Peter Sandman Website logo

divider bar

Appendix B

Risk Communication, Risk Statistics,
and Risk Comparisons:
A Manual for Plant Managers

by Vincent T. Covello, Peter M. Sandman, and Paul Slovic

(Washington, DC: Chemical Manufacturers Association, 1988), pp. 38–53

divider bar

Appendix B: Risk Comparison Tables And Figures

Tables

Figures

WARNING NOTES:

1. Since the data in these tables and figures have been calculated or assembled by others, their technical accuracy cannot be guaranteed. CMA makes no representations or warranties concerning their accuracy.

2. Some of the data are old and need to be updated. For some risks, this can make a significant difference, either because the risk itself has changed significantly or because its measurement has improved. In general, rates (e.g., number of deaths per million population) tend to change less over time than fatalities (counts).

3. It is not always clear what is included in the specific risk entries. For example, do deaths from smoking include cardiovascular disease and emphysema or just lung cancers? What is included in the categories “falling objects” or “toxic gas”? When in doubt, do not use the statistic.

4. Most tables of risk comparisons in the literature contain a hodgepodge of risks characterized by different levels of uncertainty. For risks such as driving, where fatalities can be counted, the number is likely to be reliable. But for risks such as radiation or food additives — based not on counting and actuarial statistics but on theoretical modeling and extrapolation — the number is likely to be highly uncertain. In general, data based on theoretical models and extrapolation are more likely to be a target for debate and criticism than data based on counts and actuarial statistics.

5. Most risk comparison tables offer only single number risk estimates, with no range or error term.

6. Most tables of risk comparisons in the literature have been developed to make a particular point. No matter how often the table has been reprinted, it is important to be sensitive to biases in the calculation of risks.

7. A careful risk comparison requires a good deal of background information about data sources, assumptions, and other qualifiers. Just because a risk statistic is published does not mean it is reliable. Published data often take on a life of their own. The original publication may discuss a number of qualifying uncertainties but these may be left out by the next person who reproduces the statistic. This may make the data look more certain, but in fact it makes them far less reliable. Keep in mind, however, that even if a risk estimate in a table is slightly off, it still could prove useful for comparisons in which risks differ by factors of 10, 100 or more.

8. The tables are often neither clear nor consistent about the population used to calculate the risk. Within the same table, some risk estimates are based on the entire population (e.g., the United States), while others are based only on the population that is exposed (e.g., only people who hunt or live in tornado-prone regions). Every risk looks more risky if only the most exposed population is considered, less risky if lots of unexposed people are considered.

9. Even if the risk comparison data are carefully and accurately reported, they can be misleading. For example, the risk calculation for driving includes many different driving situations. Yet speeding home from a party just before dawn is two orders of magnitude more dangerous than driving to the supermarket. Similarly, the risk of being hit by lightning for people who remain on a golf course during a thunderstorm is much higher than the risk for the U.S. population provided in these tables.

10. Risk comparisons raise all the same framing issues as risk quantification generally. That is, there are many different ways to express risk comparison data. Each of these expressions is likely to have a somewhat different impact on the audience.

11. The primary intent of these cautionary statements is to warn against casual acceptance of data in comparison tables, to emphasize the importance of acting fairly and responsibly in constructing comparisons, and to indicate the advisability of having someone carefully cross-check the comparison data. Whenever possible, avoid the use of secondary data sources. Track down the original source of the statistic and, if it seems accurate and appropriate, use that number.

12. Remember that a useful risk comparison must be accurate and appropriate. Comparing chemical plant risks to voluntary lifestyle choices such as smoking or driving without a seatbelt is seldom appropriate or successful, even if the comparison is technically accurate.

divider bar
back to top

Table B.1. Annual Risk of Death in
the United States


CauseRisk Per
Million Persons

Motor vehicle accidents (total)
Home accidents
Falls
Motor vehicle pedestrian collisions
Drowning
Fires
Inhalation and ingestion of objects
Firearms
Accidental poisoning
  Gases and vapors
   Solids and liquids (Not drugs or medicaments)
Electrocution
Tornadoes
Floods
Lightning
Tropical cyclones and hurricanes
Bites and stings by venomous animals and insects
240.0
110.0
62.0
42.0
36.0
28.0
15.0
10.0

7.7
6.0
5.3
.6
.6
.5
.3
.2

Source: Adapted from Wilson, R. and Crouch, E., Risk/Benefit Analysis, Cambridge: Ballinger, 1982.

Warning! Use of data in this table for risk comparison purposes
can damage your credibility (see text).

Illustrative Verbal Interpretation.
Every year approximately 60 persons per million die from falls in the United States. In a city of 100,000 persons, we could expect approximately 6 persons to die from falls annually. In the United States as a whole, we could expect approximately 15,000 deaths from falls per year.

 

divider bar
back to top

Table B.2: Annual Risk of Death
in the United States


HazardTotal Number
of Deaths
Risk Per
Million Persons

All causes
Heart Disease
Cancer
Motor vehicle accidents
Work Accidents
Homicides
Falls
Drowning
Fires, burns
Poisoning by solids or liquids
Suffocation, ingested objects
Firearms, sporting
Railroads
Civil aviation
Water transport
Poisoning by gases
Pleasure boating
Lightning
Hurricanes
Tornadoes
Bites and Stings
1,973,003
757,075
351,055
46,200
33,400
20,465
16,300
8,100
6,500
3,800
2,900
2,400
1,989
1,757
1,725
1,700
1,446
124
93
91
48
9000.0
3400.0
1600.0
210.0
150.0
93.0
74.0
37.0
30.0
17.0
13.0
11.0
9.0
8.0
7.0
7.0
6.0
.5
.4
.4
.2

Source: Adapted from Atallah, S., “Assessing and Managing Industrial Risk,” Chemical Engineering, September 8, 1980: 99–103.

2002 Note: Several numbers were incorrect in the original CMA publication and have been corrected here.

Warning! Use of data in this table for risk comparison purposes
can severely damage your credibility (see text).

Illustrative Verbal Interpretation.
Every year approximately 1,500 persons die in pleasure boating accidents in the United States. This represents six deaths per million persons. Of course, since everyone in the United States is not exposed to this risk, the rate per million boaters would be higher.

 

divider bar
back to top

Table B.3. Risk Comparisons
(Involuntary Risks Only)


RiskRisk of Death/
Person/Year

Influenza
Leukemia
Struck by an automobile (United Kingdom)
Struck by an automobile (United States)
Floods (United States)
Tornadoes (Midwest United States)
Earthquakes (California)
Bites of venomous creatures (United Kingdom)
Lightning (United Kingdom)
Falling aircraft (United States)
Release from nuclear power plant
  At site boundary (United States)
  At one kilometer (United Kingdom)
Flooding of dike (the Netherlands)
Explosion, pressure vehicle (United States)
Falling aircraft (United Kingdom)
Meteorite
1 in 5000
1 in 12,500
1 in 16,600
1 in 20,000
1 in 455,000
1 in 455,000
1 in 588,000
1 in 5 million
1 in 10 million
1 in 10 million
 
1 in 10 million
1 in 10 million
1 in 10 million
1 in 20 million
1 in 50 million
1 in 100 billion

Adapted from Dinman, B.D., “The Reality and Acceptance of Risk,” Journal of the American Medical Association, Vol. 244 (11): 1126–1128, 1980.

Warning! Use of data in this table for risk comparison purposes
can severely damage your credibility (see text).

Illustrative Verbal Interpretation.
The risk of tornadoes in the tornado-prone midwestern United States is 1 death per 455,000 persons per year, or about 2.2 deaths per million persons. This is much greater than the risk across the U.S. as a whole (.4 deaths per million persons per year — See Table B.2).

 

divider bar
back to top

Table B.4: Estimated Loss of
Life Expectancy Due to Various Causes


CauseDaysCauseDays

Cigarette smoking (male)
Heart disease
Being 30% overweight
Being a coal miner
Cancer
Being 20% Overweight
Cigarette smoking (female)
Stroke
Living in unfavorable state
Cigar smoking
Dangerous job (accidents)
Pipe smoking
Increasing food intake 100 calories/day
Motor vehicle accidents
Pneumonia (influenza)
Alcohol (U.S. average)
Accidents in home
Suicide
Diabetes
Being murdered (homicide)
Legal drug misuse
Average job (accidents)
Drowning
2250
2100
1300
1100
980
900
800
520
500
330
300
220
210
207
141
130
95
95
95
90
90
74
41
Job with radiation exposure
Falls
Accidents to Pedestrians
Safest job (accidents)
Fire (burns)
Generation of energy
Illicit drugs (U.S. average)
Poison (solid, liquid)
Suffocation
Firearms accidents
Natural radiation
Medical X rays
Poisonous gases
Coffee
Oral contraceptives
Accidents to bicycles
All catastrophes combined
Diet drinks
Reactor accidents (UCS)
Reactor accidents (NRC)
PAP test
Smoke alarm in home
Air bags in car
Mobile coronary care units
40
39
37
30
27
24
18
17
13
11
8
6
7
6
5
5
3.5
2
2 *
0.02*
-4
-10
-50
-125

Source: Adapted from Cohen, B. and Lee, I. “A Catalog of Risks.” Health Physics, 36, June, 1979, 707–722.

Notes: (*) These items assume that all U.S. power is nuclear. UCS stands for the Union of Concerned Scientists, a leading critic of nuclear power. NRC stands for the U.S. Nuclear Regulatory Commission.

Warning! Use of data in this table for risk comparison purposes
can severely damage your credibility (see text).

Illustrative Verbal Interpretation.
The average coal miner in the United States lives three years less than the national average. Although not indicated in the table, this is presumably due to the increased risk of accidents and disease (e.g., black and brown lung disease). However, other characteristics of coal miners, such as their smoking habits, diet, and access to medical care, may also affect this statistic.

 

divider bar
back to top

Table B.5: Risks Estimated to Increase the Probability of
Death in Any Year by One Chance in a Million


ActivityCause of Death

Smoking 1.4 cigarettes
Drinking .5 liter of wine
Spending 1 hour in a coal mine
Spending 3 hours in a coal mine
Living 2 days in New York or Boston
Traveling 6 minutes by canoe
Traveling 10 miles by bicycle
Traveling 300 miles by car
Flying 1000 miles by jet
Flying 6000 miles by jet
Living 2 months in Denver
Living 2 months in average stone or brick building
One chest X ray taken in a good hospital
Living 2 months with a cigarette smoker
Eating 40 tablespoons of peanut butter
Drinking Miami drinking water for 1 year
Drinking 30 12 oz cans of diet soda
Living 5 years at site boundary of a typical nuclear power plant
Drinking 1000 24-oz soft drinks from plastic bottles
Living 20 years near a polyvinyl chloride plant
Living 150 years within 20 miles of a nuclear power plant
Living 50 years within 5 miles of a nuclear power plant
Eating 100 charcoal-broiled steaks
cancer, heart disease
cirrhosis of the liver
black lung disease
accident
air pollution
accident
accident
accident
accident
cancer caused by cosmic radiation
cancer caused by cosmic radiation
cancer caused by natural radioactivity
cancer caused by radiation
cancer, heart disease
liver cancer caused by aflatoxin B
cancer caused by chloroform
cancer caused by saccharin
cancer caused by radiation
cancer from acrylonitrile monomer
cancer caused by vinyl chloride (1976 standard)
cancer caused by radiation
cancer caused by radiation
cancer from benzopyrene

Source: Adapted from Wilson, R., “Analyzing the Daily Risks of Life.” Technology Review, 81, 1979, pp. 40–46.

Note: These data are based on simple extrapolations from population averages. Some data are based on actuarial statistics (e.g., coal mine accidents) and others are based on theoretical models (e.g., cancers from chlorinated water).

Warning! Use of data in this table for risk comparison purposes
can severely damage your credibility (see text).

 

divider bar
back to top

Table B.6: Average Risk of Death to an Individual
from Various Natural and Human-caused Accidents


Accident
Type
Total  
Number
Individual Chance
Per Year

Motor Vehicle
Falls
Fires and Hot Substances
Drowning
Firearms
Air Travel
Falling Objects
Electrocution
Lightning
Tornadoes
Hurricanes
All Accidents
55,791
17,827
7,451
6,181
2,309
1,778
1,271
1,148
160
91
93
111,992
1 in 4,000
1 in 10,000
1 in 25,000
1 in 30,000
1 in 100,000
1 in 100,000
1 in 160,000
1 in 160,000
1 in 2,000,000
1 in 2,500,000
1 in 2,500,000
1 in 1,600

Source: Nuclear Regulatory Commission, Reactor Safety Study, WASH–1400 (NUREG/74/104), Washington, D.C., 1975.

Warning! Use of data in this table for risk comparison purposes
can severely damage your credibility (see text).

 

divider bar
back to top

Table B.7: Average Risk of Death from
Various Human-caused and Natural Accidents


Type of EventProbability of 100 or
More Fatalities
Probability of 1,000 or
More Fatalities

Human-caused
Airplane Crash
Fire
Explosion
Toxic Gas
1 in 2 yrs.
1 in 7 yrs.
1 in 16 yrs.
1 in 100 yrs.
1 in 2,000 yrs.
1 in 200 yrs.
1 in 120 yrs.
1 in 1,000 yrs.
Natural
Tornado
Hurricane
Earthquake
Meteorite Impact
1 in 5 yrs.
1 in 5 yrs.
1 in 20 yrs.
1 in 100,000 yrs.
very small
1 in 25 yrs.
1 in 50 yrs.
1 in 1 million yrs.

Source: Nuclear Regulatory Commission, Reactor Safety Study, WASH–1400 (NUREG/74/104), Washington, D.C., 1975.

Warning! Use of data in this table for risk comparison purposes
can severely damage your credibility (see text).

 

divider bar
back to top

Table B.8. Ranking of Possible Cancer Risks
from Common Substances


RankingRisk Source

0.2 PCBs (daily dietary intake): exposure through industrial residues
0.3 DDE/DDT (daily dietary intake): exposure through pesiticide residues; DDE is a by-product of DDT
1 Tap water (1 liter a day): contains chloroform, a by-product of chlorination
3 Cooked bacon (100 g/about 15 slices a day): contains dimethylnitrosamine, a preservative by-product
4 Contaminated well water (1 liter a day): from worst well in Silicon Valley; contains trichloroethylene
4 EDB (daily dietary intake): exposure through pesticide and other residues in grains and grain products
8 Swimming pool (1 hour a day for a child): exposure to chloroform by swallowing chlorinated water
30 Peanut butter (32 g/2 tablespoons a day): contains aflatoxin, a natural mold
30 Comfrey herb tea (1 cup a day): contains symphytine, a natural pesticide
60 Diet cola (12 ounces a day): contains saccharin
100 Raw mushroom (1 a day): contains hydrazines, natural pesticides
100 Dried basil (1 g of dried leaf): contains estragole, a natural pesticide
300 Phenacetin pill (average dose): ingredient in pain reliever
600 Indoor air (homes) (14 hours a day): formaldehyde emitted from furniture, carpets, and wall coverings
2,800 Beer (12 ounces a day): contains ethyl alcohol
4,700 Wine (250 ml/8 ounces a day): contains ethyl alchohol
5,800 Formaldehyde (6.1 mg/worker’s average daily intake): exposure through inhalation
16,000 Phenobarbitol (1 pill a day): a sleeping pill
140,000 EDB (150 mg/worker’s daily intake at high exposure): exposure through inhalation; worker’s maximum legal exposure

Source: Adapted from Ames, B.N., Magaw, R., and Gold, L.S., “Ranking Possible Carcinogenic Hazards,” Science, 1987, Vol. 236, (17 April 1987), 27 1–285; and J. Tierney (1988), “Not to Worry...,” Hippocrates, January/February 1988, pp. 29–38.

Warning! Use of data in this table for risk comparison purposes
can severely damage your credibility (see text).

Illustrative Verbal Interpretation.
The risk from industrial formaldehyde is 5,800 times greater than the risk from tap water.

 

divider bar
back to top

Figure B.1: Health Risk Ladder
Annual Number of Deaths per Million People

b-1.gif - 11291 Bytes
Source: Adapted from Schultz, W., G. McClelland, B. Hurd, and J. Smith (1986), Improving Accuracy and Reducing Costs of Environmental Benefits Assessment, Vol. IV. Boulder: University of Colorado, Center for Economic Analysis.

Warning! Use of data in this figure for risk comparison purposes
can severely damage your credibility (see text).

 

divider bar
back to top

Figure B.2: Upper Bound Estimates of Deaths
for Different Energy Systems

Image not available

Source: Adapted from Inhaber, H. (1979), “Risks with energy from conventional and non-conventional sources.” Science, 203, 1979, 718–723. Also Inhaber, H., Risk of Energy Production, Report No. AECB 119/rev. 3, 4th edition. Ottawa: Atomic Energy Control Board, 1979.

Warning! Use of data in this figure for risk comparison purposes
can severely damage your credibility (see text).

 

divider bar
back to top

Figure B.3: Comparisons of Different Sources
of Radiation Exposure

b-3.gif - 8593 Bytes

Source: Adapted from the National Radiological Protection Board (1986), Living with Radiation, London: HMSO.

Warning! Use of data in this figure for risk comparison purposes
can severely damage your credibility (see text).

 

divider bar
back to top

Figure B.4: The Causes of Cancer: Quantitative Estimates of the Avoidable Risk of Cancer in the U.S.

b-4.gif - 17097 Bytes

Note: Due to rounding error, percentage figures do not add up to one hundred percent.

Source: Adapted from Doll, R. and Peto, R. (1981), “The Causes of Cancer: Quantitative Estimates of the Avoidable Risk of Cancer in the U.S. Today.” Journal of the National Cancer Institute, 1981, Vol. 66, 1191–1308.

Warning! Use of data in this figure for risk comparison purposes
can severely damage your credibility (see text).

 

divider bar
back to top

Figure B.5: Radon Risk Charts

Image not available

Source: Adapted from Smith, V.K., W.D. Desvousges, and A. Fisher (1987), Communicating Radon Risk Effectively: A Mid-Course Evaluation, Report No. CR–811075. Washington, D.C.: U.S. Environmental Protection Agency, Office of Policy Analysis.

Warning! Use of data in this figure for risk comparison purposes
can severely damage your credibility (see text).

 

divider bar

Next Section

   ball   Introduction and Index
   ball   I . Effectively Communicating Risk Information
   ball   II. Guidelines for Presenting and Explaining Risk-Related Numbers and Statistics
   ball   III. Guidelines for Providing and Explaining Risk Comparisons
   ball   IV. Concrete Examples of Risk Comparisons
   ball   V. Anticipating Objections to Explanations of Chemical Risks
   ball   Conclusion
   ball   Acknowledgements
   ball   Appendix A: Concentration and Quantity Comparisons
   ball   Appendix B: Risk Comparison Tables And Figures
   ball   Appendix C: Risk Perception Factors
   ball   Selected Bibiliography on Risk Communication

Back to articles list

blue-bar.jpg - 2595 Bytes

Comment or Ask       Read the comments

Peter M. Sandman
59 Ridgeview Rd.
Princeton NJ 08540-7601
Phone: 1-609-683-4073
Fax: 1-609-683-0566
Email: peter@psandman.com
home link

Website design and management provided by SnowTao Editing Services.
bar