin cancer.

The chemistry behind this protection involves a continuous cycle. When an ozone molecule absorbs even low-energy UV radiation, it splits into an ordinary oxygen molecule and a free oxygen atom – which then quickly re-joins with another oxygen molecule to reform ozone. This “ozone-oxygen cycle” is not static destruction; it is an ongoing conversion of harmful UV energy into heat, effectively preventing that radiation from reaching the surface.

When undisturbed, the balance between natural ozone production and destruction maintains a consistent ozone concentration in the stratosphere. Other gases containing nitrogen and hydrogen also participate in reaction cycles that destroy ozone, converting it back into oxygen – but in the natural system, production and destruction remain roughly equal.

Ozone depletion: catalysts and chemistry

The natural balance of the ozone layer began breaking down in the second half of the 20th century due to synthetic chemicals released by human activity. In 1974, Molina and Rowland – who later received the 1995 Nobel Prize in Chemistry – proposed that stratospheric ozone might be destroyed by industrially produced chlorine- and bromine-containing substances, such as chlorofluorocarbons commonly used in spray cans, refrigerators, and air conditioners.

How CFCs reach and damage the stratosphere

CFCs are transparent to visible solar radiation and to UV wavelengths that penetrate to the lower atmosphere; they are negligibly soluble in water and do not react with OH, O₂, O₃ or other oxidizing agents in the lower atmosphere. This extreme chemical stability is precisely what makes them dangerous. CFCs slowly make their way up into the stratosphere – most molecules decompose before they can cross into the stratosphere from the troposphere – but this prolonged life in the atmosphere allows them to reach great altitudes where photons are more energetic. When CFCs come into contact with these high-energy photons, their components are freed.

The result is the release of reactive chlorine atoms, which then attack ozone. Chlorine acts as a catalyst – it initiates the breakdown of ozone and combines with a freed oxygen atom to create two oxygen molecules. After each reaction, the chlorine atom is regenerated and begins the destructive cycle again. One chlorine atom can thereby destroy thousands of ozone molecules.

The role of nitrogen oxides

CFCs are not the only culprits. Nitrogen oxides (NOₓ) also participate in catalytic ozone destruction. Nitrous oxide (N₂O) is a key source of reactive nitrogen species in the NOₓ catalytic cycle that destroys stratospheric ozone. NOₓ compounds react with ozone to produce nitrogen dioxide and molecular oxygen, and then the nitrogen dioxide reacts with atomic oxygen to regenerate the original nitrogen oxide – completing a cycle that continuously depletes ozone without the catalyst being consumed.

The Antarctic ozone hole

The most dramatic evidence of ozone depletion came with the discovery of the Antarctic ozone hole. Over Earth’s poles during their respective winters, the stratosphere cools to very low temperatures and polar stratospheric clouds (PSCs) form. Chemical reactions of “reservoir” chlorine gases on these cloud particle surfaces convert the chlorine into highly reactive forms that rapidly destroy ozone – causing very large decreases in ozone concentrations over Antarctica and the Arctic.

Ozone levels have dropped by a worldwide average of about 4% since the late 1970s. For approximately 5% of the Earth’s surface, around the north and south poles, much larger seasonal declines have been seen. In response, the international community established the Montreal Protocol – a global agreement to phase out ozone-depleting substances (ODS). Without the Montreal Protocol, UV irradiance at northern and southern latitudes would have increased by 10-20% between 1996 and 2020.

Tropospheric ozone: the “bad” ozone at ground level

While stratospheric ozone is depleting above us, a different ozone problem is building below. Ground-level, or tropospheric ozone, is not emitted directly into the atmosphere. It is created by chemical reactions between oxides of nitrogen (NOₓ) and volatile organic compounds (VOCs) when pollutants emitted by cars, power plants, industrial boilers, refineries, chemical plants, and other sources chemically react in the presence of sunlight.

How tropospheric ozone forms

Tropospheric ozone is a powerful oxidant and major component of photochemical smog. It forms through complex chemical reactions involving ozone precursors – NOₓ and VOCs – in the presence of sunlight. Sources of these precursors can be either natural or anthropogenic, both contributing significantly to ambient ozone formation. Natural VOC sources include vegetation (particularly isoprene from tropical forests), while anthropogenic sources dominate in urban and industrial zones.

The reaction mechanism works like this: sunlight breaks down nitrogen dioxide (NO₂) into nitric oxide (NO) and a free oxygen atom. That oxygen atom combines with O₂ to form O₃. Under normal conditions, ozone would react back with NO and be destroyed – but VOCs and CO participate in complex photochemical reactions that produce free radicals which compete with ozone to react with NO. The net effects include the accumulation of ozone, the oxidation of VOCs into oxygenated organic compounds, and the formation of nitrogen-containing compounds – the whole mixture composed of ozone, secondary organic aerosols, and gaseous precursors is called photochemical smog.

Health and environmental consequences

Tropospheric ozone is a major component of smog. It can worsen bronchitis and emphysema, trigger asthma, and permanently damage lung tissue. Tropospheric ozone exposure is responsible for an estimated one million premature deaths each year. Children, the elderly, and people with lung or cardiovascular diseases are particularly at risk.

Beyond human health, the ecological damage is also significant. Estimated global crop production losses owing to ozone total 79-121 million tonnes, worth US$11-18 billion annually. Ozone damages plant cell membranes, reducing photosynthesis efficiency and crop yields – a compounding concern given rising global food demand.

Climate change is making the tropospheric ozone problem worse. High ozone levels are more likely to form in warmer temperatures – and because climate change is driving warmer temperatures, it is also leading to increased levels of ozone in many places. Climate change could exacerbate ozone pollution through enhanced natural precursor emissions, increased stratospheric-to-tropospheric exchange, stagnant weather patterns, and elevated methane and CO₂ levels.

Two ozone problems, one molecule

The ozone story presents a compelling environmental paradox. In the stratosphere, human activity has stripped away a layer that shields life from UV radiation. In the troposphere, those same industrial and transport emissions are creating excess ozone that damages lungs, crops, and ecosystems. The amounts of “good” stratospheric and “bad” tropospheric ozone depend on a balance between processes that create ozone and those that destroy it – and an upset in that balance has serious consequences for life on Earth.

Addressing both problems requires targeting the same root causes: the unchecked emission of industrial chemicals, combustion byproducts, and synthetic compounds. The success of the Montreal Protocol in beginning the recovery of the stratospheric ozone layer demonstrates that targeted international regulation can work. The ongoing challenge is applying the same urgency to ground-level ozone, where the American Lung Association identifies it as one of the least well-controlled and most dangerous pollutants currently affecting public health.

What do you think? Given that the same molecule – ozone – is both essential for life in the stratosphere and hazardous at ground level, how should environmental policy communicate this complexity to the public without causing confusion? And considering that tropospheric ozone is worsening with rising temperatures, do current clean air regulations go far enough to protect communities most vulnerable to air pollution?

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References
  1. https://earthobservatory.nasa.gov/features/Ozone/ozone_2.php
  2. https://ozone.unep.org/ozone-and-you
  3. https://www.lung.org/clean-air/outdoors/what-makes-air-unhealthy/ozone

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Environmental Chemistry

1 Environmental Chemistry-I

  1. Concept and Scope of Environmental Chemistry
  2. Fundamentals of Elemental Stoichiometry
  3. Chemical Equilibrium
  4. Chemical Potential
  5. Chemical Kinetics
  6. Simple Reaction Mechanisms
  7. Order and Molecularity of Chemical Reactions
  8. Chemical Reactions
  9. Catalysis
  10. Adsorption in Catalysis

2 Environment Chemistry-II

  1. Acid-Base Reactions
  2. Ionic Product of Water
  3. pH and pOH
  4. Hydrolysis
  5. Buffer Solutions
  6. Common Ion Effect
  7. Oxidation and Reduction

3 Environmental Chemistry-III

  1. Solubility and Solubility Product
  2. Solubility of Gases
  3. Carbonate System
  4. Chemical Speciation
  5. Chemistry of Heavy Metals
  6. Radionuclides
  7. Saturated and Unsaturated Hydrocarbons
  8. Chemistry of Fuels
  9. Lubricants
  10. Biogas

4 Developments In Environmental Chemistry

  1. Need for Emergence of Green Chemistry
  2. Some Important Laws for Environmental Protection
  3. Green Chemistry and Sustainability
  4. Greener Solvents
  5. Earth-Friendly Plastics
  6. Environmentally Benign Pesticides

5 Atmospheric Chemistry

  1. Origin of Atmosphere
  2. Composition of Atmosphere
  3. Structure of Atmosphere
  4. Atmospheric Stability
  5. Chemical and Photochemical Reactions in Atmosphere
  6. Distribution of Species in Atmosphere
  7. Reactions of Atmospheric Oxygen
  8. Reactions of Atmospheric Ozone
  9. Reactions of Nitrogen Oxides
  10. Particles in the Atmosphere

6 Water Chemistry

  1. Distribution of Water
  2. Chemistry of Water-Structure and Polarity
  3. Properties of Water
  4. Hydrology
  5. Sources and Uses of Water: The Hydrological Cycle
  6. Physical and Chemical Properties of Fresh Water and Sea Water
  7. Coagulation and Sedimentation
  8. Water Quality
  9. Chemical Species in Water
  10. Distribution of Gases in Water
  11. Organic Matter and Dissolved Humic Substances in Water

7 Soil Chemistry

  1. Origin and Nature
  2. Soil Formation
  3. Soil Chemical Properties
  4. Macro and Micronutrients in Soil
  5. Soil Fertility

8 Chemistry of Air Pollution-I

  1. Carbon Monoxide
  2. Carbon Dioxide
  3. Oxides of Nitrogen
  4. Sulphur Dioxide
  5. Ozone
  6. Acid Rain

9 Chemistry of Air Pollution-II

  1. Sources of Organic Air Pollutants
  2. Hydrocarbons as Pollutants
  3. Photochemical Smog
  4. Ozone Layer and its Depletion
  5. Reactions During Photochemical Smog
  6. Aerosols in Atmospheric Smog
  7. Ozone Destruction Mechanisms
  8. Ozone Destruction in Non-Polar Regions

10 Parameters of Water Pollution

  1. Aquatic System
  2. Dissolved Oxygen
  3. Biochemical Oxygen Demand (BOD)
  4. Chemical Oxygen Demand (COD)
  5. Acidity
  6. Alkalinity
  7. Acid-Base Chemistry in Natural Water: The Carbonate System
  8. Complexation and Chelation
  9. Colloidal Particles in Water
  10. Ion Exchange with Bottom Sediments
  11. Organic Compounds in Sediments and Suspended Matter

11 Chemistry of Hazardous Substances and Wastes

  1. Classification of Hazardous Substances and Wastes
  2. Combustible Waste: Physical and Chemical Properties
  3. Reactive Substances: Physical and Chemical Properties
  4. Corrosive Substances: Physical and Chemical Properties
  5. Toxic Substances: Physical and Chemical Properties

12 Basic Analytical Techniques

  1. Analytical Techniques: Importance
  2. Classification of Analytical Techniques
  3. Electrical Methods of Analysis
  4. Optical Methods of Analysis
  5. Evaluation of Analytical Data

13 Spectrometry

  1. UV-Vis Spectrophotometry
  2. IR Spectrometry
  3. Mass Spectrometry
  4. Environmental Applications of UV-Vis Spectrometry
  5. Environmental Applications of IR Spectrometry

14 Chromatography Techniques

  1. Gas-Liquid Chromatography
  2. High-Performance Liquid Chromatography
  3. Supercritical Fluid Chromatography
  4. Applications of Chromatography Techniques in Environmental Monitoring
  5. Types of High-Performance Liquid Chromatography

15 Radiochemical Techniques

  1. Basics of Radiochemical Techniques
  2. Carbon Dating
  3. Radioactive Labeling
  4. Tracer Technique
  5. Measuring Radiation: Geiger Muller and Scintillation Counters