Causation

Causation
HRISTINA VLAJINAC
Institute of Epidemiology, School of Medicine,
University of Belgrade, Belgrade, Serbia
kristiv@eunet.yu
Synonyms
Causality
Definition
A cause of a disease can be defined as an event, condition,
or characteristic that plays an essential role in producing
an occurrence of the disease (Rothman 1986).
The most important aim of epidemiology is to identify
the causes and the  risk factors of a disease, and to
improve public health by reducing or eliminating exposure
to these factors.
Basic Characteristics
Epidemiological – EcologicalModels
A disease is a result of the  interaction of host factors
and the environment. Several models have been developed
in order to depict the ways in which these interactions
influence the occurrence of the disease: the triangle,
the wheel, and the web of causation.
The triangle – Thismodel consists of three components,
 agent, host, and environment, which are in a kind of
dynamic equilibrium. Change in any of these components
will alter an existing equilibrium and increase or
decrease the frequency of the disease. This model has
been the most frequently applied to infectious diseases
in which infectious organismswere separated from other
environmental factors and identified as agents.
For diseases that have not been linked to specific agents,
two other models have been developed.
The Wheel – In this model, the host, with its genetic
make-up as its core, is presented as the hub of the
wheel, surrounded with the environment, which is separated
into biological, social and physical components.
This separation is artificial since these three parts of the
environment are closely interrelated with one another
and with host factors.
The Web – The web model emphasizes the concept that
effects never depend on single causes but develop as the
result of causal chains, which make the web. Each link
in the web is the result of antecedents, and breaking
of the web at any level can prevent occurrence of the
disease. This means that full knowledge of etiology is
not needed for effective disease prevention and control.
(Mausner, Kramer 1985; Bhopal 2002)
Search for Causal Relationship
There are two approaches to testing hypotheses about
causes of disease, experimental and observational.
Experimental study can establish the causal relationship
of a factor with a disease more conclusively, but
since experiments in epidemiology are performed on
humans, for ethical reasons the effects of some possible
causal factors cannot be investigated directly.
Observational studies have therefore been providing the
major contribution to the understanding of many diseases.
The first step in an investigation of causal relationship
is to see whether there is an  association between
a disease and a postulated causal factor. If an association
exists, it does not necessarily mean that it is
a causal one. It can be: a) spurious ( spurious association),
b) secondary ( secondary association), or c)
causal. Before an association is assessed for the possibility
that it is causal, other alternative explanations,
such as chance, selection bias, information bias, and
confounding, have to be excluded.
A Concept of Necessary and Sufficient Cause
“A causal factor whose presence is required for the
occurrence of the effect” (Last 2001), that is, without
which the disease never develops, is the necessary
cause. Sufficient cause is a “minimum set of conditions,
factors or events needed to produce a given outcome;
minimal implies that none of the conditions or events is
superfluous” (Rothman 1986). A sufficient cause is not
usually a single factor, but often comprises several components
– component causes or contributing causes.
A disease can have several sufficient causes and these
may have one or more contributing causes in common.
Types of Causal Relationship A causal factor can be
either necessary or sufficient, both, or neither:
1. Necessary and sufficient
A factor can be both necessary and sufficient, which
means that the disease never develops without that factor,
and that factor always produces the development
of the disease. This type of causal relationship occurs
rarely. For example, a person who has three copies of
chromosome 21 instead of two will inevitably be mentally
retarded – Down’s syndrome (Bhopal 2002).
2. Necessary but not sufficient
The factor, although necessary, cannot produce the disease
without the presence of some other factors, called
component or contributory causes. For clinically manifest
tuberculosis, in addition to the bacillus, which is
the necessary cause, contributing causes such as poor
nutritional and socio-economic conditions are needed.
3. Sufficient but not necessary
Although sufficient for producing the disease, the factor
(usually more than one) is not necessary because there
are some other factors that can also produce the disease.
Either radiation exposure or benzene exposure can
produce leukemia independently of each other (Gordis
2004).
4. Neither sufficient nor necessary
Smoking is a cause of lung cancer but not everyonewho
smokes develops this type of cancer and not everyone
who develops lung cancer has smoked.
Guidelines for Causal Reasoning in Epidemiology
Although epidemiologic evidence by itself is insufficient
to establish causality, Bradford Hill (Hill, 1965)
suggested that the following attributes (criteria) of an
association be considered in assessment of the possibility
that it is a causal one.
1. Strength of the association – The strength of association
is measured by the relative risk (odds ratio), that is
the ratio of disease rates for those exposed and those not
exposed to the hypothesized causal factor. The stronger
the association, the more likely it is that the relation is
causal. However, it does not mean that a weak association
cannot be judged to be a causal one. “The strength
of an association is not a biologically consistent feature,
but rather a characteristic that depends on the relative
prevalence of other causes” (Rothman, 1986).
2. Dose-response relationship – A dose-response is
established when, with increasing level of exposure
(“dose” or duration), the risk of disease also increases.
The absence of a dose-response relationship does not
rule out the possibility of causal association since, for
some causes, a threshold may exist and a disease may
not develop unless a certain level of exposure is present.
3. Consistency of the association – A cause-effect relationship
is supported when similar results are obtained
in a number of studies performed in various populations
or population groups, by different investigators,
and with different methodology. The causal relationship
might not be found in some studies because “the
effect of a causal agent cannot occur unless the component
causes act, or have already acted, to complete
a sufficient cause” (Rothman 1986).
4. Temporality – Exposure to the postulated causal factor
must precede the onset of disease by a period of
time consistent with the proposed biologic mechanism
( induction,  incubation,  latency). In some diseases,
especially chronic and those with a long period
of latency, temporality cannot always be easy to establish.
Although the only indispensable attribute among
all Hill’s conditions, a temporally correct association
between two events does not necessarily mean that it is
that of cause and effect. They could both be generated
by the same factor.
5. Biologic plausibility – The existence of a causeeffect
relationship is enhanced if it is coherent with the
current body of biologic knowledge. This, of course,
depends on the state of scientific information at a given
time. An association that is biologically implausible at
one time may eventually prove to be plausible.
6. Experimental evidence – Causal understanding can
be greatly advanced by “in-vivo” and animal experiments,
but data obtained in that way must be integrated
with observations in the human population. Because of
ethical reasons, experimental evidence is seldom from
the human population. However, evidence for a causal
relationship is supported if reduction or elimination of
exposure to a certain factor (postulated causal factor) is
related to decline of disease frequency.
7. Coherence – Coherence implies that a cause-effect
interpretation of an association does not conflict with
the generally known facts of the natural history and
biology of the disease.
8. Specificity of the association – An association is
specific when a certain exposure is associated with
only one disease. Taking into account the multifactorial
nature of disease and the fact that one factor can
cause more than one disease, the specificity is the least
important criterion to satisfy, and “should be probably
deleted from the list” (Gordis 2004).
In making decisions about causation, the list of criteria
presented above should be considered only as guidelines.
If temporality is viewed as part of the definition
of causation, “there is no necessary or sufficient criterion
for determining whether an observed association is
causal” (Rothman, Greenland 1998; Rothman, Greenland
2005). Decisions about causation must always
remain a matter of judgment based on all available evidence
“achievable through hypothesis generation and
testing, with data interpreted using a logical framework
of analysis, which draws on multidisciplinary perspectives”
(Bhopal 2002).
Hill himself pointed out that these “viewpoints” cannot
be used as criteria for causal inference, but can help
to make a judgment, and to act on the premise that
a causal relationship exists rather than awaiting further
evidence: “All scientific work is incomplete – whether it
be observational or experimental. All scientific work is
liable to be upset or modified by advancing knowledge.
That does not confer upon us a freedom to ignore the
knowledge we already have, or to postpone the action
that it appears to demand at a given time”.
Most definitions are taken from the last edition of Last’s
Dictionary of Epidemiology (Last, 2001).We are much
obliged to Professor Last for his kind consent.
Cross-References
 Agent (of Disease)
 Association
 Incubation
 Induction
 Interaction
 Latency
 Risk Factor
 Secondary Association
 Spurious Association
References
Bhopal R (2002) Concepts of Epidemiology: An integrated introduction
to the ideas, theories, principles and methods of epidemiology.
Oxford University Press, Oxford
Gordis L (2004) Epidemiology. Elsevier Saunders, Philadelphia
Hill B (1965) The environment and disease: Association or causation.
Proc Roy Soc Med 58:295–300
Last J (2001) A Dictionary of Epidemiology, 4th edn. Oxford
University Press, New York
Mausner J, Kramer S (1985) Epidemiology. WB Saunders,
Philadelphia
Rothman K (1986) Modern Epidemiology. Little Brown, Boston
Rothman K, Greenland S (1998) Modern Epidemiology, 2nd edn.
Lippincott – Raven Publishers, Philadelphia
Rothman K, Greenland S (2005) Basic Concept. In: Ahrens W,
Pigeot I (ed) Handbook of Epidemiology. Springer, Berlin,
pp 45–

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Biostatistical Software

Biostatistical Software
NIKOLA KOCEV
Institute for Medical Statistics and Informatics, School
of Medicine, University of Belgrade, Belgrade, Serbia
nkocev@EUnet.yu
Synonyms
Statistical software; Statistical packages
Definition
Biostatistics – is the application of statistics to the analysis
of biological and  medical data. Biostatistical
software is a suite of computer programs specialized
for statistical analysis of biological and medical data. It
enables people to obtain the results of standard statistical
procedures and statistical significance tests, without
requiring low-level numerical programming. Most
statistical packages also provide facilities for data management.
Basic Characteristics
Nowadays, very often, biostatistics uses general statistical
packages, which include many procedures that are
seldom used in the solution of biostatistical problems.
Statistical software used for biostatistics’ problems
should encompass routine procedures, such as:  data
entry and data management; summarizing information
from data in tables and graphs and summary statistics;
probability, probability distribution, randomization of
patients, sufficient sample size to have adequate statistical
power; for making inference from data: confidence
intervals and hypothesis test; specifying α – type error
I, β – type error II and  power analysis; estimating
and comparing mean or differences in mean; comparing
three or more means (ANOVA); estimating and comparing
proportions; associations and prediction; statistical
methods (parametric and nonparametric) for analyzing
survival data; statistical methods for multiple
variables; evaluating diagnostic procedures, time series
analysis, etc.
Bearing in mind that different statistical software’s contain
routine procedures more developed than other software’s,
we are frequently compelled to use more than
one statistical package in the process of solving one particular
biostatistics’ problem. Also, given the moment
in time that we are all living in, statistical software’s
tend to become rapidly outdated forcing software vendors
to continually update and correct their product
(often issuing patches or service releases that correct
errors and bugs). Consequently, buyers – via vendor’s
web sites – can provide themselves with information
regarding errors, bugs, macros and add-ons that extend
the capability of the basic package. The same way, they
are offered the possibility of a free 30-day trial of fully
functional new version which enables them to test them
with their own biostatistics’ problems.
All in all, there are no  data management packages
available on the market which are designed and
optimized for biostatics’ softwares, nevertheless, each
package comes with the data entry and data management
options and it is their functionality that permits
data adjustments for particular statistics’ routine procedures
and for connection with the existing database
systems.
Statistical Software
for Successful Biostatistics’ Problem-Solving
For a successful biostatistics’ problem-solving, it is
possible to use one of the commercial packages, general
public license packages, analysis packages with statistics
add-ons, as well as some general purpose languages
with statistics libraries. Consistent with that, some of
the aforementioned are described later.
SAS/STAT® Software
(www.sas.com)
From traditional analysis of variance and predictive
modeling to exact methods and  statistical visualization
techniques, SAS/STAT software provides tools for
both specialized and enterprizewide analytical needs.
Key features: analysis of variance, regression, categorical
data analysis, multivariate analysis, survival analysis,
psychometric analysis, cluster analysis, nonparametric
analysis, survey data analysis, multiple imputation
for missing values, study planning.
SAS/ETS contains popular forecasting methods such
as regression analysis, trend extrapolation, exponential
smoothing, Winter’s method (additive and multiplicative),
ARIMA (Box-Jenkins) and dynamic or transfer
function models.

JMP
(http://www.jmp.com/)
SAS created the JMP desktop statistical discovery software,
that uses a structured, problem-centered approach
for exploring and analyzing data. The intelligent interface
guides users to the adequate analyzes. JMP automatically
displays graphs with statistics, enabling users
to visualize and uncover data patterns.
BMDP
(http://www.statsol.ie/html/bmdp/bmdp_home.
html)
BMDP has its roots as biomedical analysis packages
from the late 1960s. It is a comprehensive library
of statistical routines from simple data description
to advanced multivariate analysis, and is backed by
extensive documentation. Each individual BMDP subprogram
is based on the most competitive algorithms
available and has been rigorously field-tested. The
BMDP package contains over 40 interrelated statistical
programs. All of the programs share common instructions
and convenience features to save time and effort.
SPSS
(www.spss.com)
Data Analysis with Comprehensive Statistics Software,
statistical and  data management package for analysts
and researchers. SPSS forWindows is a modular, tightly
integrated, full-featured product line for the analytical
process – planning, data collecting, data access,
data management and preparation, data analysis, reporting,
and deployment. Using a combination of add-on
modules and stand-alone software that work seamlessly
with SPSS Base enhances the capabilities of this statistics
software. The SPSS Programmability Extension™
enables analytic and application developers to extend
the SPSS command syntax language to create procedures
and applications – and perform even the most
complex jobs – within SPSS.
StatSoft STATISTICA
(http://www.statsoft.com)
StatSoft’s flagship product line is the STATISTICA
suite of analytic software products. STATISTICA provides
the most comprehensive array of data analysis,
data management, data visualization, and data mining
procedures. Its techniques include the widest selection
of predictive modeling, clustering, classification, and
exploratory techniques in one software platform. The
STATISTICA Visual Basic language that can be used
to write custom extensions.
NCSS and PASS
(Statistical & Power Analysis Software)
(www.ncss.com)
NCSS software provides a complete, easy-to-use collection
of over 200 statistical and graphics tools to analyze
and visualize data.
PASS ( power analysis and Sample Size) software is
an easy-to-use research tool for determining the number
of subjects that should be used in a study, performs
power analysis and calculates sample sizes for over 150
statistical tests.
Mathematica,WOLFRAM RESEARCH
(http://www.wolfram.com/)
Mathematica’s statistics capabilities are part of Mathematica’s
standard add-on packages. Like any statistics
package, Mathematica provides a numerical and graphical
toolset to illustrate, simulate, and find approximate
numeric solutions to numerical problems.
Matlab
(http://www.mathworks.com/)
MATLAB® is a high-performance language for technical
computing. It integrates computation, visualization,
and programming in an easy-to-use environment where
problems and solutions are expressed in familiar mathematical
notation.
The Statistics Toolbox, for use with MATLAB®, is
a collection of statistical tools built on the MATLAB
numeric computing environment. The toolbox supports
a wide range of common statistical tasks, from random
number generation, to curve fitting, to design of experiments
and statistical process control. The toolbox provides
two categories of tools: Building-block probability
and statistics functions and Graphical, interactive
tools. The first category of tools is made up of functions
that can be called up from the command line or
from an individual’s own applications. Many of these

functions are MATLAB M-files, series of MATLAB
statements that implement specialized statistics algorithms.
R Project for Statistical Computing
(http://www.r-project.org/)
R is a language and environment for statistical computing
and graphics. It is a GNU project which is similar
to the S language and environment which was developed
at Bell Laboratories (formerly AT&T, now Lucent
Technologies) by John Chambers and colleagues. R can
be considered as a different implementation of S. There
are some important differences, but much code written
for S runs unaltered under R. R provides a broad variety
of statistical (linear and nonlinear modeling, classical
statistical tests, time-series analysis, classification,
clustering, etc.) and graphical techniques, and is highly
extensible. The S language is often the vehicle of choice
for research in statistical methodology, and R provides
an Open Source route to participation in that activity. R
is available as Free Software under the terms of the Free
Software Foundation’s GNU General Public License in
source code form.
Free Statistical Software
(http://statpages.org/javasta2.html)
This page contains links to free software packages
that can be downloaded and installed onto a computer
for stand-alone (offline, non-Internet) computing. They
are listed below, under the following general headings:
General Packages: support a wide variety of statistical
analyses; Subset Packages: deal with a specific
area of analysis, or a limited set of tests; Curve
Fitting and Modeling: to handle complex, nonlinear
models and systems; Biostatistics and Epidemiology:
especially useful in the life sciences; Surveys, Testing
andMeasurement: especially useful in the business and
social sciences; Excel Spreadsheets and Add-ins: need
a recent version of Excel; Programming Languages and
Subroutine Libraries: customized for statistical calculations;
need to learn the appropriate syntax; Scripts
and Macros: for scriptable packages, like SAS, SPSS,
R, etc.; Miscellaneous: do not fit into any of the other
categories; Other Collections of Links to Free Software.
Cross-References
 Data Entry
 Data Management Packages
 Medical Data
 Power Analysis
 Statistical Procedure
 Statistical Visualization Techniques
Reference
Statistics at George Mason University. A Guide to Statistical
Software 1998 Version | 2005 Version. http://www.galaxy.
gmu.edu/. Accessed 2007

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Bias

ZORANA GLEDOVI´C
Institute of Epidemiology, School of Medicine,
University of Belgrade, Belgrade, Serbia
gledovic@sezampro.yu
Synonyms
Bias: Systematic error; Confounding: Bias due to confounding;
Interaction: Effect modification
Definition
The important issues in deriving causal inferences are:
bias, confounding and interaction.
“Bias can be defined as deviation of results or inferences
from the truth, or processes leading to such deviation”.
“Confounding is a situation in which the effects of two
processes are not separated”.
“Interaction is the interdependent operation of two or
more causes to produce or prevent an effect” (Last
2001).
Basic Characteristics
The goal of an epidemiological study is  accuracy
in measurement. Epidemiological studies are prone to
 error. Errors can be either random or systematic.
Since the errors can never be eliminated,much attention
is devoted to minimize them, and to assess their importance.
The principles of study design emerge from consideration
of approaches to reduce both types of errors.
Random error is the divergence, due to chance alone,
of an observation on a sample, from the true population
value, leading to lack of precision in themeasurement
of an association. Sources of random error are: individual
biological variation, sampling error and measurement
error (Bhopal 2002). Random error can never be
completely eliminated. The best way to reduce it is to
increase the size of the study.
Validity
The validity of a study is usually separated into two
components: internal validity and external validity.
Internal validity implies that the index and comparison
groups are selected and compared in such a manner, that observed differences between them on dependent variables
under study may be attributed only to the hypothesized
effect under consideration.
External validity concerns validity of the inferences as
they pertain to people outside the study population.
External validity depends on internal validity, which is
its prerequisite, but it depends also on the results of other
studies, theoretical knowledge of the disease process
and related factors, and biological considerations.
Internal validity is the degree to which the results of
an observation are correct for the particular group of
people being studied. Internal validity can be threatened
by all sources of systematic error (bias) but can
be improved by good design of a study (Rothman and
Greenland 1998).
There are three main types of biases: selection bias,
information bias and confounding.
Selection Bias
Selection bias occurs when there is a systematic difference
between characteristics of the people selected
for a study and the characteristics of those who are not.
There are a number of reasons for the occurrence of
this type of bias. Common feature for all of them is that
the relationship between the  exposure and disease
observed among those who participate in the study is
different from that for the individuals who would have
been eligible to participate but were unwilling or not
selected by the investigator (Rothman and Greenland
1998).
Example: Selection bias can occur if investigators
include hospital cases or cases under a physician’s care
and exclude those who die before admission to hospital
because the course of their disease was severe, those
with mild symptoms not requiring hospital care, cost of
hospital treatment or other factors.
Information Bias
Information bias occurs whenever the study subjects are
erroneously categorized with respect to either exposure
or disease. The effect of this bias depends on whether
this misclassification is differential or non-differential
(Rothman and Greenland 1998).
Differential misclassification occurs when the proportion
of subjects misclassified differ between the study
groups. It can occur when there is any systematic difference
in the soliciting, recording or interpreting of information
from study participants.
Example: Mothers whose children have had or have
died of leukemia are more likely than mothers of
healthy children (control group in a  case-control
study) to remember details of diagnostic x-ray examinations
to which these children were exposed in utero
(recall bias).
The effect of differential misclassification is overestimation
of an association even if it does not really exists,
or underestimation or lack of an association when it
really exists.
Non-differential misclassification occurs when inaccuracies
in the categorization of subjects by exposure
or disease are present in similar proportion in each
of the study group. Such misclassification is often
present because of inaccuracy of most measurements
in biomedicine.
Non-differentialmisclassification almost always results
in an underestimate of the true strength of the association.
Some degree of this misclassification is present
in almost all types of epidemiological studies and this
bias may account for some apparent differences in the
results of epidemiological studies (Hennekens and Buring
1987).
The control of potential biases must be accomplished
by careful study design. Some of design features that
can minimize potential biases are: carefully prepared
questionnaire (close-ended questions), clearly written
protocol, trained study personnel, the use of multiple
sources of data whenever possible etc.
Confounding
The word confounding is derived from a Latin word
meaning to mix up. The word’s meaning in everyday
language is to confuse or puzzle. Confounding mixes
up causal and non-causal relationships.
Confounding is a major cause of bias in epidemiology,
and the more difficult one to understand. The
potential for it to occur is whenever the cardinal rule’
compare like-with-like’ is broken. This rule is perhaps
never attained except in experimental research. Comparing
like-with-like may be achieved in experimental
studies where subjects can be randomly allocated to
one group or another, a technique which employs the
laws of chance to create comparable groups (Bhopal
2002).
Confounding is one of the most important problems in
observational studies.
Example: In a study of mortality rates, investigators
find that mortality rates in an English seaside resort are
much higher than in a country as a whole. Why might
this be so?
One possible explanation:
A holiday town attracts the elderly, so has a comparatively
old population.
What is confounding factor in this example?
Age, which is associated with both living in a resort and
with death.
The Control of Confounding
Several methods are available to control confounding,
either through study design or during the analysis of
the results (Hennekens and Buring 1987; Rothman and
Greenland 1998)
The Control of Confounding in Study Design
 Randomization is applicable only in experimental
studies. It is method which ensures that potential confounding
variables are equally distributed among the
groups being compared.
 Restriction is used to limit the study to people who
have particular characteristics. For example, in a study
on the effects of coffee on pancreatic cancer, participation
in the study could be restricted to nonsmokers,
thus removing any potential effect of confounding by
cigarette smoking.
Matching ensures that study participants are selected
so that potential confounding variables are evenly distributed
in the groups being compared. For example in
a case-control study each patient with a disease can be
matched with a control of the same sex and age group to
ensure that confounding by sex and age does not occur.
Control of Confounding in the Analysis of Results
 Stratification involves the measurement of the
strength of association in well-defined and homogeneous
categories (strata) of the confounding variable.
If the confounding variable is age, the association may
be measured in 10-year age groups. Stratification is
often limited by the size of the study and it cannot help
to control many factors simultaneously. In this situation,
mathematical modeling is required to estimate the
strength of the associations while controlling for a number
of confounding variables.
The multivariate modeling involves  logistic model
and analysis of covariance (Rothman and Greenland
1998).
Interaction
According to MacMahon interaction can be defined as
follows: “When the  incidence rate of disease in the
presence of two or more risk factors differs from the
incidence rate expected to result from their individual
effects” (MacMahon 1972). The effect can be grater
than that we would expect (positive interaction,  synergism)
or less than what we would expect (negative
interaction,  antagonism).
The problem is to determine what we would expect to
result from the individual effects of the exposures.
In exploring the possibility of interaction, the first question
is whether an association between exposure and
a disease exists. If it exist, is it due to confounding? If
it is causal, is it equally strong in each of the strata that
are formed on the basis of some other variable? (Gordis
2004).
Example: If the association of smoking and lung cancer
is equally strong in all strata formed on the basis
of degree of urbanization, there is no interaction. But if
the association is of different strength in different strata
formed on the basis of age, there is interaction.
Conclusion
Biases reflect inadequacies in the design or conduct of
a study and affect its validity. Because of that, biases
need to be assessed and, if possible, eliminated, while
confounding and interaction describe the reality of the
relationships between certain factors and a certain outcome
(Gordis 2004). Such relationships are particularly
important in investigating the role of various factors in
disease causation.
Cross-References
 Accuracy
 Antagonism
 Case Control Studies
 Error
 Incidence Rate
 Logistic Model
 Matching
 Precision
 Questionnaire
 Randomization
 Restriction
 Stratification
 Synergism
References
Bhopal R (2002) Concepts of Epidemiology: An integrated introduction
to the ideas, theories, principles and methods of epidemiology.
Oxford University Press, Oxford
Gordis L (2004) Epidemiology, 3rd edn. Elsevier-Saunders,
Philadelphia
Hennekens CH, Buring JE (1987) Epidemiology in Medicine.
Little, Brown and Company, Boston, Toronto, pp 4–8
Last JM (2001) A Dictionary of Epidemiology, 4th edn. Oxford
University Press, New York
MacMahon B (1972) Concepts of multiple factors. In: Lee DH,
Korin P (eds) Multiple Factors in the Causation of Environmentally
Induced Disease. Academic Press New York, New
York
Rothman KJ, Greenland S (1998) Modern Epidemiology, 2nd
edn. Lippincot-Raven, Philadelphi

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Air Quality and Pollution

Air Quality and Pollution
ZORAN MARMUT
Institute of Hygiene and Medical Ecology, Faculty
of Medicine, University of Belgrade, Belgrade, Serbia
zmarmut@eunet.yu
Definition
Air quality refers to the physical, chemical, and biological
characteristics of air, both in outside space and in
enclosed spaces, such as most industrial settings, other
non-industrialworking places, and residencies. Air pollution
is the abnormal presence of various substances
(gases, vapors or particles) in the air in sufficient concentrations
such that accumulated substances lead to
poor air quality and affect human health, living matter
and other materials. These substances may be released
into the air by natural processes or by human activities.
Basic Characteristics
Air is a mixture of gases, water vapor, solid and liquid
airborne particles in a wide range of concentrations that
range from essential for life to chemically inert. Some
of them are even hazardous, but are normally present
in low concentrations. Air is what constitutes Earth’s
atmosphere and it is present as an almost transparent,
thin envelope around our planet. The atmosphere significantly
determines the necessary conditions for various
forms of life on Earth, and also shapes and modifies
the subtle combination of environmental factors that we
call climate.
The normal chemical composition of dry air in the
troposphere is as follows: major gases are nitrogen
and oxygen (78,09% and 20,94%, respectively, by volume);
minor gases are argon (0,93%) and carbon dioxide
(0,03%); and trace gases (the whole group totaling
0,01%) are neon, helium, methane, krypton, hydrogen,
nitrogen oxides, ozone, ammonia, and sulfur dioxide.
Water vapor content in the low atmosphere is highly
variable, ranging from less than 1% to 5–6% by volume.
Air quality may range widely from quite good (satisfactory)
to poor, in various degrees. Air quality is good
when there is normal chemical composition of air without
significant variations in physical (or physico-chemical,
e. g. radiological) and biological characteristics.
Air quality is poor and detrimental if air is odorous
and stale, if physical parameters are out of optimal values,
or if air is polluted by chemicals of various origin.
The main physical characteristics of air that affect
air quality are temperature, humidity, air velocity, and
radiant heat. Biological origins of air quality deterioration
include bacteria, viruses (humans are the main
sources in indoor spaces), fungi (molds), insects (fleas
and cockroaches), arthropods (e. g. house dustmites),
mammals (e. g. home pets – their excreta, hair, dander
or feathers), and plants (pollen grains). There are two
main groups of sources of air pollution – natural, and
artificial or man-made sources.
Natural Sources of Air Pollution
Over the millennia it has been in existence, the atmosphere
has been relatively balanced and stable in composition,
being polluted mainly by natural processes.
Like now, natural sources of pollution have been volcanic
eruptions, forest wildfires, biochemical release of
pollutants from soils and oceans, soil erosion, windstorms,
lightning, and plant pollen release, etc. Natural
sources are much stronger than artificial ones, but pollutants
are usually diluted or widely dispersed over the
whole atmosphere, often far from human habitation.
Artificial Sources of Air Pollution
During the last 150–300 years, which have seen agricultural
and industrial revolutions, human technology
has reached a point where it is disturbing the global
balance of the atmosphere. Man has begun to pollute
air in a much stronger manner than ever before. Pollution
has been caused by an enormous output of harmful
substances into the atmosphere, emitted from a variety
of stationary or mobile sources. These artificial or
man-made sources are usually situated inside human
settlements or close to them; for this reason, they are
much more threatening to human health than natural
sources. The most important sources of pollution are:
a) power and heat generation objects (e. g. fossil fuel
power stations, domestic combustion appliances, and
biomass burning); b) industrial objects (smelteries and
foundries) and agricultural activities; c) transportation
(motor vehicles with internal combustion); d) waste
sites (the burning or spontaneous evaporation of pollutants
out of dumps); and e) Other human activities producing
gases, vapors or aerosols (fumigation, spraying,
etc.).
Ambient or Outdoor Air Pollution
Major pollutants are slightly different throughout the
world, depending on the predominance of pollution
sources locally. However, the six major types are the
organic pollutants carbon monoxide and hydrocarbons,
and the inorganic pollutants nitrogen oxides, sulfur
dioxide, particulates, and low ozone.  Smog, a contraction
of the words smoke and fog, is a common term
used to indicate the presence of a mixture of multisource
pollutants in the air around large human settlements.
Indoor Air Pollution
Indoor space is the interior of each working or residential
building in the commercial, public or private sectors,
not including industrial working interiors or outdoor
space. Indoor spaces are: a) private residences; b)
non residential, commercial and public buildings, e. g.
offices, libraries, cinemas, indoor market places, restaurants,
hospitals, schools and indoor sport arenas, and c)
transportation, e. g. the interior of private cars, buses,
aircrafts and subways.
The indoor environment is now more significant for
health considerations than the outdoor environment.
Concerns about potential public health problems due to
indoor air pollution are based on epidemiological evidence
that urban residents spend approximately 90% of
their time indoors. By such activity patterns, they have
more exposure to harmful agents that exist indoors. The
most important pollutants are nitrogen oxides, volatile
organic compounds, formaldehyde, carbon monoxide,
ozone, and  suspended particles. If tobacco smoking
is not restricted, a mixture of dangerous pollutants may
be detected. Inside many indoor spaces, airborne allergens
such as dustmites are present, and sometimes even
the radioactive gas radon. Carbon dioxide is a marker of
indoor air pollution rather than a specific pollutant.
Adverse Effects of Air Pollution
Enormous and continually increasing rates of outdoor
air pollution may have significant consequences on the
quality of air, human health and the whole environment.
Local, regional and even global environmental effects
are well known and scientifically proven. Considering
local health effects, increased morbidity and mortality
rates are reported among vulnerable population groups
in highly polluted areas. Usually registered are: a) upper
respiratory tract illnesses; b) lower respiratory tract illnesses
(bronchitis, asthma and pneumonia); c) malignant
diseases of the respiratory tract; d) ocular mucous
membrane illnesses and complaints; and e) decreased
resistance to common allergens. Effects on the local
climate are also pronounced as climate characteristics
Over certain regions of the Earth, air pollution induces
ecosystem acidification and acid deposition ( acid
rain), with both noticeable adverse environmental consequences
(e. g. damage to vegetation), and human
health impairments. Air pollution has also led to deterioration
of the atmosphere on a global scale. The
most important global consequences are ozone layer
depletion in the stratosphere (ozone holes), and the
greenhouse effect. As a consequence of ozone layer
depletion, the amount of harmful short-wave ultraviolet
reaching the Earth’s surface has been enhanced.
The  greenhouse effect (global warming of the atmosphere)
is mainly a result of carbon dioxide and
methane being released into the atmosphere due to
burning of fossil fuels and farming practices, respectively.
During the last decade of the 20th century, the US
Environmental Protection Agency consistently ranked
indoor air pollution among the top five risks for health
impairments in general population groups. There is
mounting evidence that exposure to polluted indoor air
is the cause of excessive morbidity and mortality. The
main health consequences of indoor air pollution are
grouped into a)  specific building- and home-related
illnesses (SBRI), and b)  chemical sensitivity syndromes.
Cross-References
 Acid Rain
 Chemical Sensitivity Syndromes
 Greenhouse Effect
 House Dust Mites
 Smog
 Specific Building- and Home-Related Illnesses
 Suspended Particles
References
Cadle RD (1998) Environmental Pollution - Air pollution. The
Academic American Encyclopedia (The 1998 Grolier Multimedia
Encyclopedia version). Copyright (c) 1997 Grolier,
Inc. Danbury, CT.
Manuel J (1999) A Healthy Home Environment? Environ Health
Perspect 107(7):A352-7
Kumar HD, Häder DP (1999) Global aquatic and atmospheric
environment. Springer, Berlin
Ledford DK, Lockey RF (1994) Building- and home-related complaints
and illnesses: Sick building syndrome. J Allergy Clin
Immunol 94(2):275–6
Mendell MJ, Heath GA (2005) Do indoor pollutants and thermal
conditions in schools influence student performance? A critical
review of the literature. Indoor Air 15(1):27–52
Seltzer JM (1994) Building-related illnesses. J Allergy Clin
Immunol 94(2):351–61
Sundell J (2004) On the history of indoor air quality and health.
Indoor Air 14(Suppl 7):51–8
WHO Commission on Health and Environment (1992) Our planet,
our health: report of the WHO Commission on health and
environment. World Health Organization, Geneva
World Health Organization (2000) Climate change and stratospheric
ozone depletion: early effects on our health in
Europe. In: Sari Kovats et al. (eds) WHO regional publications.
European series, No. 88
World Health Organization (2000) Air quality guidelines for
Europe, 2nd edn. WHO regional publications. European
series, No. 91

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