EPA Observational Economy Series: Volume 1: Composite Sampling

United States

Environmental Protection

Policy, Planning.

EPA-230-R-95-005

And Evaluation

August 1995

Agency

(2163)

EPA Observational

Economy Series

Volume 1: Composite Sampling

EPA Observational Economy Series

Vol. 1: Composite Sampling

United States

Environmental Protection

Agency

Policy, Planning,

And Evaluation

(2163)

EPA 230-R-95-005

August 1995

Contents

Foreword

iii

Acknowledgments

1. Introduction

2. What is Composite Sampling?

2.1 Method . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

2.2 Limitations of Composite Sampling . . . . . . . . . . . . . . . .

3. Applications

3.1.

Soil Sampling

...........................

3.1.1. PCB Contamination

....................

3.1.2. PAH Contamination

....................

3.2. Ground Water Monitoring

....................

3.3. Indoor Air Monitoring

.......................

3.4. Biomonitoring

...........................

3.4.1. Bioaccumulation in Human Adipose Tissue

.......

3.4.2. Assessing Contamination in Fish

.............

3.4.3. Assessing Contaminants in Mollusks

...........

3.4.4. Measuring Average Fat Content in Bulk Milk

......

4. Summary

References

Foreword

The high costs of laboratory analytical procedures frequently strain environ-

mental and public health budgets. Whether soil, water or biological tissue is

being analyzed, the cost of testing for chemical and pathogenic contaminants

can be quite prohibitive.

Composite sampling can substantially reduce analytical costs because the

number of required analyses is reduced by compositing several samples into

one and analyzing the composited sample. By appropriate selection of the

composite sample size and retesting of select individual samples, composite

sampling may reveal the same information as would otherwise require many

more analyses.

Many of the limitations of composite sampling have been overcome by

recent research, thus bringing out more widespread potential for using com-

posite sampling to reduce costs of environmental and public health assess-

ments while maintaining and often increasing the precision of sample-based

inference.

iii

Acknowledgments

The EPA Observational Economy Series is a result of the research conducted

under a cooperative agreement between the U.S. Environmental Protection

Agency and the Pennsylvania State University Center for Statistical Ecology

and Environmental Statistics, Professor G.P. Patil, Director.

The EPA grant CR-821531010, entitled “Research and Outreach on Ob-

servational Economy, Environmental Sampling and Statistical Decision Mak-

ing in Statistical Ecology and Environmental Statistics” consists of ten sep-

arate projects in progress at the Penn State Center: 1) Composite Sampling

and Designs; 2) Ranked Set Sampling and Designs; 3) Environmental Site

Characterization and Evaluation; 4) Encounter Sampling; 5) Spatio-temporal

Data Analysis; 6) Biodiversity Analysis and Monitoring; 7) Adaptive Sam-

pling Designs; 8) Statistics in Environmental Policy and Regulation for Com-

pliance and Enforcement; 9) Statistical Ecology and Ecological Risk Assess-

ment; and 10) Environmental Statistics Knowledge Transfer, Outreach and

Training.

The series is published by the Statistical Analysis and Computing Branch

of the Environmental Statistics and Information Division in the EPA Office

of Policy, Planning and Evaluation. This volume in the series is largely based

on the work of M. T. Boswell, S. D. Gore, G. D. Johnson, G. P. Patil, and C.

Taillie at the Penn State Center in cooperation with John Fritzvold, Herbert

Lacayo, Robert O’Brien, Brenda Odom, Barry Nussbaum, and John Warren

as project officers at U.S. EPA. Questions or comments on this publication

should be directed to Dr. N. Phillip Ross, Director, Environmental Statistics

and Information Division (Mail Code 2163), United States Environmental

Protection Agency, 401 M Street SW, Washington, DC 20460; Ph. (202)

260-2680.

1. Introduction

While decision making in general involves opinion based on prior experience,

scientifically based decision making requires careful collection, measurement

and interpretation of data from physical observations.

Examples of such

decisions are:

“Has a hazardous waste site been sufficiently cleaned?“; or

“Are pollutants accumulating in certain foods as well as in human or wildlife

tissues?“.

Scientifically based decision making should minimize the risk of being

wrong. Since decisions require information, which is in turn extracted from

data, this risk decreases as the data become more representative of the pop-

ulation being studied.

In order for a data set to properly represent a population, it must cover

the ranges of space and time within which the population lies, as well as

have sufficient resolution within these ranges. It soon becomes obvious that

collection and review of representative data can be prohibitively expensive

if a large sample size (number of measurements, recordings or counts) is re-

quired, especially when analytical costs are very high such as with monitoring

environmental and biological media for chemical or pathogenic contaminants.

Conventional statistical techniques allow for the reduction of either cost or

uncertainty. However, the reduction of one of these factors is at the expense

of an increase in the other. Composite sampling offers to maintain cost or

uncertainty at a specified level while decreasing the other component.

Cornpositing simply refers to physically mixing individual samples to form

a composite sample, as visualized in Figure 1. Just one analysis is performed

on the composite, which is used to represent each of the original individual

samples.

Cornpositing is common practice for simply increasing the representative-

ness of a measurement, such as when measuring the fat content of a particular

entree that is cornposited across several restaurants included in a national

survey (Burros, 1994). For this reason, cornpositing can always reduce costs

for estimating a total or an average value. However, analysis of composite

samples can be cleverly extended to classify the original individual sample

units that comprised a composite.

For example, one may need to identify

the presence or absence of a pathogen like HIV in blood samples, or one may

need to identify all soil cores whose contaminant concentration exceeds an

action level at a hazardous waste site.

When analytical costs dominate over sampling costs, the savings potential

is obviously high; however, the immediate question is “How do we compensate

for information that is lost due to compositing?“. More specifically, if we are

testing whether or not a substance is present or existing at a concentration

above some threshold, we do not want to dilute individual “contaminated”

samples with clean samples so that the analysis does not detect any con-

tamination.’ Furthermore, if our measurements are of a variable such as a

chemical concentration, we may need to know the actual values of those in-

dividual samples with the highest concentrations. For example, “hot spots”

need to be identified at hazardous waste sites.

Through judicial choice of a strategy for retesting some of the original in-

dividual samples based on composite sample measurements, many limitations

of composite sampling can be overcome. Furthermore, other innovative ap-

plications of composite sampling are emerging such as combining with ranked

set sampling, another approach to achieve observational economy that is dis-

cussed in Volume 2 of this series.

Individual Field Samples

Figure 1: Forming composite samples from individual samples

2. What is Composite

Sampling?

2.1. Method

First; let’s clarify that a “sample” in this document refers to a physical object

to be measured, whether an individual or a composite, and not a collection

of observations in the statistical sense.

Individual sample units are what

is obtained in the field, such as soil cores or fish fillets; or obtained from

subjects, such as blood samples. Meanwhile, a composite sample may be a

physical mix of individual sample units or a batch of unblended individual

sample units that are tested as a group. Most cornpositing for environmental

assessment and monitoring consists of physically mixing individual units to

make a composite sample that is as homogeneous as possible.

With classical sampling, no distinction is made between the process of

sampling (i.e., selection or inclusion) and that of observation or measurement.

We assume, with classical sampling, that any unit selected for inclusion in a

statistical sample is measured and hence its value becomes known. In com-

posite sampling, however, there is a clear distinction between the sampling

and measurement stages. Compositing takes place between these two stages,

and therefore achieves two otherwise conflicting goals. While a large number

of samples can be selected to satisfy sample size requirements, the number

of analytical measurements is kept affordable.

If a variable of concern is a measurement that is continuous in nature

such as a chemical concentration, the mean (arithmetic average) of composite

samples provides an unbiased estimate of the true but unknown “population”

mean. Also, if measurement error is known, the population variance based

on the scale of the individual samples can be estimated by a simple weighting

of the measured composite sample variance.

With selective retesting of individual sample units, based on initial com-

posite sample results, we can classify all of the individual sample units ac-

cording to the presence or absence of a trait, or exceedance (vs. compliance)

of a numerical standard. We can subsequently estimate the prevalence of

subsamples (aliquots) of

individual samples used to

form a composite

retest select individuals

Yes: all individual samples

classified as negative

Figure 2: Composite sampling with retesting

a trait or proportion of non-compliance. Basically, if a composite measure-

ment does not reveal a trait in question or is in compliance, then all individual

samples comprising that composite are classified as “negative”. When a com-

posite tests positive, then retesting is performed on the individual samples

or subsamples (aliquots) in order to locate the source of “contamination”.

Retesting, as visualized in a general sense in Figure 2, may simply be

exhaustive retesting of all individuals comprising a composite or may entail

more specialized protocols. Generally, as the retesting protocol becomes more

sophisticated, the expected number of analyses decreases. Therefore, one

must consider any increased logistical costs along with the expected decrease

in analytical cost when evaluating the overall cost of a compositing/retesting

protocol.

Due to recent research (Patil, Gore and Sinha, 1994), the individual sam-

ples with the highest value, along with those individual samples comprising

an upper percentile, can be identified with minimal retesting. This ability

is extremely important when “hot spots” need to be identified such as with

soil monitoring at a hazardous waste site.

Whether we are dealing with data from binary (presence/absence) meas-

urements or data from measurements on a continuum, composite sampling

can result in classifying each individual sample without having to separately

analyze each one. While composite sampling may not be feasible when the

prevalence of contamination is high, the analytical costs can be drastically

reduced as the number of contaminated samples decreases.

2.2. Limitations of Composite Sampling

Both physical and logistical constraints exist that may restrict the applica-

tion of composite sampling. The limitations which more commonly arise are

discussed here along with some simple recommendations for how compositing

still may help.

Physical:

If the integrity of the individual sample values changes because of com-

positing, then composite sampling may not be the desired approach. For

example, volatile chemicals can evaporate upon mixing of samples (Cline

and Severin, 1989)

or interaction can occur among sample constituents. In

the first case, compositing of individual sample extracts may be a reasonable

alternative to mixing individual samples as they are collected.

Another limitation is imposed by potential dilution, where an individual

sample with a high value is combined with low values resulting in a compos-

ite sample that falsely tests negative.

When classifying samples according

to exceedance or compliance with some standard value, c, the problem of

dilution is overcome by comparing the composite sample result to c divided

by the composite sample size, k, (c/k). Furthermore, when an analytical

detection limit, d, is known, the maximum composite sample size is estab-

lished according to the inequality k < c/d. One may lower this upper bound

on the composite sample size to reduce effects of measurement error. As

can be seen here, when reporting limits (Rajagopal, 1990) or action levels

(Williams, 1990) of some hazardous chemical concentrations are legally re-

quired to be near the detection limit, the possibility of composite sampling

may be eliminated.

Sample homogeneity is another consideration. A homogeneous sample is

one where the variable of interest, such as a chemical concentration, is evenly

distributed throughout the sample. In contrast, a heterogeneous sample can

have substantially different values for the variable of interest, depending on

what part of the sample is actually analyzed. If the whole sample unit is

analyzed, then heterogeneity is not a problem; however, most laboratory

analyses are performed on a small subsample of the original sample unit. For

example, one gram of soil may be taken from a one kilogram soil core for

actual extraction and analysis. If a subsample is to represent a larger sample

unit, then the larger unit must be fairly homogeneous with respect to the

variable of interest.

Therefore, an individual sample unit should be homogenized as much as

possible prior to obtaining an aliquot for inclusion in a composite. Further-

more, formation of a composite must include homogenization if the composite

is going to be represented by measurement on a smaller subsample.

Often, measurements on multiple attributes are desired. However, if

retesting is performed in order to classify individual samples, it is unclear

how to optimize the retesting relative to the different attributes (Schaeffer et

al., 1982). For example, should chemicals be tested independently, or does

there exist dependence in the multivariate information that can be used to

improve cost efficiency? Classifying for multiple attributes remains an open

problem in composite sampling.

Logistical:

When retesting of certain individual samples may be required based on

composite sample results, then subsamples (aliquots) of the original individ-

ual samples must be preserved and stored until all testing is done. This may

lead to extra expense that must be considered in the overall cost comparison

between compositing and other strategies. For most environmental and pub-

lic health studies, the analytical savings from compositing will far outweigh

the extra cost of sample preservation and storage.

Another consideration is that events out of control of the scientists may

dictate the feasibility of composite sampling. For example, people whose

wells are being tested may demand that their wells be treated as equitably

as the wells of their neighbors. Measuring some well samples individually and

some well samples solely as part of a composite may give an appearance of

inequitability and result in a political decree to measure each well individually

(Rajagopal, 1990).

Circumstances that may presently disqualify composite sampling from

being applied may change upon advances in technology. Long turn-around

time for laboratory results and large labor costs may currently eliminate

optimal retesting designs from consideration. However, retesting designs in

the future may be automated and guided by an expert system (Rajagopal,

1990). Also, advances in statistical methodology may further extend the

utility of composite sampling,

For other reviews of composite sampling, see Rohde (1976, 1979), Elder

(1977), Elder, Thompson, and Myers (1980), Boswell and Patil (1987) and

Garner, Stapanian, and Williams (1988). For an overview, see Patil, Gore,

and Taillie (1994).

3. Applications

Composite sampling has its roots in what is known as group testing. An early

application of group testing was to estimate the prevalence of plant virus

transmission by insects (Watson, 1936). In this application, insect vectors

were allowed to feed upon host plants, thus allowing the disease transmission

rate to be estimated from the number of plants that subsequently become

diseased.

Apparently, the next important application of group testing occurred dur-

ing World War II when U.S. servicemen were tested for syphilis by detecting

the presence or absence of a specific antigen of the syphilis-causing bacterium

in samples of their blood (Dorfman, 1943). Initial analyses were done on com-

posite samples formed from aliquots of blood drawn from the subjects. A

composite sample testing negative indicated that all individuals contributing

to the composite were negative, while a composite testing positive prompted

exhaustive retesting of the original aliquots comprising that composite. If

blood aliquots of, k individuals are composited, the number of required tests

to classify these k individuals will either be 1 or k + 1. For a given prevalence

of the trait, the expected number of tests can be calculated for a composite

of size k. This application has gone on to become a classic example of how

statistical cleverness can assist researchers in attaining what we call obser-

vational economy (Rao, 1989).

In light of recent developments, composite sampling is increasingly be-

coming an acceptable practice for sampling soils, biota, and bulk materials

when the goal is estimation of some population value under restrictions of a

desired standard error and/or limits on the cost of sample measurement.

In response to an informal survey of various professionals, several favor-

able applications of composite sampling were received. They include:

l Establishing and verifying attainment of remedial cleanup standards in

soils using sample compositing and bootstrapping techniques

l Use of compositing to obtain adequate support in geostatistical sam-

pling

l Optimal compositing strategies for screening material for deleterious

agents

A soil sample design utilizing techniques of compositing, binary search,

and confidence limits on proportions

Composite sampling for analyzing foliage and other biological materials

While many diverse applications exist for composite sampling, some ex-

amples that are particularly relevant to environmental and public health

studies are detailed in the remainder of this chapter.

3.1.

Soil Sampling

3.1.1. Characterization of Soil PCB Contamination at

Gas Pipeline Compressor Stations

As part of a recent settlement between the Pennsylvania Department of

Environmental Resources and the Texas Eastern Pipeline Company, PCB-

contaminated soils had to be characterized and remediated at 19 sites. Be-

cause waste sources included indiscriminate dumping, disposal in trash pits,

air emissions and even application as weed killer along fence lines, the result-

ing spatial distribution of contaminated soil was very heterogeneous, with

hot spot locations unknown. Therefore, the only way to reliably characterize

these sites required a very large number of soil samples, around 12,000 to be

more precise. With each sample analyzed for total PCB,s, the cost for site

characterization alone was around $33 million. Now to really appreciate the

magnitude of the problem, one must realize this discussion only pertains to

the Pennsylvania settlement. The problem extends along the whole pipeline

from the Gulf Coast to New England.

Results of a retrospective study (Gore, Patil, and Taillie, 1992; Patil, Gore

and Sinha, 1994), using the actual site characterization data, revealed that

composite sampling methods potentially could have substantially reduced

the analytical costs.

Three aspects of the data were evaluated: (i) estimation of the mean

and variance of total PCB concentration as well as total PCB mass, (ii)

classification of each individual (uncomposited) sample as above or below

a specified critical level, and (iii) quantification of those individual samples

with the highest PCB levels.

Results showed that unbiased estimates of the mean and variance could

be obtained with one fourth the number of analyses (90 instead of 360). A

small loss of precision resulting from compositing seemed quite acceptable in

light of large analytical cost reduction.

Cornpositing can actually increase

precision if composites are purposely formed to increase heterogeneity within

composites; however, in this case composites were formed from spatially prox-

imate field samples in order to minimize heterogeneity within composites.

This approach was taken because it provides for the most efficient retesting

for classifying individual samples, which, as with most hazardous waste sites,

was the primary objective.

A site was acceptably clean if 90% of the measured samples were below

10 parts per million (ppm) with no values exceeding 25 ppm. With charac-

terization data from the worst of the nineteen sites, cornpositing could have

reduced the analytical cost of classifying individual samples according to the

10 ppm criterion by 9%, relative to exhaustive testing. Starting from this

nearly worst case scenario, the cost savings increase as we move to cleaner

sites and should be dramatic when analyzing post-remediation verification

data. For example, another site along the pipeline that is cleaner, although

still contaminated, could have had all individual samples classified accord-

ing to 10 ppm for 50% less of the analytical cost associated with exhaustive

testing. (See Gore, Boswell, Patil, and Taillie, 1992).

Finally, if concerned with simply knowing which individual sample has the

highest concentration, we could have discovered this by exhaustively retesting

just two composite samples. In other words, with only eight measurements

in addition to the 90 composite measurements, we could have identified the

“hottest” spot.

Furthermore, 12 additional measurements could have re-

vealed the locations with the four highest concentrations (See Patil, Gore

and Sinha, 1994).

Keep in mind that the percentages cited here result from a retrospective

study where expected composite values were estimated by arithmetically av-

eraging individual values. Since this approach assumes no measurement error

(but some is expected due to incomplete homogenization of samples), these

percentages are best interpreted as potential savings.

3.1.2. Characterization of Soil PAH Contamination at

a Superfund Site

In another study involving remediation of contaminated soil (Messner, et al,

1990), the investigators wanted to determine which half-acre plots at a Su-

perfund site should be remediated. The contaminant was total polyaromatic

hydrocarbons (PAHs) and the cleanup objective was to remediate any plots

that posed greater than a 10

-4

risk based on direct ingestion as the most

likely route of exposure.

These investigators concluded that the most cost-effective sampling design

was to take two composite samples from each half-acre plot, with each of the

two composites consisting of ten individual samples. Even when considering

the influence of small “hot spots,”

the proposed composite sampling design

assured a high probability of making the correct decision. Since the estimated

cost per analysis for this study was $800, the savings due to compositing is

phenomenal.

3.2. Ground Water Monitoring

As the distribution of a constituent in a given medium becomes more ho-

mogeneous, measurement error decreases, making composite sampling more

feasible. For this reason, composite sampling has great economic potential

for analyzing dissolved solutes, whether the solvent is water or some other

liquid. In fact, a study of composite sampling of wastewater (Schaeffer, Ker-

ster and Janardan, 1980) h

owed

that variability of analytical results due to

compositing was an insignificant source of total variability.

Rajagopal and Williams (1989) critically evaluated the economy of com-

positing ground water samples when screening a large monitoring network in

order to identify contaminated wells. With a binary retesting scheme, com-

positing resulted in decreased analytical effort and subsequent cost when no

more than about 12.5% of the wells were contaminated. Of course the savings

increased as the number of contaminated wells in the network decreased.

When more than one out of eight wells were contaminated, the number

of analyses increased over the amount required’ by initial exhaustive testing,

with the worst case scenario resulting in 50% additional analyses. If, however,

curtailed retesting was performed instead of straight binary retesting, the

absolute maximum exceedance of analyses would be 31% over that required

by initial exhaustive retesting. This number of additional analyses becomes

even smaller as the distribution of contaminated wells becomes contagious

(or clumped); therefore the rate of 31% additional analyses is absolute worst

case.

As seen here, if the number of contaminated wells is expected to be gen-

erally low, (e.g. less than 12%), cornpositing can be economically attractive.

3.3. Indoor Air Monitoring for Allergens

Quantification of specific allergens in dust from human dwellings provides

important information for determining allergen exposure. The fact that in-

door allergens are not equally distributed in the dust of human dwellings

makes it difficult to estimate allergen exposure with a high degree of cer-

tainty. A composite sample may provide a more reliable estimate of indoor

allergen exposure and minimize error associated with unequal distribution

of allergens on discrete objects. Composite samples of household dust may

provide useful information while minimizing the sample collection effort and

analytical test costs.

In a recent study (Lintner et al., 1992), dust samples from three specific

objects and composite samples from the same three objects were collected

from the living rooms and bedrooms of 15 homes by a single technician.

Discrete and composite samples were collected from floor, furniture (uphol-

stery/bed) and window- coverings in both the living room and a bedroom of

each home. Discrete samples were collected by vacuuming the specific objects

for 10 minutes. Composite samples were collected in a defined sequence by

vacuuming the three objects for 5 minutes each. In this way, the composites

were formed at the time of sample collection by allowing the vacuum cleaner

to do the physical mixing of the dust from several objects.

Results of this study seem to indicate that the actual measurement of a

composite sample will be approximately the average of the values that would

be obtained from separate measurements on discrete samples. However, if

an object has a significantly higher allergen content than other objects, the

composite sample measurement tends to be higher than the average of the

discrete sample measurements.

In order to effectively use composite sam-

pling, only items which are likely sources of allergen should be used to form

a composite sample.

3.4. Biomonitoring

3.4.1. Measuring Bioaccumulation in Human Adipose

Tissue

The National Human Adipose Tissue Survey (NHATS) is an annual survey

to collect and analyze a sample of adipose tissue specimens from autopsied

cadavers and surgical patients (Orban, Lordo and Schemberger, 1990). The

primary objectives of NHATS include:

l To identify chemicals that are present in the adipose tissue of individ-

uals in the U.S. population,

l To estimate the average concentrations, with confidence intervals, of

selected chemicals in adipose tissue of individuals in the U.S. population

and in various demographic subpopulations, and

l To determine if geographic region, age, race and sex affect the average

concentrations of selected chemicals detected in the U.S. population

Every year approximately 800-1200 adipose tissue specimens are collected

using a multistage sampling plan.

First, the 48 conterminous states are

stratified into four geographic areas, which form four strata. Next, a sample

of metropolitan statistical areas (MSAs) is selected from every stratum with

probabilities proportional to MSA populations. Finally, several cooperators

(hospital pathologists or medical examiners) are chosen from every selected

MSA and asked to supply a specified quota of tissue specimens. The quota

specifies the number of specimens needed in each of the following categories:

l Age groups: 0-14 years, 15-44 years, and 45+ years;

l Race: Caucasian and non-Caucasian; and

l Sex: Male and female.

The sampling plans are designed to give unbiased and efficient estimates

of the average concentrations of selected chemicals in the entire population

and in various subpopulations defined by the demographic variables described

above. Concentrations are characterized by the average or median chemical

concentrations; while prevalence is the proportion of individuals with chem-

ical concentrations exceeding specified criterion levels.

Instead of analyzing 800-1200 individual specimens, only about 50 com-

posite samples are analyzed. This not only reduces analytical cost, but also

provides enough tissue mass to use high resolution gas chromatography /

mass spectrometry which allows for a wider list of target chemicals to test

for.

3.4.2. Assessing Contamination in Fish

When monitoring human tissue for assessing the bioaccumulation of contam-

inants, compositing was forced on the study in order to achieve sufficient

mass of material for analysis. Now, with other organisms this is not typically

a limitation because we can sacrifice the whole organism. Nevertheless, as

researchers have shown (Paasivirta and Paukku, 1989), compositing is still

preferable because it is much more cost-effective.

When concerned with the concentrations of a host of organochlorine com-

pounds in Herring off of Finland’s East Gulf, researchers recognized how

expensive such monitoring could become. They therefore evaluated the ef-

fectiveness of composite sampling and concluded that costs could be reduced

by about 54% using optimized composite sampling instead of analyzing indi-

vidual fish. They also showed that average chemical concentrations could be

estimated from composite samples with the same accuracy as a larger num-

ber of individual samples, and that optimum composite sample sizes could

be easily calculated if laboratory variance can be predicted.

3.4.3. Assessing Contaminants in Mollusks

As part of the National Oceanic and Atmospheric Administration’s “Mus-

sel Watch” program,

177 coastal sites were sampled from 1986 to 1988

(NOAA, 1989).

While mussels were collected along the West Coast and north-

ern East Coast, oysters were taken along the southern East Coast, the Gulf

Coast and three sites in Hawaii.

Using the soft tissue of these mollusks, composite samples were made by

homogenizing either 30 mussels or 20 oysters. Six composites were then used

for chemical analysis, three for organics and three for trace elements.

Cornpositing served two purposes here; to provide sufficient media (tis-

sue) for analysis and to increase the information in each measurement. The

statistics of interest were means and variances, therefore retesting of individ-

ual mollusks or groups thereof was not necessary and the desired information

was obtained with minimal analyses.

3.4.4. Measuring Average Fat Content in Bulk Milk

Apparently, the economic value of composite sampling is well known in the

dairy industry, where milk must be routinely analyzed. For example, the fat

content of milk is determined on composite samples which are formed from

samples using all deliveries during a specified period of time.

Since composite samples are known to provide an unbiased estimate of the

population mean, dairy scientists are mainly concerned with the precision of

a composite sample estimator compared to that of an individual sample es-

timator. Williams and Peterson (1978)

developed

a framework for assessing

the precision of sampling schemes by estimating different sources of varia-

tion associated with the sampling process. They identified four components:

variance due to real difference between collections from a supplier within a

cornpositing period (biological variance), variance among samples taken from

the same collection (sample variance), variance among measurements on the

same sample (testing variance) and the variance associated with forming a

composite sample (cornpositing variance).

Based on a study of sixty-one herd milk supplies in three different cream-

ery locations, Connolly and O’Connor (1981) found that the biological com-

ponents of variability were about 10 times as large as sampling or cornpositing

components, indicating that the true biological variability is not masked by

the composite sampling process.

4. Summary

Compared to exhaustively testing all individual sample units, testing compos-

ite samples has the potential to greatly increase one’s observational economy

when conducting environmental and public health monitoring.

When the objective is to estimate the population mean or total, com-

positing will always reduce analytical cost; however, a sufficient number of

composite samples must still be obtained for estimating the variance.

When the objective is to classify each individual sample, with subsequent

estimation of the prevalence of a binary trait or proportion of noncompliance

measurements, testing composite samples with selective retesting becomes

cost-effective when the prevalence or proportion is low. Examples of where

composite sampling can be very cost-effective for classification include (i)

estimating the prevalence of a rare disease and (ii) verifying if a hazardous

waste site has been sufficiently remediated.

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