United States
Environmental Protection
Agency
National Exposure Research
Laboratory
Research Triangle Park, NC 27711
Research and Development
EPA/600/SR-97/107   January 1998
Project  Summary

 Round-Robin  Testing  of
 Methods for Collecting
 Dislodgeable  Residues from
 Carpets
Christopher R. Fortune
  A round-robin test  was conducted
using  six volunteers to evaluate three
dislodgeable residue methods sampling
new carpets treated with a commercial
pesticide formulation.  Seven separate
tests were performed, each using a for-
mulation containing three target pesti-
cides (chlorpyrifos, pyrethrin I, and pip-
eronyl butoxide). Strict QA/QC  guide-
lines were followed as  each participant
collected three replicate samples each
with the polyurethane foam (PDF) roller,
the California roller, and the Dow drag
sled methods. Sampling precision was
high for all three methods for measure-
ments of this type. The overall results
(mean %RSD, relative  standard devia-
tion, N=21) show the Dow sled with the
best sampling precision (25.4% RSD),
followed by the California roller (30.7%),
and then the PUF roller (37.9%). Mean
transfer efficiency, the  ratio of the
method  transfer rate to the pesticide
deposition rate, was  highest  for the
California roller (5.0%), followed by the
Dow  sled (2.1%)  and the PUF roller
(1.7%). The mean  transfer  efficiency
rates in  this study were  substantially
higher than those  reported in  earlier
studies of this type.
  Information  relating  to  ease of use,
simplicity, time requirements, and other
criteria for each of the test methods
was obtained  from written subjective
evaluation and critique by each volun-
teer. A compilation of  that information
revealed that both the Dow sled  and
PUF roller methods were rated highly
and equal to  one  another,  while the
California roller was rated lower. Fur-
ther testing  is recommended to deter-
mine the effect on transfer efficiency
rates due to carpet age, type and prior
cleaning or chemical treatment.
   This Project Summary was developed
 by EPA's National Exposure Research
 Laboratory,  Research Triangle Park,
 NC, to announce  key findings of the
 research project  that is  fully docu-
 mented in a separate report of the same
 title (see Project Report ordering infor-
 mation at back).

 Introduction
   A recent study was conducted to test
 the performance of three dislodgeable pes-
 ticide residue methods  on floor surfaces.
 One result of that study was a recommen-
 dation to conduct a round robin study of
 the same three methods, following strict
 QA/QC guidelines,  using volunteers  to
 perform the testing  and provide written
 evaluations of the procedures. This report
 presents the results of that round-robin
 study using six volunteers.
   The PUF roller, the California roller and
 the Dow drag sled  methods were evalu-
 ated. Written standard  operating proce-
 dures (SOPs) were  prepared, tested and
 modified, where necessary,  for each
 method prior to the onset of the testing.
 Volunteers were trained  in the use of each
 procedure just prior to beginning the sam-
 pling activities. For  each test a new,  ny-
 lon, plush cut-pile,  stain resistant carpet
 was treated with a  commercial pesticide
 formulation used to  control a heavy infes-
 tation of fleas. Field blank and field spike
 samples were collected along  with  the
 replicate samples collected using the three
 test methods.
   Test samples, along with both  field and
 laboratory QA/QC samples, were extracted
 and then analyzed by a  referee laboratory
 using a GC/MS SIM  mode procedure. The
 analytical results  for  the three target
 analytes, chlorpyrifos, pyrethrin I and pip-
 eronyl butoxide, were used  to calculate

-------
the method sampling precision  and the
transfer efficiency rate for each test pro-
cedure. Upon the conclusion of each test,
the volunteer provided a written evalua-
tion pertinent to a wide variety of specific
performance characteristics for each test
method used in the study.

Study Design
  Six volunteers were recruited from local
agricultural and chemical research organi-
zations. Half of the participants were from
large organizations and the other half were
from smaller companies.  An 8- x  20-ft
modular trailer unit was leased for use in
performing the tests. Participants were pro-
vided advanced  copies of the SOPs and
general instructions  concerning the
planned training  and testing activities. On
the morning of each scheduled test, the
staff collected field blanks from a new 6- x
14-ft carpet test  sample and then treated
the carpet  with the freshly prepared test
formulation. A mixture of 0.5% chlorpyrifos,
0.05%  pyrethrin I, and 0.5% piperonyl bu-
toxide was sprayed on the carpet surface
at a manufacturer's recommended rate of
1 gal/1600 ft2. The carpet was divided into
three equal sections for sampling layout
purposes,  and  a 4- x 4-in. a-cellulose
deposition  coupon was placed  in  each
section  prior to spraying in order to pro-
vide  a  measure of the actual  pesticide
deposition rate for each test.
  Shortly after arriving at our test facility,
the volunteers were given a thorough dem-
onstration  and  hands-on  familiarization
session with the three dislodgeable resi-
due test methods.  After a 4 hour drying
period  and complete  ventilation, the test-
ing session was initiated. A set of field
spikes  of each  of the four sample  matri-
ces was collected  in the  laboratory. The
volunteers  then  performed the replicate
sampling using each test method to col-
lect one sample  in  each of the three sec-
tions of the test carpet. The exposed depo-
sition coupons were  collected from  each
section individually at the time test samples
were collected.
  All samples were  stored in pre-labled
containers,  packed on dry ice, and shipped
to the laboratory by overnight express de-
livery service. Participants were debriefed
following the testing  and were  asked to
rate the test procedures by filling out ques-
tionnaires provided for that purpose.
  The  analytical laboratory services  were
provided by Southwest Research Institute,
San  Antonio,  TX.  Having  had previous
experience in studies  of this kind, the labo-
ratory  followed written  protocols in per-
forming the extraction and GC/MS analy-
sis of the test samples and laboratory QA/
QC samples. The resulting data were used
to determine the  overall  quality of the
sample extraction and analysis procedures,
the uniformity of pesticide applications, and
the overall  sampling  precision and trans-
fer efficiency of each test method under
evaluation.

Test Methods

a-Cellulose Deposition Coupon
  The deposition coupons used were 100-
mm  squares of cellulose filter paper at-
tached to aluminum  foil-covered backing
sheets of the same size.  Each coupon
was  marked by pencil line so that a 12.5-
mm (0.5 in.) border on all sides was avail-
able to allow handling. Prior to extraction,
the coupon  border was trimmed  away to
leave a 75-mm square (56.25 cm2) filter
sample for analysis in the laboratory. Esti-
mates of the deposition rate for a given
sample were determined from the ratio of
the mass of pesticide residue found on
the coupon  to its area and were usually
reported in units of micrograms per square
centimeter.

PUF Roller
  The  PUF  roller dislodgeable residue
sampling method  used a  prototype  me-
chanical apparatus having two rear wheels,
a cylindrical aluminum roller at the front,
and  a  handle for pushing  or pulling at-
tached at the rear.  Two stainless  steel
blocks (total weight = 3.875 kg) were at-
tached to the center  portion of the frame.
A polyurethane foam (PUF)  ring  measur-
ing 90-mm o.d.- x 30-mm i.d.- x 76 mm in
length was  fitted onto the aluminum cylin-
der, which was then  attached to the front
of the sampler assembly.
  The location of the sample was marked
on the test surface  by placing  a metal
guidebar adjacent to the planned track of
the device. The 100-cm sample  traverse
distance  was marked off in  10-cm seg-
ments on the bar. A solvent-washed thin
aluminum sheet was placed at the start-
ing position to serve as a platform to  hold
the PUF roller before starting the test.
  A  sample traverse  consisted  of  two
passes,  one  forward and one backward,
over the 100 cm pathlength. At the end of
the second  pass, the roller was immedi-
ately lifted  off the carpet. The aluminum
cylinder was then  detached  from the as-
sembly and  the PUF ring was recovered
and stored  in its container.  The marks at
10 cm intervals on the guidebar were used
to maintain  the sampling rate at about 10
cm/s.

California Roller
  The California roller method used a de-
vice  resembling a  large rolling pin to col-
lect surface dislodgeable residues on  a
percale sheet cloth matrix. The roller con-
sisted of a 63-cm-long PVC pipe,  13 cm
in diameter, fitted with PVC endcaps hav-
ing  roller handles. The roller was covered
with a 1-cm thick foam cover,  51  cm in
length, and is filled with a quantity of small
to  medium-size steel  ball bearings suffi-
cient to bring the total weight of the roller
to 25 Ib.
  The sampling  medium, consisting of a
precleaned 17-  x  17-in. cloth  cut  from
percale bedsheet material (50% combed
cotton, 50% FortrelŪ polyester, 180 thread
count), was placed flat on the carpet sur-
face and  covered with a plastic sheet (e.g.
medium-size  plastic trash bag, 20- x 24-
in.) Sampling$"as  performed  by moving
the roller back and forth ten times at a
steady rate over the sample medium (20
total passes). A special  metal handle as-
sembly was fabricated for use in  these
tests to permit the operator to more com-
fortably move the  roller without exerting
any downward pressure on the handles.
After the final sample pass, the  roller and
handle assembly were removed from the
test area, the plastic sheet discarded and
forceps used to  collect and fold the per-
cale cloth for insertion  into its sample con-
tainer.

Dow Drag  Sled
  The Dow drag sled procedure used a 3-
x 3-in. piece  of  3/4-in. thick plywood  as
the base  for a sled with a ridge contructed
on the top to hold an 8-lb round downrigger
weight. A screw eye  was placed in the
center of one edge of the block, to which
a 24-in.  long wire  and pull handle were
attached. The base and  sides of the sled
were covered with two layers of aluminum
foil attached with staples.
  The sampling  media consisted  of
precleaned 4- x 4-in. undyed cotton denim
cloth squares. A thin aluminum sheet start-
ing  platform and a guidebar were used
with the  Dow sled procedure.  A sample
traverse  consisted  of  a  single pass with
the sled  over  a  distance of 48 in. using
guide marks at 4 in.  intervals to achieve
an approximate sampling rate of 10 cm/s.
  The denim cloth sampling media was
attached  to the base  of the sled by using
plastic-headed pushpins  positioned
through the overlapping edges of the cloth
and into the front and sides of the wooden
sled.  With  the denim cloth securely in
place, the sled was placed on  the alumi-
num starting platform, and the 8-lb. weight
was put into its position on top of the sled.
The  drag line was then  attached to the
screw eye on the front of the sled. Keep-
ing the drag  line  at a  low angle relative to
the floor, the  operator pulled the sled for-
ward at a steady rate until the front of the

-------
sled reached the  48-in.  mark  on the
guidebar. The sled was then quickly lifted
from the carpet surface and the  denim
cloth was removed from the sled,  folded
and stored  in its container.

Sample Analysis
  Test samples were prepared for analy-
sis  by  Soxhlet extraction  in ether: n-hex-
ane  (6:94) for 16  hours followed  by a
Florisil  cleanup. A surrogate compound (p
terphenyl-d14) was added to each sample
as a QC check on the process.
  Analysis  was performed  with a Fisons
VG MD800 GC/MS instrument in  selected
ion monitoring mode. A DB-5 column, 0.25-
mm-i.d. - x 30-m, was used for the analy-
sis. Quantitation was based on a five-
point standard calibration curve, and con-
tinuing  calibration was performed by  us-
ing the mid level standard.

Results and Discussion
  The  analytical results  for blanks, field
spikes, surrogate recoveries, and GC/MS
calibrations were acceptable for all seven
sets of test samples analyzed.  Pesticide
formula applications were uniform with the
results  of deposition coupon analysis yield-
ing  an  average of 23% RSD  for three
replicates per test.
  The  results for method sampling preci-
sion, shown in Table 1,  indicate that all
three  methods achieved relatively  good
precision. From a total of 63 sets of tripli-
cate results (7 tests x 3  methods x 3
pesticides), the overall average sampling
precision was 31.3% RSD (range = 2.4
                    86.1% RSD).  The Dow sled achieved the
                    best  sampling precision with an average
                    of 25.4% RSD, followed by the California
                    roller method at 30.7%, and the PUF roller
                    at 37.9%. Using the  calculated average
                    deposition rate  for each test,  the  mean
                    transfer efficiency rate was determined for
                    the three replicate  samples collected us-
                    ing each test method. The  average re-
                    sults  for the seven  tests performed  in the
                    study are shown in Table 2. The  results
                    indicate that the transfer efficiency for each
                    method is generally quite consistent for all
                    three target pesticides and over the  whole
                    range of subject operators. The California
                    roller produced  the highest transfer  effi-
                    ciency results, with an overall average of
                    5.0%. The  rates for the PUF  roller  and
                    Dow  sled methods were similar, with the
                    Dow  sled showing only slightly higher val-
                    ues on average. The PUF roller averaged
                    a 1.7%  tranfer  efficiency rate, while the
                    Dow  sled averaged 2.1%. Since both of
                    these test methods were designed to mimic
                    the exposure of a  20-lb child to surface
                    residues, it is  not surprising that the trans-
                    fer efficiency results are similar. The Cali-
                    fornia roller method seemed to be subject
                    to problems during execution of the tech-
                    nique by several operators. On many oc-
                    casions  the  dosimeter was  observed to
                    move or  slide on the  carpet surface dur-
                    ing the  rolling  operation. This problem
                    might account for higher transfer efficiency
                    results for some of the test samples  col-
                    lected relative to tests during  which the
                    dosimeter remained stationary during the
                    rolling operation.
Table 1. Round-Robin Test Results Summary - Sampling Precision*


                    Chlorpyrifos       Pyrethrin I    Piperonyl Butoxide
                                             Average
PUF Roller
California Roller
Dow Drag Sled
28.3%
27.1%
23.5%
45.7%
35.2%
26.8%
39.7%
29.7%
25.8%
0.379
0.307
0.254
* Mean % RSD for 3 replicates per test, average results for 7 tests.





Table 2. Round-Robin Test Results Summary - Transfer Efficiency*


                   Chlorpyrifos         Pyrethrin I    Piperonyl Butoxide
                                              Average
PUF Roller
California Roller
Dow Drag Sled
1.4%
4.2%
1.9%
1.9%
4.2%
2.1%
1.8%
6.6%
2.3%
1.7%
5.0%
2.1%
' Mean % transfer for 3 replicates per test, average results for 7 tests.
  The results of this  study  were  com-
pared to those of the study that led to the
recommendation for this round robin test.
The results for transfer rates of the three
test methods were similar in both studies
for tests  on  new carpets.  In  the  earlier
study,  however,  tests performed on car-
pets that were used  and then  repeatedly
cleaned  by chemical treatment  yielded
transfer rates that were  ten times lower
than those from tests on new carpets.
  The volunteers in the round robin study
provided  a  written  evaluation of all three
test methods following completion of the
testing. The methods were rated numeri-
cally as to (a)  ease  of  use,  (b) conve-
nience, (c)  transporting  apparatus in the
field, and (d)  ease of handling the sample
media. Responses were also obtained per-
taining to the time requirements and sim-
plicity of each method. The California roller
method was  consistently rated  lower  in
every catergory,  while the PUF roller and
Dow sled methods were generally rated
highly and about equal to one another.

Conclusions and
Recommendations
  1.   The volunteers were readily able  to
       perform the dislodgeable  residue
      sampling procedures with only mini-
       mal  prior orientation  and  instruc-
      tion.
  2.   The pesticide application procedure
       used for each  of the seven  round-
       robin tests yielded uniform results.
      The   average  deposition  rate
      (mean+SD, u,g/cm2) was 17.8+4.1
      for Chlorpyrifos, 1.33+0.61 for pyre-
      thrin I, and  10.1+2.3 for piperonyl
       butoxide.
  3.   One  of the primary objectives  of
      this study was to determine the level
      of sampling precision that could be
      attained with each  of the test meth-
      ods when used by typical opera-
      tors under controlled conditions. As
       measured by the calculated %RSD
      for three replicate samples, the Dow
      sled  method registered the highest
      overall sampling precision  (25.4%
       RSD).  The PUF roller method reg-
       istered the lowest sampling preci-
      sion  (37.9% RSD), and results for
      the California  roller method, modi-
      fied  to include use of a  custom
       handle assembly, were slightly bet-
      ter than the average (30.7% RSD).
  4.   The  other main objective criterion
       measured by the  results from the
       round-robin testing was that   of
       method transfer efficiency. Trans-
      fer efficiency is defined as the ratio
      of a method's transfer rate (|ig/cm2)

-------
    to the  deposition rate (|ig/cm2) as      6.
    determined by the mean value for
    three  deposition  coupons.  The
    mean transfer efficiency for the Cali-
    fornia roller was  high (5.0%), while
    the PUF roller and the  Dow sled
    mean  transfer  efficiencies were
    nearly  identical at 1.7%  and 2.1%,
    respectively.
5.   Transfer efficiency  for  all three
    dislodgeable residue test methods
    was  higher by about one order of
    magnitude in the round  robin tests      7.
    on new  carpets as  compared to
    that  determined  in  similar  experi-
    ments  performed on used carpets
    in an  earlier study  of  this type.
    Method transfer  rate, the ratio of
    the amount  (|ig) of  pesticide  col-
    lected  to the  area (cm2) of carpet
    surface traversed by the sampler,
    may  be  profoundly influenced, as
    the earlier work  suggests,  by the
    type, age, and prior  surface treat-
    ment of the carpets being tested.
The  results of subjective evalua-
tions of the three test methods by
the six round-robin test volunteers
indicated a clear consensus  in rat-
ing the California  roller method
lower overall as compared to the
PUF roller and Dow sled  methods.
The latter two methods were rated
highly and almost equal to one an-
other  according to the volunteers'
responses to criteria addressed in
the opinion survey.
The quantitative results of the study
along with  the subjective evalua-
tions by the volunteers lead  to the
conclusion that the California roller
method is the least suitable  of the
three  test  methods  for  sampling
dislodgeable residue on carpets. Its
high  transfer efficiency  (5.0%) is
less representative of actual human
skin  transfer  efficiency,  and  the
method involves  bulky equipment
that is difficult to use. Both the PUF
roller and the Dow drag sled  meth-
      ods performed well and are consid-
      ered equally suitable.
  8.   Although the results of this study
      show that reproducible and consis-
      tent data  can  be  obtained for
      dislodgeable pesticide residues on
      new carpet by  using  any of the
      three test methods under evalua-
      tion, the substantial difference  in
      measured transfer efficiency  rates
      between this study and  one con-
      ducted  earlier are cause  for con-
      cern. We therefore recommend that
      tests be conducted with one or more
      of the residue sampling methods
      on both new and used carpets  of
      varying types, including carpets that
      have, and  have not, been chemi-
      cally treated.
  The work reported herein was performed
by ManTech  Environmental Technology,
Inc.,  under U.S. Environmental Protection
Agency Contract  68-D5-0049,  and  by
Southwest Research Institute under Sub-
contract 96-0049-01 to ManTech.

-------
  ChristopherR. Fortune is with ManTech Environmental Technology, Inc., Research
    Triangle Park, NC 27709
  Robert G. Lewis is the EPA Project Officer (see below).
  The complete report, entitled "Round-Robin Testing of Methods for Collecting
    Dislodgeable Residues from Carpets,"(OrderNo. PB98-117989; Cost: $21.50,
    subject to change) will be available only from:
          National Technical Information Service
          5285 Port Royal Road
          Springfield, VA 22161
          Telephone: 703-487-4650
  The EPA Project Officer can be contacted at:
          National Exposure Research Laboratory
          U.S. Environmental Protection Agency
          Research Triangle Park, NC 27711
United States
Environmental Protection Agency
Center for Environmental Research Information
Cincinnati, OH 45268

Official Business
Penalty for Private Use $300
      BULK RATE
POSTAGE & FEES PAID
         EPA
   PERMIT NO. G-35
EPA/600/SR-97/107

-------