Available from:
Environmental
Reference Materials, Inc.
Research
Triangle Park, N.C. 27709
1-888-645-7645
(U.S. only)
FAX:
1-919-544-1669
Email: agaskill@nc.rr.com
These lead paint program testing standards are certified
reference materials that have been developed to assist laboratories in meeting
the quality control requirements of the American Industrial Hygiene
Association’s (AIHA) Environmental Lead Laboratory Accreditation Program
(ELLAP). The ELLAP accredits testing
laboratories under the U.S. EPA’s National Lead Laboratory Accreditation
Program.
They can be used as laboratory control standards or as
spiking materials for paint, soil and wipes.
These standards can also be used as practice samples for laboratories
participating in the AIHA’s Environmental Lead Proficiency Analytical Testing
Program (ELPAT). All products are
certified for Lead content. In
addition, products LCS-301 and 401 are certified for up to 15 additional
elements. A summary of product
information is presented below and complete certificates of analysis
follow. Certificates of analysis for
exhausted products and lots available on request. They can be viewed at www.leadpaint.150m.com/Lead
Paint StandardsExhausted1.htm and www.leadpaint.150m.com/Lead
Paint StandardsExhausted2.htm. To see our line of oil
proficiency and quality control testing standards go to www.leadpaint.150m.com/Oil
PT Standards.htm.
Product No. and Name Unit Size Lead Content, ppm Unit Price $ NIST Traceable
ERM-6e Lead Free Paint 50g <8 $160 yes
ERM-7a Lead Free Soil 50g <4 $160 yes
ERM-8e Low Level Lead in Paint 50g 626 $190 yes
ERM-9a Lead Paint in Soil 50g 484 $160 yes
ERM-12f Lead Paint in Soil 50g 5189 $190 yes
LCS-301 Northeast Urban Soil 50g 547 $190 yes
LCS-401 Blended Paints from 50g 4430 $190 yes
Public Buildings
Revisions to certificates and products: For LCS-401, results for Mercury determined by EPA Method 7471A were added (4-3-06). Lead results by EPA Method 3052 were upgraded to NIST traceable (4-3-06). ERM-8b added to replace ERM-8a and LCS-402 (3-27-07). ERM-12a added to replace ERM-11 and LCS-302 (5-24-07). Gravimetric values for Lead added to certificates for ERM-12a (6-13-07) and 8b (12-12-07). All products shown in table above are available. ERM-7 and 9 expiration date extended (1-9-08). ERM-8b text corrected to state that mixture of paints and not paint and soil used to prepare product (5-31-08—since this is an editorial change, a new revision number was not assigned). ERM-8c added to replace ERM-8b (5-27-08). ERM-12b added to replace ERM-12a (8-8-08). ERM-6e added to replace ERM-6d (4-23-09). ERM-8d added to replace ERM-8c and ERM-12c added to replace ERM-12b (7-8-09). Certificate for ERM-8a restored to list (7-8-09). ERM-12d added to replace ERM-12c (3-29-10). ERM-8e added to replace ERM-8d (11-30-10). ERM-12e added to replace ERM-12d (1-28-11). ERM-7 and 9 are now exhausted. Expiration dates for ERM-7a, 9a, LCS-301 and LCS-402 extended. ERM-12f added to replace ERM-12e. (11-22-11). Expiration dates for all exhausted lots extended. All exhausted lots added to website. Minor editorial changes made to certificates for exhausted lots. (12-20-11).
ENVIRONMENTAL REFERENCE
MATERIALS, INC.
P.O. BOX12527 RESEARCH TRIANGLE PARK, N.C. 27709 1-919-544-1669 1-888-OIL-SOIL
CERTIFICATE OF ANALYSIS
LEAD FREE PAINT
CAT. NO. ERM-6e
LOT NO. 6-09-1
DATE OF MANUFACTURE: 4-22-09
EXPIRATION DATE: 4-22-19
CERTIFIED VALUE FOR LEAD: <8 ± 0 mg/kg
DESCRIPTION AND INTENDED USE:
Virgin latex and enamel house
paints were evaporated to dryness, milled, sieved to pass an 850-micron sieve
and blended. The product was packaged
sequentially in 50g units in glass jars.
Units from the beginning, middle and end of the packaging sequence were
analyzed for Lead using EPA Method 6010C, Inductively Coupled Plasma-Atomic
Emission Spectroscopy after digestion by EPA Method 3050B, Acid Digestion of
Sediments, Sludges and Soils. A two-way
ANOVA of the resulting data showed that the within and between bottle analyses
could be considered equivalent. All of
the results were below the method detection limit of 8mg/kg. Therefore, the product is considered
homogeneous with respect to Lead. The
results of the 9 determinations were pooled and the 95% prediction interval
calculated. The certified value is the
mean value of these determinations ± the uncertainty for the 95%
prediction interval, which in this case, is <8 ± 0
mg/kg. Laboratories should be able to obtain
similar results using this method and a 0.5g sample size. Use of smaller or larger sample sizes will
potentially result in different detection limits and the acceptance range may
need to be changed accordingly. This
material was also analyzed for Lead along with NIST SRMs 2709, San Joaquin Soil
and 2586, Trace Elements in Soil Containing Lead from Paint and the NIST
traceable CRM, RTI LCS-401, Blended Paints from Public Buildings. The results for single determinations for
Lead in these materials were for SRM 2709 10mg/kg, 77% of the median of the
information values for Lead of 12-18mg/kg; for SRM 2586 420mg/kg, 97% of the
certified value for Lead of 432mg/kg and for LCS-401, 4711mg/kg, 106% of the
certified value for Lead of 4430mg/kg.
The certified value for Lead in SRM 2709 is 18.9 mg/kg, but is based on
a total digestion using hydrofluoric as well as nitric and hydrochloric acids. Information values presented from digestions
by Method 3050, an incomplete dissolution procedure using only nitric and
hydrochloric acids, showed a range of 12-18 mg/kg with a median value of
13. Because this SRM’s certified and
information values are also close to typical detection limits for soils, the
results for ERM-6e can be considered NIST traceable for Lead for this SRM. Because of the close agreement with the
certified values for the SRMs and LCS-401, the results for ERM-6e can be
considered NIST traceable for Lead.
This material is intended to be
used as a quality control standard in performing tests for Lead in paint by EPA
Methods 6010B and 7420 and ASTM Methods E1613-94 and D3335-85a (1994). Tests for stability will be performed as necessary. Any changes in the certified value outside
the 95% prediction interval will be reported to purchasers of this
product. The product does not require
any additional homogenization.
Approved by:
________________________ ___________
Alvia Gaskill, Jr., President Date
ENVIRONMENTAL
REFERENCE MATERIALS, INC.
P.O. BOX 12527 RESEARCH TRIANGLE
PARK, N.C. 27709 1-919-544-1669 1-888-OIL-SOIL
CERTIFICATE OF ANALYSIS
LEAD FREE SOIL
CAT. NO. ERM-7a
LOT NO. 7-02-1
DATE OF MANUFACTURE: 10-8-02
EXPIRATION DATE: 11-22-21
REVISION 2: 11-22-11
CERTIFIED VALUE FOR LEAD: <4.2 mg/kg
DESCRIPTION AND INTENDED USE:
A clean clay soil from land under
development in an industrial park was sieved to pass a 177-micron sieve and
blended. The product was packaged
sequentially in 50 g units in glass jars.
Units from the beginning, middle and end of the packaging sequence were
analyzed in triplicate for Lead using EPA Method 6010A, Inductively Coupled
Plasma-Atomic Emission Spectroscopy after digestion by EPA Method 3050A, Acid
Digestion of Sediments, Sludges and Soils.
A two-way ANOVA of the resulting data showed that the within and between
jar analyses could be considered equivalent.
All of the results were below the method detection limit of 4.2
mg/kg. Therefore, the product is
considered homogeneous with respect to Lead.
The results of the 14 determinations were pooled and the 95% prediction
interval calculated. The certified
value is the mean value of these determinations ± the uncertainty for the 95%
prediction interval, which in this case, is zero. Laboratories should be able to obtain similar results using this
method and a 0.5 g sample size. Use of
smaller or larger sample sizes will potentially result in different detection
limits and the acceptance range may need to be changed accordingly. This material was also analyzed for Lead
along with NIST SRM 2709, San Joaquin Soil.
The results of three determinations were all below the detection limit
of 4.2 mg/kg. The certified value for
Lead in this SRM is 18.9 mg/kg, but is based on a total digestion using
hydrofluoric as well as nitric and hydrochloric acids. Information values presented from digestions
by Method 3050, an incomplete dissolution procedure using only nitric and
hydrochloric acids, showed a range of 12-18 mg/kg. Because the SRM’s certified and information values are also close
to typical detection limits for soils, the results for ERM-7a can be considered
NIST traceable for Lead.
This material is intended to be
used as a quality control standard in performing tests for lead in soil by EPA
Methods 6010A and 7420 and ASTM Method E1613-94. Tests for stability will be performed as necessary. Any changes in the certified value outside
the 95% prediction interval will be reported to purchasers of this
product. The product does not require
any additional homogenization and there are no special storage requirements.
Approved by:
________________________ ___________
Alvia Gaskill, Jr.,
President Date
ENVIRONMENTAL
REFERENCE MATERIALS, INC.
P.O. BOX 12527 RESEARCH TRIANGLE PARK, N.C. 27709 1-919-544-1669 1-888-OIL-SOIL
CERTIFICATE OF ANALYSIS
LOW LEVEL LEAD IN PAINT
CAT. NO. ERM-8e
LOT NO. 8-10-1
EXPIRATION DATE: 11-17-20
CERTIFIED VALUE
FOR LEAD: 626.2 ± 33.7 mg/kg
GRAVIMETRIC VALUE FOR LEAD: 600.8 mg/kg
DESCRIPTION AND INTENDED USE:
Lead containing paint from public
buildings undergoing abatement was ball-milled, sieved to pass a 75-micron
sieve and blended with Lead free paint (<150microns) in a rotating
blender. The product was packaged sequentially
in 50g units. Samples from the
beginning, middle and end of the packaging sequence were analyzed for Lead
using EPA Method 7420, Lead (Atomic Absorption, Direct Aspiration) after
digestion by EPA Method 3050B, Acid Digestion of Sediments, Sludges and Soils. A two-way ANOVA of the resulting data from
Method 7420 showed that the within and between bottle analyses could be
considered equivalent. The CV of the
pooled data from Method 7420 was 2.4%.
Based on these analyses, the product was judged to be homogeneous with
respect to Lead. The results of the 15
determinations were pooled and the 95% prediction interval calculated. The certified value for Lead is the mean
value of these determinations ± the uncertainty for the 95% prediction interval. Laboratories should be able to obtain
results for Lead within this interval using this method and a 0.5g sample
size. This material was also analyzed
for Lead along with NIST SRM 2582, Powdered Paint. The mean of the results of three determinations for Lead in SRM
2582 by Method 7420 was 193.0mg/kg, 92.4% of the certified value of
208.8mg/kg. Because of the agreement
with the certified value for the SRM, the results for ERM-8e can be considered
NIST traceable for Lead. Because this
product was prepared by blending together paints of known content, a
gravimetric expected value can also be calculated. The certified value is 4.2% higher than the gravimetric value of
600.8mg/kg.
This
material is intended for use as a quality control standard in performing tests
for Lead in paint by EPA Methods 6010 and 7420 and ASTM Method E1613-94. Results also apply to digestions performed
using EPA Methods 3050A and 3051. Tests
for stability will be performed as necessary.
Any changes in the certified value outside the 95% prediction interval
will be reported to purchasers of this product. The product does not require any additional homogenization and
there are no special storage requirements.
Approved by:
________________________ ___________
Alvia Gaskill, Jr.,
President Date
ENVIRONMENTAL REFERENCE
MATERIALS, INC.
P.O. BOX 12527 RESEARCH TRIANGLE PARK, N.C. 27709 1-919-544-1669 1-888-OIL-SOIL
CERTIFICATE OF ANALYSIS
LEAD PAINT IN SOIL
CAT. NO. ERM-9a
LOT NO. 9-02-1
DATE OF MANUFACTURE: 10-8-02
EXPIRATION DATE: 11-22-21
REVISION 2: 11-22-11
CERTIFIED VALUE FOR LEAD: 483.6 ± 48.9 mg/kg
DESCRIPTION AND INTENDED USE:
Soil containing lead paint was
sieved to pass a 177-micron sieve and blended with clean base soil. The product was packaged sequentially in 50
g units in glass jars. Units from the
beginning, middle and end of the packaging sequence were analyzed in triplicate
for Lead using EPA Method 6010A, Inductively Coupled Plasma-Atomic Emission
Spectroscopy after digestion by EPA Method 3050A, Acid Digestion of Sediments,
Sludges and Soils. A two-way ANOVA of
the resulting data showed that the within and between jar analyses could be
considered equivalent. The CV of the
pooled data from these tests was 4.5%.
Based on these analyses, the product was judged to be homogeneous with
respect to Lead. The results of the 14
determinations were pooled and the 95% prediction interval calculated. The certified value for Lead is the mean
value of these determinations ± the uncertainty for the 95% prediction interval. Laboratories should be able to obtain
results for Lead within this interval using this method and a 0.5 g sample
size. This material was also analyzed along
with NIST SRM 2586, Trace Elements in Soil Containing Lead from Paint. The mean of the results of three
determinations was 401.9 mg/kg, 93% of the certified value for Lead of 432
mg/kg. Because of the close agreement
with the certified value for the SRM, the results for ERM-9a can be considered
NIST traceable for Lead.
This material is intended to be
used as a quality control standard in performing tests for Lead in soil by EPA
Methods 6010A and 7420 and ASTM Method E1613-94. Tests for stability will be
performed as necessary. Any changes in
the certified value outside the 95% prediction interval will be reported to
purchasers of this product. The product
does not require any additional homogenization and there are no special storage
requirements.
Approved by:
________________________
___________
Alvia Gaskill, Jr., President Date
ENVIRONMENTAL REFERENCE
MATERIALS, INC.
P.O. BOX 12527 RESEARCH TRIANGLE PARK, N.C. 27709 1-919-544-1669 1-888-OIL-SOIL
CERTIFICATE OF ANALYSIS
LEAD PAINT IN SOIL
CAT. NO. ERM-12f
LOT NO. 12-11-2
DATE OF MANUFACTURE: 9-29-11
EXPIRATION DATE: 9-29-21
CERTIFIED VALUE FOR LEAD: 5189 ± 386 mg/kg
GRAVIMETRIC VALUE FOR LEAD: 5599 ± 4 mg/kg
DESCRIPTION AND INTENDED USE:
Lead paint, lead paint containing
soil and clean base soil, all of which passed a 100-micron sieve were
blended. Units from the beginning, middle
and end of the packaging sequence were analyzed for Lead using EPA Method 7420,
Lead (Atomic Absorption, Direct Aspiration) after digestion by EPA Method
3050B, Acid Digestion of Sediments, Sludges and Soils. A two-way ANOVA of the resulting data showed
that the between and within unit analyses could be considered equivalent. The CV of the pooled data from these tests
was 3.1%. Based on these analyses, the
product was judged to be homogeneous with respect to Lead. The results of the 9 determinations were
pooled and the 95% prediction interval calculated. The certified value for Lead is the mean value of these
determinations ± the uncertainty for the 95% prediction interval. Laboratories should be able to obtain
results for Lead within this interval using this method and a 0.5g sample
size. This material was also analyzed
along with NIST SRM 2586, Trace Elements in Soil Containing Lead from
Paint. The mean of the results of a
single determination for Lead in SRM 2586 was 400mg/kg, 92.6% of the certified
value for Lead of 432mg/kg. Because of
the agreement with the certified value for the SRM, the results for ERM-12f can
be considered NIST traceable for Lead.
Because this product was prepared by blending together soil and paint of
known Lead content, a gravimetric expected value can also be calculated. The gravimetric value, 5599mg/kg is just
outside the 95% prediction interval.
The certified value is 7.3% lower than the gravimetric value.
This material is intended for use
as a quality control standard in performing tests for Lead in soil by EPA
Methods 6010 and 7420 and ASTM Method E1613-94. Results also apply to digestions performed using EPA Methods
3050A and 3051. Tests for stability
will be performed as necessary. Any
changes in the certified value outside the 95% prediction interval will be
reported to purchasers of this product.
The product does not require any additional homogenization and there are
no special storage requirements.
Approved by:
________________________ ___________
Alvia Gaskill, Jr.,
President Date
RESEARCH
TRIANGLE INSTITUTE
P.O. BOX 12194 RESEARCH TRIANGLE PARK, N.C. 27709-2194 1-919-541-6883
CERTIFICATE OF ANALYSIS
NORTHEAST URBAN SOIL
CAT. NO. LCS-301
LOT NO. 301-98-1
DATE OF MANUFACTURE: 5-98
EXPIRATION DATE: 11-22-21
REVISION 2: 11-22-11
CERTIFIED VALUE FOR LEAD: 547.1 ± 41.2 mg/kg
DESCRIPTION AND INTENDED USE:
The material used in this reference
material was prepared according to procedures developed and used by Research
Triangle Institute (RTI) for its preparation of Environmental Lead Proficiency
Analytical Testing (ELPAT) materials for the American Industrial Hygiene
Association and also Standard Operating Procedures for Preparation of Lead in
Paint and Lead in Dust prepared for the U.S. EPA (EPA 600/R-93/235, NTIS
#PB94-141165; EPA 600/R-94/132, NTIS #PB95-174090; and EPA 600/R-94/146, NTIS
#PB95-190427).
Soil containing lead paint from
drip lines around pre-1978 houses was ball-milled, sieved to pass a 75µ sieve and blended in a V shell mixer. The product was packaged sequentially in 50
g units in glass bottles. Around 10% of
all units from the beginning, middle and end of the packaging sequence were
analyzed in duplicate for Lead using EPA Method 6010B, Inductively Coupled
Plasma-Atomic Emission Spectroscopy after digestion by EPA Method 3050A, Acid
Digestion of Sediments, Sludges and Soils and EPA Method 3051, Microwave
Assisted Acid Digestion of Sediments, Sludges, Soils and Oils. A two-way ANOVA of the resulting data showed
that the within and between bottle analyses could be considered equivalent. Additional statistical analyses showed the
Method 3050A and 3051 data could be considered equivalent. The CV of the pooled data from these tests
was 3.7%. Based on these analyses, the
product was judged to be homogeneous for Lead.
The results of the 70 determinations were pooled and the 95% prediction
interval calculated. The certified
value for Lead is the mean value of these determinations ± the
uncertainty for the 95% prediction interval.
Laboratories should be able to obtain results for Lead within this
interval using this method and a 0.5 g sample size. This material was also analyzed along with NIST SRM 2704, Buffalo
River Sediment. The mean of the results
of six determinations was 163 mg/kg, 101% of the certified value for Lead of
161 mg/kg. Because of the close
agreement with the certified value for the SRM, the results for LCS-301 can be
considered NIST traceable for Lead.
Results for additional NIST and non-NIST traceable elements are given on
the following pages.
This material is intended to be
used as a quality control standard in performing tests for Lead and other
elements in soil by EPA Methods 6010B and 7420 and ASTM Method E1613-94. Tests for stability will be performed as
necessary. Any changes in the certified
value outside the 95% prediction interval will be reported to purchasers of
this product. The product does not
require any additional homogenization and there are no special storage
requirements.
Approved by:
__________________________________________ ___________
William F. Gutknecht, Research
Triangle Institute
Date
Results
for additional NIST traceable elements in LCS-301
by pooling
data from Methods 3050A and 3051*
Pooled Mean value, ±Uncertainty,
Element N data CV mg/kg 95% P.I., mg/kg
Aluminum 70 8.5%
9474 1613
Barium 70 3.9% 93.3 7.3
Cadmium 70 0% <1 0
Chromium 70 9.3% 16.2 3.0
Copper 70 13% 19.9 5.2
Iron 70
8.1% 11631 1918
Magnesium 70 4.7% 2838 268
Manganese 70 6.0% 228.7 27.4
Nickel 70
8.5% 11.7 2.0
Strontium 70 14.7% 19.7 5.8
Vanadium 70 10.2% 22.3 4.6
Zinc 70
4.5% 137.5 12.7
*All
product preparation and testing identical to that for Lead on cover page of
this certificate except as noted.
Within/between bottle analyses in agreement, Method 3050A/3051 data
determined to be equivalent and product judged homogeneous for all elements shown
except Copper and Strontium. N = number
of determinations. P.I. = prediction interval.
Results
for non-NIST traceable elements in LCS-301
by pooling
data from Methods 3050A and 3051*
Pooled Mean value, ±Uncertainty,
Element N data CV mg/kg 95% P.I., mg/kg
Boron 70 16.2% 13.0
4.2
Beryllium 70 14.0% 1.4
0.4
Molybdenum 70 0% <10
0
*All
product preparation and testing identical to that for Lead on cover page of
this certificate except as noted. Within/between
bottle analyses in agreement, Method 3050A/3051 data determined to be
equivalent and product judged homogeneous for all elements shown except Boron
and Beryllium. N = number of
determinations. P.I. = prediction interval.
Results
for NIST traceable elements
in LCS-301
by modified Method 3052 only*
Pooled Mean value, ±Uncertainty,
Element N data CV mg/kg 95% P.I., mg/kg
Aluminum 35 1.8%
50300 1888
Barium 35 3.2% 442.8 29.0
Cadmium 35
0% <5 0
Chromium 35 12.3% 36.5 9.3
Copper 35 36.0% 21.1 15.6
Iron 35
2.6% 19646 1046
Lead 35
7.3% 552.5 83.4
Magnesium 35 2.7%
4606 254
Manganese 35 2.4% 441.9 22.2
Nickel 35
35.4% 19.2 14.0
Strontium 35 2.7% 140.5 7.8
Vanadium 35 9.2% 50.1 9.5
Zinc 35
7.3% 152.2 22.9
*All product preparation and testing identical to
that for Lead on cover page of this certificate except as noted. Modified Method 3052, based on EPA Method
3052, Microwave Assisted Acid Digestion of Siliceous and Organically Based Matrices,
is a microwave-assisted total digestion procedure in which the samples were
first digested in a mixture of concentrated nitric acid and 49% hydrofluoric
acid followed by additional digestion with concentrated hydrochloric and 49%
hydrofluoric acids and on cooling, addition of boric and hydrochloric
acids. For details of this procedure,
contact manufacturer. Product judged
homogeneous for all elements shown except for Chromium, Copper and Nickel. N = number of determinations. P.I. =
prediction interval.
Results for non-NIST traceable elements
in LCS-301
by modified Method 3052 only*
Pooled Mean value, ±Uncertainty,
Element N data CV mg/kg 95% P.I., mg/kg
Beryllium 35 30% 3.3 2.1
Molybdenum 35 0% <40 0
*Same
footnotes as in previous table, except Beryllium only element not homogeneous.
NIST
traceability for LCS-301 vs. SRM 2704
using
pooled means for Methods 3050A and 3051*
Mean
value,
Certified value
Element N
mg/kg mg/kg %
of SRM value
Aluminum 6 11850 61110 19
Barium 6 87.9 414 21
Cadmium 6 3.70 3.45 107
Chromium 6 81.4 135 60
Copper 6 75.5 98.6 77
Iron 6 30350 41100 74
Magnesium 6 9022 12000 75
Manganese 6 489 555 88
Nickel 6 39.0 44.1 89
Strontium 6 34.5 130 27
Vanadium 6 21.7 95 23
Zinc 6
413 438 94
*Low
recoveries for Aluminum, Barium, Strontium and Vanadium not unexpected, since
NIST SRM values based on total digestion and 3050A/3051 results based on
partial digestion.
NIST
traceability for LCS-301
vs. SRM
2704 for modified Method 3052
Mean
value,
Certified value
Element N
mg/kg mg/kg %
of SRM value
Aluminum 3 59767 61110 98
Barium 3 402 414 97
Cadmium 3 5.30 3.45 154
Chromium 3 121 135 90
Copper 3 76 98.6 77
Iron 3
39567 41100 96
Lead 3
149 161 93
Magnesium 3 11933 12000 99
Manganese 3 539 555 97
Nickel 3 44.4 44.1 101
Strontium 3 126 130 97
Vanadium 3 94.1 95 99
Zinc 3
400 438 91
RESEARCH
TRIANGLE INSTITUTE
P.O. BOX 12194 RESEARCH TRIANGLE PARK, N.C. 27709-2194 1-919-541-6883
CERTIFICATE OF ANALYSIS
BLENDED PAINTS FROM PUBLIC BUILDINGS
CAT. NO. LCS-401
LOT NO. 401-98-1
DATE OF MANUFACTURE: 5-98
EXPIRATION DATE: 11-16-21
CERTIFIED VALUE FOR LEAD: 4430 ± 266 mg/kg
DESCRIPTION AND INTENDED USE:
The material used in this
reference material was prepared according to procedures developed and used by
Research Triangle Institute (RTI) for its preparation of Environmental Lead
Proficiency Analytical Testing (ELPAT) materials for the American Industrial
Hygiene Association and also Standard Operating Procedures for Preparation of
Lead in Paint and Lead in Dust prepared for the U.S. EPA (EPA 600/R-93/235,
NTIS #PB94-141165; EPA 600/R-94/132, NTIS #PB95-174090; and EPA 600/R-94/146,
NTIS #PB95-190427).
Lead-containing paint from a
hospital undergoing abatement was ball-milled, sieved to pass a 75µ sieve and blended in a V shell mixer. The product was packaged sequentially in 50
g units in glass bottles. Around 5% of
all units from the beginning, middle and end of the packaging sequence were
analyzed in duplicate for Lead using EPA Method 6010B, Inductively Coupled
Plasma-Atomic Emission Spectroscopy after digestion by EPA Method 3050A, Acid
Digestion of Sediments, Sludges and Soils and EPA Method 3051, Microwave
Assisted Acid Digestion of Sediments, Sludges, Soils and Oils. A two-way ANOVA of the resulting data showed
that the within and between bottle analyses could be considered
equivalent. Additional statistical
analyses showed the Method 3050A and 3051 data could be considered
equivalent. The CV of the pooled data
from these tests was 2.9%. Based on
these analyses, the product was judged to be homogeneous for Lead. The results of the 34 determinations were
pooled and the 95% prediction interval calculated. The certified value for Lead is the mean value of these
determinations ± the uncertainty for the 95% prediction interval. Laboratories should be able to obtain results
for Lead within this interval using this method and a 0.5 g sample size. This material was also analyzed along with
NIST SRM 1579, Lead Paint. The mean of
the results of a single determination was 11.00%, 93% of the certified value
for Lead of 11.87%. Because of the
close agreement with the certified value for the SRM, the results for LCS-401
can be considered NIST traceable for Lead.
Results for additional NIST and non-NIST traceable elements are given on
the following pages.
This material is intended to be
used as a quality control standard in performing tests for Lead and other
elements in paint by EPA Methods 6010B and 7420 and ASTM Method E1613-94. Tests for stability will be performed as
necessary. Any changes in the certified
value outside the 95% prediction interval will be reported to purchasers of
this product. The product does not
require any additional homogenization and there are no special storage requirements.
Approved by:
__________________________________________ ___________
William F. Gutknecht, Research
Triangle Institute
Date
Results
for non-NIST traceable elements in LCS-401
by pooling
data from Methods 3050A and 3051*
Pooled Mean value, ±Uncertainty,
Element N data CV mg/kg 95% P.I., mg/kg
Beryllium 34 0% <1 0
Cadmium 34 9.3% 16.2 3.1
Chromium 34 8.3% 72.3 12.4
Copper 34 7.9% 13.3 2.3
Manganese 34 4.4% 137.0 12.6
Molybdenum 34 0% <15 0
Nickel 34
5.9 79.1 9.7
Vanadium 34 4.5% 7.6 0.6
*All
product preparation and testing identical to that for Lead on cover page of
this certificate except as noted.
Within/between bottle analyses in agreement, Method 3050A/3051 data
determined to be equivalent and product judged homogeneous for all elements
shown. N = number of determinations.
P.I. = prediction interval.
Results
for non-NIST traceable elements
in LCS-401
by Method 3050A only*
Pooled Mean value, ±Uncertainty,
Element N data CV mg/kg 95% P.I., mg/kg
Aluminum 17 3.9%
8914 764
Barium 17 23.0% 3250 1657
Iron 17
5.7% 4332 543
Magnesium 17 3.7% 7712 628
Strontium 17 4.3% 132.0 12.4
*All
product preparation and testing identical to that for Lead on cover page of
this certificate except as noted.
Results for Methods 3050A and 3051 were different enough that they could
not be combined and are reported separately.
Product judged homogeneous for all elements shown except Barium. N = number of determinations. P.I. =
prediction interval.
Results
for non-NIST traceable elements
in LCS-401
by Method 3051 only*
Pooled Mean value, ±Uncertainty,
Element N data CV mg/kg 95% P.I., mg/kg
Barium 17 4.7%
10565 1077
Iron 17 10.7% 2855 662
Magnesium 17 4.6% 6299 634
Strontium 17 3.6%
180.4 13.9
Mercury** 18 1.9% 23.76 0.95
*All
product preparation and testing identical to that for Lead on cover page of
this certificate except as noted.
Results for Methods 3050A and 3051 were different enough that they could
not be combined and are reported separately.
Product judged homogeneous for all elements shown. N = number of determinations. P.I. =
prediction interval. **Results for
Mercury using EPA Method 7471A Mercury in Solid or Semisolid Waste (Manual
Cold-Vapor Technique).
Results
for non-NIST traceable elements
in LCS-401
by modified Method 3052 only*
Pooled Mean value, ±Uncertainty,
Element N data CV mg/kg 95% P.I., mg/kg
Aluminum 18 6.2%
14294 1918
Barium 18 3.3%
15572 1098
Beryllium 18 0% <1 0
Cadmium 18 33.3% 17.1 12.3
Chromium 18 6.5% 97.1 13.6
Copper 18 0% <16 0
Iron 18
6.4% 5194 714
Magnesium 18 5.7% 21239 2624
Manganese 18 5.5% 197.1 23.3
Molybdenum 18 0% <40 0
Nickel 18
10.4% 115.8 26.1
Strontium 18 3.0% 238.3 15.3
Vanadium 18 16.1% 69.0 24.0
Zinc 18
5.8% 57850 7265
*All
product preparation and testing identical to that for Lead on cover page of
this certificate except as noted.
Modified Method 3052, based on EPA Method 3052, Microwave Assisted Acid
Digestion of Siliceous and Organically Based Matrices, is a microwave-assisted
total digestion procedure in which the samples were first digested in a mixture
of concentrated nitric acid and 49% hydrofluoric acid followed by additional
digestion with concentrated hydrochloric and 49% hydrofluoric acids and on
cooling, addition of boric and hydrochloric acids. For details of this procedure, contact manufacturer. Product judged homogeneous for all elements
shown except for Cadmium and Vanadium.
N = number of determinations. P.I. = prediction interval.
Results
for NIST traceable elements
in LCS-401
by modified Method 3052 only*
Pooled Mean value, ±Uncertainty,
Element N data CV mg/kg 95% P.I., mg/kg
Lead 18
6.7% 4623 671
*Same
footnotes as in previous table.
NIST traceability
for LCS-401
vs. SRM
1579 for modified Method 3052
Mean
value,
Certified value
Element N
mg/kg mg/kg % of SRM value
Lead 1
12900 11870 109
Page
last updated: December 20, 2011. Prices
and availability of products are current as of that date.